finding of suitability to transfer fost 2013-5

FINDING OF SUITABILITY TO TRANSFER FOST 2013-5

PARCELS AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, AND EDC-46

(Approximately 59.58 Acres)

FORMER NAVAL AIR STATION BRUNSWICK BRUNSWICK, MAINE

Prepared by:

Department of the Navy Base Realignment and Closure

Program Management Office East 4911 S. Broad Street

Philadelphia, Pennsylvania 19112

March 2014

W5213868F -i- Finding of Suitability to Transfer 2013-5

TABLE OF CONTENTS SECTION PAGE

TABLE OF CONTENTS ................................................................................................................................ i

1.0 PURPOSE ........................................................................................................................................ 1

2.0 PROPERTY DESCRIPTION ............................................................................................................ 1 2.1 Parcel Descriptions .......................................................................................................................... 1 2.2 Proposed Reuse for Transfer Parcels .............................................................................................. 4

3.0 SUMMARY OF ENVIRONMENTAL REQUIREMENTS AND NOTIFICATIONS ............................ 6 3.1 Comprehensive Environmental Response, Compensation and Liability Act ................................... 7 3.2 Resource Conservation and Recovery Act .................................................................................... 12 3.3 Presence of Petroleum Products and Derivatives ......................................................................... 15 3.4 Underground Storage Tanks, Aboveground Storage Tanks, and Oil-Water Separators .............. 16 3.5 Munitions and Explosives of Concern ............................................................................................ 17 3.6 Asbestos-Containing Material ........................................................................................................ 18 3.7 Lead-Based Paint ........................................................................................................................... 20 3.8 Polychlorinated Biphenyls .............................................................................................................. 20 3.9 Pesticide Notification ...................................................................................................................... 21 3.10 Environmental Notices, Restrictions, and Covenants .................................................................... 21 3.11 Environmental Compliance Agreements/Permits/Orders .............................................................. 21 3.12 Availability of References ............................................................................................................... 22 3.13 Notification to Regulatory Agencies and Public ............................................................................. 22

4.0 FINDING OF SUITABILITY TO TRANSFER ................................................................................ 23 EXHIBITS A References B Figures and Tables Figure B-1 Location Map Figure B-2 Aerial View Figure B-3 Features Map (Main Base) Figure B-4 Features Map Parcels AIR-8 and AIR-11 Figure B-5 Features Map Parcel AIR-10 Figure B-6 Features Map Parcels AIR-13, EDC-15 and EDC-35 Figure B-7 Features Map Parcel AIR-18 Figure B-8 Features Map Parcel EDC-27 Figure B-9 Features Map Parcel EDC-28 Figure B-10 Features Map Parcel EDC-34 Figure B-11 Features Map Parcel EDC-45 Figure B-12 Features Map Parcel EDC-46 Table B-1 Current and Former Buildings and Land Area Table B-2 Summary of Environmental Sites on or Near Transfer Parcels Table B-3 Environmental Issues by Building and Land Area Table B-4 Summary of Documented Spills Table B-5 Underground Storage Tanks Table B-6 Aboveground Storage Tanks

W5213868F -ii- Finding of Suitability to Transfer 2013-5

TABLE OF CONTENTS (cont.) Table B-7 Oil-Water Separators Table B-8 Summary of Asbestos Containing Material Table B-9 Summary of Current and Removed Equipment Containing Dielectric Fluid Table B-10 Monitoring Well Locations on Transfer Parcels C CERCLA Hazardous Substances Notice D Notice of Petroleum Products and Derivatives E Asbestos-Containing Materials Hazard Disclosure and Acknowledgment Form F Lead-Based Paint Hazard Disclosure and Acknowledgment Form G Environmental Notices, Restrictions, and Covenants H Comments and Responses

W5213868F -1- Finding of Suitability to Transfer 2013-5

1.0 PURPOSE

This Finding of Suitability to Transfer (FOST) summarizes how the requirements and notifications for

hazardous substances, petroleum products, and other regulated material on Parcels AIR-8, AIR-10, AIR-

11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Transfer

Parcels) have been satisfied. This FOST documents my determination, as the responsible Department of

Defense (DoD) component official, that certain real property and associated improvements at the former

Naval Air Station Brunswick (NASB) are environmentally suitable for deed transfer subject to the notices,

restrictions, and covenants set forth in this document. The Transfer Parcels are located on the former

NASB Main Base in Brunswick, Maine, as depicted on Figure B-1. They will be conveyed to one

GRANTEE, the Midcoast Regional Redevelopment Authority (MRRA). The parcels comprise

approximately 59.58 acres of land.

The suitability for transfer decision is based primarily on review of information contained in reports, former

NASB Environmental Department records, and other communications listed in Exhibit A (References).

Factors leading to this decision and other pertinent information related to property transfer requirements

are stated below.

2.0 PROPERTY DESCRIPTION 2.1 Parcel Descriptions

The Transfer Parcels are identified in the following table with their parcel identification number (ID), figure

number, the applicable reuse district based on the Reuse Master Plan (Matrix, 2007), approximate

acreage, the conveyance mechanism (i.e., Public Benefit Conveyance [PBC] or Economic Development

Conveyance [EDC]), and the intended recipient (GRANTEE).

Parcel

ID Figure Reuse Master Plan District Approximate Acres Conveyance Grantee

AIR-8 B-4 Aviation 1.24 PBC MRRA

AIR-10 B-5 Aviation/Education/Natural Areas 24.17 PBC MRRA




EDC-15 B-6 Business & Technology Industries 2.92 EDC MRRA


EDC-28 B-9 Residential 4.72 EDC MRRA

EDC-34 B-10 Professional Office 3.74 EDC MRRA



Parcel ID Figure Reuse Master Plan District Approximate

Acres Conveyance Grantee


EDC-46 B-12 Community Mixed Use 0.31 EDC MRRA FOST 2013-5 Total Acres 59.58

The acreages presented for the Transfer Parcels are approximate. The figures and descriptions included

in this FOST provide a general depiction of the boundaries of, and buildings and structures within, the

Transfer Parcels as depicted in Figures B-2 through B-12. The exact boundary of each Transfer Parcel

will be determined by a real estate survey, along with a map and legal description that meets the

requirements of the Cumberland County Registry of Deeds.

Parcels AIR-8 and AIR-11 (Figure B-4) are adjacent to each other at the southern end of the airfield

apron. The parcels are bordered by the apron and Building 554 (P-3 Support Facility) and Hangar 5 to

the north, the apron and runways to the west, the end of the apron and Buildings 553 (Airfield Support

Building) and 153 (Recycling Center) to the south, and Orion Street, Buildings 584 (General Warehouse)

and 590 (Transportation Maintenance), and Installation Restoration (IR) Program Sites 4 (Acid/Caustic

Disposal Pit) and 13 (Defense Reutilization and Marketing Office Area) to the east. Building 611 (T-56

Engine Test Facility) is located on Parcel AIR-8 and Building 555 (Sonobuoy/Vehicle Storage) is located

on Parcel AIR-11, as described in Table B-1.

Parcel AIR-10 (Figure B-5) is primarily open, grassy land located west of the runways that includes

Building 63 (Storage Facility; former High Explosives Magazine), the Fire Training Area – West (FTA-W),

an Area of Potential Interest (AOPI), and most of the Former Munitions Bunker West (FMBW) Site, a

Navy Munitions Response Program (MRP) site, as described in Tables B-1 and B-2. IR Site 18 (West

Runway Study Area) is surrounded by Parcel AIR-10, but is not part of the parcel.

Parcels AIR-13, EDC-15, and EDC-35 are located in the north-central portion of the former NASB on or

near the airfield apron. Parcels AIR-13 and EDC-15 are immediately adjacent to each other, and Parcel

EDC-35 is just south of Parcel EDC-15 (Figure B-6). The airfield Operations/Control Tower (Building 200)

is north of Parcel AIR-13, and the Former Hangars 1, 2, and 3 AOPI is both north and south of the parcel.

Parcel AIR-13 includes Buildings 292 (Fire/Rescue Facility) and 45 (Hazardous Waste Transfer Facility).

Two aviation gasoline pipelines that connected former Hangars 1, 2, and 3 to the Old Navy Fuel Farm

(ONFF) in the 1940s were present on the parcel and are believed to have been abandoned in place.

Parcel EDC-15 contains Buildings 41 (Security Office) and 647 (Bottled Gas Storage/Pest Control Shop).

The Former Hangars 1, 2, and 3 AOPI is north of Parcel EDC-15. Historically, the parcel contained a


Public Works Department paint locker/storage shop, supply/classroom buildings, a former mobile (indoor)

shooting range east of Building 41, a beacon tower and a ready magazine.

Parcel EDC-35 contains Buildings 44 (Fitch Avenue Magazine) and 556 (Loading Dock). The Former

Buildings 7 & 10 AOPI is directly south of Parcel EDC-35.

Parcel AIR-18 is in the northwest section of the former NASB (Figure B-7). The surrounding areas

consist of an old runway to the east, an old taxiway to the south, a small outdoor physical training area to

the west, and small wooded areas. Building 231 (Air Traffic Control Tower), also known as the Radar

Approach Control (RAPCON) site, is on the parcel and is described in Table B-1. In July 2012, the Navy

forwarded proposed transfer documentation to the Federal Aviation Administration (FAA) and requested

their decision on accepting custody and control of three land parcels, which included Parcel AIR-18. FAA

did not accept the transfer and formally withdrew its request for the property in September 2012. The

Navy retains custody and control of Parcel AIR-18, and MRRA requested the parcel by modifying its

approved Airport PBC.

Parcel EDC-27 is in the east-central portion of the former NASB across Orion Street from Hangar 5

(Figure B-8). Building 81 (CHRIMP Facility) and IR Site 9 (Neptune Drive Disposal Area) are to the north,

the Orion Street Skeet Range MRP site (formerly known as the Main Base Skeet Range) is to the north

and east, and Building 50 (Groundwater Treatment Plant) is to the south. Buildings 55 (Base Security)

and 551 (Security Generator) are on the parcel, as described in Tables B-1 and B-2. The Machine Gun

Boresight Range MRP site (Table B-2) is also within the parcel boundary. Building 51 (NCIS/Fire

Prevention) and the land within its footprint are not located on Parcel EDC-27 as they were previously

transferred as Parcel EDC-47.

Parcel EDC-28 is in the northeastern residential area of the former NASB where former Building 586

(Amateur Radio Shack, formerly AF-4, Air Force Transmitter Building) was once located (Figure B-9).

The parcel is grassy to the north and west and wooded to the south and east.

Parcel EDC-34 is the majority of the Navy Mobile Construction Battalion 27 (NMCB-27) Compound

(Seabee Compound) on the north-central boundary of the former NASB (Figure B-10). Buildings 404,

629, 630, 631, 633, 634, 635, 636, 659, 661, and 662, as well as numerous unnumbered concrete pads

and other structures, are located on Parcel EDC-34 which is bordered by Route 24 (Bath Road) to the

north, woods to the south and east, and open runway clear zone to the west. The buildings within Parcel

EDC-34 are described in Table B-1.


Parcel EDC-45 is located in the north-central portion of the base (Figure B-11), and is bordered by the

Former Hangars 1, 2, and 3 AOPI and Building 103 (Dog Kennel) to the north, IR Site 17 (Former

Building 95) and POL Site 1 (ONFF) to the east, and open areas to the south and west where multiple

former buildings were located. Building 102 (Indoor Small Arms Range) is the only building currently

located on Parcel EDC-45. Historically, the parcel contained former Building 13 (Supply Department

paint and oil storage building), several training buildings, and an oil tank that was identified as a building.

Current and former buildings within the parcel are described in Table B-1.

Parcel EDC-46 is the former Navy College Office (Building 20) which is described in Table B-1. The

parcel is comprised of the building and the land within the building footprint only. It is located in the

commercial area of the former NASB (Figure B-12), and is surrounded by parking lots and other

commercial buildings – Buildings 11 (Navy Exchange) to the southwest, 585 (Chapel) to the northwest,

583 (Bowling Center/Recreation Mall) to the northeast, and Building 31 (Navy Lodge) to the east.

Additional information about current and former buildings in the Transfer Parcels is provided in Table B-1.

2.2 Proposed Reuse for Transfer Parcels

Proposed reuses are included in the Reuse Master Plan (Matrix, 2007), which establishes the overall

framework for future reuse and redevelopment of the former NASB, and will be implemented by MRRA.

Typical reuse options for the master plan reuse districts applicable to the Transfer Parcels are described

below.

MRRA’s application to acquire a portion of the former NASB under a PBC for airport purposes was

approved by the Federal Aviation Administration (FAA) and accepted by the Navy. A portion of the

requested land was found suitable to transfer in December 2010 and was conveyed by the Navy to

MRRA in March 2011. Additional parcels were found suitable to transfer and conveyed to MRRA in

March 2012 and March 2013. This FOST includes additional airport property identified as Parcels AIR-8,

AIR-10, AIR-11, AIR-13, and AIR-18. MRRA proposes continued operation of the airfield and

development of aviation-related business, industry, transportation and distribution, technology

employment, and other uses that rely on, or directly benefit from, proximity to airport facilities and

operations. Such uses could include general and corporate aviation, aircraft maintenance, repair and

overhaul, aviation-related manufacturing, and government and aerospace research and development.

The AIR parcels on the east side of the runways (AIR-8, AIR-11, and AIR-13) are located within the

Aviation-related Business District. Parcels AIR-10 and AIR-18 are west of the runways and are located in

or surrounded by the Airport Operations, Natural Areas, and/or Education Districts. Parcel AIR-10 is

currently open space and is located within the airport easement. Parcel AIR-18 was not included in the


Reuse Master Plan because it was originally intended for transfer to the FAA for continued use as an air

traffic control tower and RAPCON facility. It will now be transferred to MRRA for airfield operations

purposes.

MRRA has requested approval from the Navy to acquire Parcels EDC-15, EDC-27, EDC-28, EDC-34,

EDC-35, EDC-45, and EDC-46 for economic development purposes. This use is consistent with current

and former land use (i.e., industrial, commercial, administration, training) on these parcels. The EDC

parcels are located within the B&TI District, Professional Office (PO) District, Residential District, and

Community Mixed Use (CMU) District.

Parcels EDC-15, EDC-27, EDC-35, and EDC-45 are in the B&TI District which is intended to provide a

high-tech employment center that will accommodate large scale technology uses, such as technology-

based research and development, energy parks, laboratories, light manufacturing, and warehouse and

distribution uses. This district could also accommodate activities that are normally considered industrial in

nature, but which produce few, if any, external impacts that may be adverse to nearby properties or to the

community in general.

Parcel EDC-34 is in the PO District which is intended to provide an employment center for corporate and

professional offices such as law, medical, insurance, architectural, engineering, finance, real estate, or

other similar users. Such uses could be accommodated within this zone in stand-alone buildings, in a

campus setting, or in a more compact office complex.

Parcel EDC-28 is in the Residential District which is intended to provide for a variety of housing types in a

compact, pedestrian-oriented setting. Typical uses will include single-family attached or detached, multi-

family apartments, assisted/senior housing, and retirement/second homes.

Parcel EDC-46 is in the CMU District which is intended to provide a centralized area that encourages a

compact pedestrian-oriented mix of community-related uses that will provide a variety of “live, work, play,

and educate” opportunities. Typical uses within the CMU could include neighborhood-scale retail,

professional offices, business and support services, restaurants, hotels and conference centers, health

and fitness centers, day care centers, civic and cultural uses (e.g. churches, libraries, and museums),

parks, and government buildings. A variety of higher-density attached housing types such as town

homes, condominiums and apartments (including affordable rental and home ownership, and

assisted/independent care senior housing) could also be included.


3.0 SUMMARY OF ENVIRONMENTAL REQUIREMENTS AND NOTIFICATIONS

Available information concerning the past storage, release, or disposal of hazardous substances and/or

petroleum products on the Transfer Parcels was compiled from record searches conducted or data

generated for the following documents: the Initial Assessment Study (IAS, Naval Energy and Environment

Support Activity [NEESA], 1983); the Environmental Condition of Property (ECP) report (U.S. Department

of the Navy (DoN) Base Realignment and Closure [BRAC] PMO, 2006); the Community Environmental

Response Facilitation Act (CERFA) Report (NAVFAC, 2007); the Third Five Year Review for Naval Air

Station Brunswick (Tetra Tech, 2010a); and the Resource Conservation and Recovery Act (RCRA) Partial

Closure Reports (Tetra Tech, 2010b-c, 2011a-q, 2012a-e, 2013b, 2013e) associated with these parcels.

Various specific studies conducted under the IR Program and specifically to support the FOST are cited.

Sources included NASB Environmental Department records and databases (for storage tanks,

transformers, spills); NASB Public Works (PW) Records and Drawings ranging from 1943 to 2006; Maine

Department of Environmental Protection (MEDEP) Spills and Tanks Databases (accessed 2013); NASB

PW documents associated with lead-based paint and asbestos; and historical aerial photographs (James

W. Sewell, 1953-1997; United States Environmental Protection Agency [USEPA] 1987 EPIC analysis).

Personnel interviews with current and former environmental department personnel and on-site visual

inspections were also conducted. References are cited in Exhibit A.

Detailed environmental recordkeeping, policies, and procedures evolved in the early 1980s as a result of

passage of RCRA (1976) and the Comprehensive Environmental Response, Compensation, and Liability

Act (CERCLA) (1980). The 1983 IAS provided the first detailed documentation of Navy management

practices for the use and storage of hazardous substances and storage and disposal of hazardous

wastes at the former NASB. Environmental records for the periods prior to this time were less centralized

and may not have been retained. Thus, the majority of the information used to evaluate the

environmental management practices and the environmental condition of the property at the former

NASB is based on information obtained over the past 30 years.

The following sections discuss the findings, actions, and notification requirements associated with the

past storage, release, or disposal of hazardous substances and/or petroleum products or other regulated

materials; and the transfer restrictions warranted to ensure protection of human health and the

environment and the environmental restoration process. Potential environmental impacts from adjacent

property conditions related to hazardous substances, petroleum products, or other regulated materials

are discussed, and additional information is provided in Tables B-2 and B-4. Table B-3 provides a brief

checklist of the environmental conditions that apply to the existing buildings and land areas within the

Transfer Parcels.


3.1 Comprehensive Environmental Response, Compensation and Liability Act

3.1.1 CERCLA Hazardous Substance Notice

In accordance with Title 42, U.S.C. §9620(h)(3)(A)(i), all deeds transferring federal property must provide

notice as to those hazardous substances which it is known, based on a complete search of agency files,

were stored for one year or more, released or disposed of on the property in excess of those threshold

quantities specified under 40 CFR 373, and all response actions taken to date to address any such

releases or disposals.

No hazardous substances are known to have been stored for one year or more, or released or disposed

of in excess of their respective threshold quantities on Parcels AIR-8, AIR-10, AIR-11, AIR-18, EDC-15,

EDC-28, EDC-34, and EDC-35. Thus, the transfer deeds for these parcels will not require a hazardous

substance notice.

Building 45 (Hazardous Waste Transfer Facility) is located on Parcel AIR-13. It provided temporary (less-

than-90-day) storage (transfer facility) for wastes (hazardous, oil, and universal). Since its construction in

1992, all hazardous/universal waste for the base was stored in Building 45 prior to off-site treatment

and/or disposal of the waste. The hazardous waste database printouts reviewed for the FOST for the

numerous wastes stored at the facility are included with Exhibit C. It is likely that some of the wastes

stored there (e.g., lead in batteries) exceeded their threshold quantities for CERCLA Hazardous

Substance Notice. While wastes were not stored for one year or more, notice is being provided due to

the volume, nature, and frequency of wastes stored. On Parcel EDC-27, lead was released to soil at the

former Machine Gun Boresight Range (MGBR), as further described in Table B-2. Parcel EDC-45 was

the location of former Building 13 where the NASB Supply Department stored hazardous materials and

distributed them to the various shops and squadrons that used them. Table 6-1 of the IAS (NEESA, 1983)

provides a list of the types of hazardous materials that would have been stored at former Building 13 at

the time of the IAS and where they would have been used on the Main Base. Former Building 13 was

also the location of a drum crushing operation, as summarized in Table B-2 and described in more detail

in the RCRA closure report for Building 102, which is located on the footprint of former Building 13 (Tetra

Tech, 2012e). On Parcel EDC-46, asbestos was released to the environment as described in Sections

3.1.2 and 3.6. The hazardous substance notice for Parcels AIR-13, EDC-27, EDC-45, and EDC-46 is

provided in Exhibit C, which notes (1) the requisite notice of the type and quantity of such hazardous

substances; (2) notice of the time the storage, release, or disposal took place; and (3) a description of the

remedial action taken, if any.


3.1.2 CERCLA Responses on the Transfer Parcels

Two MRP sites and one AOPI are located within the Transfer Parcels, as shown on Figures B-3 through

B-12:

Parcel AIR-10 - Former Munitions Bunker West (FMBW) MRP Site and Fire Training Area – West

(FTA-W) AOPI

Parcel EDC-27 - Machine Gun Boresight Range MRP Site

The Navy performed a Site Inspection (SI) comprised of a surface sweep and geophysical survey at the

FMBW in 2008. No munitions and explosives of concern (MEC) were encountered. In 2010, a Time

Critical Removal Action (TCRA) was conducted at the FMBW to follow up on subsurface anomalies

identified by the geophysical survey. No MEC, nor material documented as an explosive hazard (MDEH),

was found at the FMBW area; therefore, there were no MEC/MDEH clearance operations required and

the absence of MEC was confirmed. Surface soil samples collected in front of the Building 63 entrance in

May 2011 did not identify any site impacts, and no soil was removed as a result of the SI/TCRA (Tetra

Tech, 2012f). The Commanding Officer of the Naval Ordnance Safety and Security Activity (NOSSA)

submitted the After Action Report for Munitions Response Action at FMBW to the Chairman of the DoD

Explosives Safety Board (ESB) in February 2012 for review (NOSSA, 2012). The DoD ESB response

noted that the after action report would be filed with no issues noted (DDESB, 2012).

Waste liquids were reportedly transported to a concrete pad at the FTA-W and ignited for fire department

personnel to extinguish. The exact location of the reported FTA was not positively identified. Soil borings

were installed and groundwater sampling was conducted at the suspected location of the FTA-W in 2010.

Trace levels of VOCs and SVOCs were detected in soil and groundwater. Groundwater samples were

analyzed for two perfluorinated compounds (PFCs). Neither was detected. No further action was

recommended for the FTA-W (Tetra Tech 2014a).

The Navy conducted a limited soil removal action in May and June 2012 at the MGBR to address two

small surface soil “hot spot” locations on Parcel EDC-27 where elevated concentrations of lead and other

metals were found during previous investigations. Subsequent confirmation sampling results indicated

soil contamination at the former MGBR has been adequately addressed and there are no further soil

issues of concern at the site (Tetra Tech, 2013f).

No other impacts to the Transfer Parcels have been identified from these sites. Table B-2 provides

descriptions of the sites, including “Site Concerns”, “Investigation and Remedial Action Summary and


Status”, “Site-Specific Restrictions”, and “Site Impact on Subject Property” (including the need for any

land use controls).

There are no other IR, MRP, or AOPI sites located on the Transfer Parcels.

Based on site visit observations and records research performed during the RCRA closure process

(Section 3.2), sampling investigations were conducted within and around the following buildings on the

Transfer Parcels, as summarized in Table B-2.

Buildings 611 and 555 Area (Parcels AIR-8 and AIR-11)

Former Building 233 Area (Parcel AIR-13)

Former Building 586 Area (Parcel EDC-28)

Seabee Compound Buildings 633, 634, 635, and 661 Area (Parcel EDC-34)

Building 44 Area (Parcel EDC-35)

Detailed information is provided in their individual investigation reports (Tetra Tech, 2013c, 2014b,

2014d). Former Building 233 was located on a parcel (AIR-15) adjacent to Parcel AIR-13; however, the

investigation included collection of two soil samples on Parcel AIR-13 near a former transformer pad

associated with the building. None of these investigations resulted in a recommendation for additional

investigation or remedial action on the Transfer Parcels.

Historical Radiological Assessment The DoN undertook the assessment of radioactive materials at the former NASB under the authority of

CERCLA, which defines radionuclides as hazardous substances. A Historical Radiological Assessment

(HRA) was prepared pursuant to the DoN’s Environmental Restoration Program to fulfill the requirements

for a CERCLA preliminary assessment (NAVSEA, 2012). Information on all existing and former buildings

and areas was reviewed as part of the HRA. Those areas for which further review was recommended

were designated as “impacted” which meant only that further evaluation was warranted, not that the areas

were impacted by radiological materials. Further review was conducted for Building 41 on Parcel EDC-

15.

According to the HRA, half of Building 41 was used for parachute maintenance operations that included

maintenance of survival vests equipped with compasses and personnel markers which contained

radioluminescent material. The Historical Radiological Assessment (HRA) (TetraTech, 2012c) identified

the specific isotopes of concern in Building 41 to be tritium (H-3), strontium 90 (Sr-90), and radium 226

(Ra-226). A Task Specific Plan was developed to define the type and amount of surveys to be conducted

in the potentially impacted areas. The Task Specific Plan was designed to serve as a Final Status Survey


if no contamination were found. Surveys of the potentially impacted areas of Building 41 and an adjacent

concrete pad were performed in July 2012 with the results incorporated into the Final Status Survey

Report. (Tetra Tech, 2013a)

Based on the results of all surveys within the potentially impacted areas of Building 41, there was no

evidence of radioactivity on building surfaces resulting from Navy operations. All readings were

consistent with background, with no readings exceeding the release criteria. Therefore, the building was

recommended for unrestricted use without concern for radiological contamination. The Navy Radiological

Affairs Support Office approved the report. The Radiation Control Program of the Maine Department of

Health and Human Services (DHHS), Environmental Health Division, based on its observations of the

work performed in the field and the documentation provided, concurred with the recommendation in a

letter dated February 25, 2013 (Maine DHHS, 2013).

Asbestos Removal at Building 20 (Parcel EDC-46)

Asbestos records reviewed in preparation of the FOST indicated that soil of the dirt floor in the crawl

space beneath Building 20 was contaminated with asbestos (Sanders, 2011). The Navy had restricted

access to this area to prevent exposure. Although the area was not accessible and is in a crawl space,

the USEPA considered ACM in soil at Building 20 to constitute a release to the environment that required

a response. In June 2012, the Navy procured the services of a contractor to conduct a survey to

determine the extent of the contamination. Based on the findings of the survey, a soil removal was

conducted in the Building 20 crawl space in the fall of 2012, as further described in Section 3.6. Based

on the construction completion report issued for the asbestos-contaminated soil remediation, no further

remedial action is required (AGVIQ, 2013).

3.1.3 CERCLA Responses Not on the Transfer Parcels but Within 200 Feet

The following IR, MRP, and AOPI sites are within 200 feet of the Transfer Parcels, as shown on Figures

B-3 through B-12:

Parcel AIR-10 – IR Site 18 (West Runway Study Area)

Parcel AIR-11 – IR Site 4 (Acid/Caustic Disposal Pit) and IR Site 13 (Defense Reutilization and

Marketing Office Area)

Parcel AIR-13 – Hangars 1, 2, and 3 AOPI

Parcel EDC-15 - Hangars 1, 2, and 3 AOPI

Parcel EDC-27 – IR Site 9 (Neptune Drive Disposal Area) and Orion Street Skeet Range MRP Site

(formerly known as the Main Base Skeet Range)


Parcel EDC-35 – Buildings 7 and 10 AOPI

Parcel EDC-45 – IR Site 17 (Former Building 95)

As described in Table B-2, these sites are not expected to impact the Transfer Parcels; however, land

use controls (LUCs) may be required on the Transfer Parcels to protect the integrity of remedies

implemented at the sites or because they fall within areas requiring LUCs previously established by

CERCLA decision documents.

There are no other IR, MRP, or AOPI sites within 200 feet of the Transfer Parcels.

3.1.4 CERCLA Covenant

No hazardous substances and no petroleum products or their derivatives are known to have been

released or disposed of in excess of their respective threshold quantities on Parcels AIR-18, EDC-15,

EDC-28, EDC-34, and EDC-35. Therefore, in accordance with the requirements and limitations

contained in Title 42, U.S.C., Section 9620(h)(4)(D)(i), the deed transferring these parcels will contain a

covenant (see Exhibit G-1) warranting that any response action or corrective action found to be

necessary after the date of transfer for contamination existing on the property prior to the date of transfer

shall be conducted by the United States.

Hazardous substances were stored for one year or more, released or disposed of in excess of their

respective threshold quantities on Parcels AIR-13, EDC-27, EDC-45, and EDC-46, and a CERCLA SI and

TCRA were conducted on Parcel AIR-10. Therefore, in accordance with the requirements and limitations

contained in Title 42, U.S.C., Section 9620(h)(3)(A)(ii), the transfer deed for these parcels will contain a

warranty (see Exhibit G-2) that:

(a) All remedial action necessary to protect human health and the environment with respect to any

hazardous substances remaining on the property has been taken by the United States, and

(b) Any additional remedial action found to be necessary after delivery of the Quitclaim Deed shall be

conducted by the United States.

No hazardous substances are known to have been released or disposed of in excess of their respective

threshold quantities on Parcels AIR-8 and AIR-11. However, petroleum products or their derivatives have

been released on these parcels; therefore, the Title 42, U.S.C., Section 9620(h)(4)(D)(i) covenant is not

applicable.


3.1.5 CERCLA Access Clause

No hazardous substances and no petroleum products or their derivatives are known to have been

released or disposed of in excess of their respective threshold quantities on Parcels AIR-18, EDC-15,

EDC-28, EDC-34, and EDC-35. Therefore, in accordance with Title 42, U.S.C., Section 9620(h)(4)(D)(ii),

the deed transferring these parcels will contain a clause (see Exhibit G-1) granting the United States

access to the property in any case in which a response action or corrective action is found to be

necessary after the date of transfer of the property, or when such access is necessary to carry out a

response action or corrective action on adjoining or nearby property.

Hazardous substances were stored for one year or more, released or disposed of in excess of their

respective threshold quantities on Parcels AIR-13, EDC-27, EDC-45, and EDC-46, and a CERCLA SI and

TCRA were conducted on Parcel AIR-10. Therefore, in accordance with the requirements and limitations

contained in Title 42, U.S.C., Section 9620(h)(3)(A)(iii), the transfer deed will contain a clause granting to

the United States, its officers, agents, employees, contractors, and subcontractors the right to enter upon

the parcels in any case that a response action or corrective action is found to be necessary after the date

of transfer (see Exhibit G-2).

No hazardous substances are known to have been released or disposed of in excess of their respective

threshold quantities on Parcels AIR-8 and AIR-11. Petroleum products or their derivatives have been

released on these parcels. Therefore, the Title 42, U.S.C., Section 9620(h)(4)(D)(ii) access clause is not

applicable. However, the transfer deed for this parcel will include a Reservation of Access Clause

(Exhibit G-3) in accordance with the terms of the NASB Federal Facility Agreement (FFA) (DoN, USEPA,

State of Maine, 1990).

The transfer deeds will also contain a clause granting to the State of Maine its officers, agents,

employees, contractors, and subcontractors the right to enter upon the Transfer Parcels in the case that a

response action or corrective action is found to be necessary after the date of transfer, as described in

Exhibits G-1, G-2, and G-3.

3.2 Resource Conservation and Recovery Act The former NASB was a large quantity generator as defined by the 1984 Hazardous and Solid Waste

Amendments to the RCRA of 1976 and was assigned USEPA ID Number ME8170022018. RCRA

authority was delegated by the USEPA to the State of Maine. The RCRA Facility was defined as the

former NASB Main Base. The former NASB RCRA Facility needed to be closed to meet the hazardous

waste closure requirements of Maine Hazardous Waste Rules, Chapter 851, Standards for Generators,

Section 11, Closure, and other relevant rules pursuant to 38 M.R.S.A., Section 1301, et seq. Therefore,


the Navy prepared RCRA Partial Closure Reports to close the individual buildings, structures, and land

areas that comprise the former Main Base.

The closure activities performed on the Transfer Parcels are described in detail in the associated RCRA

Partial Closure Reports (Tetra Tech, 2010b-c, 2011a-q, 2012a-e, 2013b). These reports document the

records research; site visit observations; results of NASB Environmental Department personnel

interviews; sampling results if applicable; and response actions, if any, with respect to hazardous waste

generation, accumulation, or storage activity. The RCRA closure reports served as a major source of

information for this FOST, and relevant findings are incorporated into the appropriate sections.

Based on the site visit observations and records research findings, both interior and exterior sampling

investigations were conducted within and around select buildings on the Transfer Parcels to provide

information needed to achieve RCRA closure. More extensive soil and groundwater sampling

investigations were conducted for six areas. The investigation of one of these areas – the former Building

13 Drum Crusher Area (Parcel EDC-45) – was completed as part of the RCRA closure, as summarized

in Table B-2 and described in more detail in the RCRA closure report (Tetra Tech, 2012e). The

investigations for the other five areas listed in Section 3.1.2 are summarized in Table B-2. Investigations

involving limited sampling are described briefly below and in more detail in the individual RCRA closure

reports.

With one exception (sumps inside Building 647), limited sampling was performed outside the buildings

listed below to evaluate potential contamination from hazardous wastes, polychlorinated biphenyls

(PCBs) in paint, former PCB transformers, lead-based paint, and petroleum. Based on the analytical

results, there were no recommendations for further investigation or action at any of these buildings or

parcels, except Building 647 where solids from the sump in Room 108 were removed and disposed of

properly based on the test results. Details regarding the sampling and results for each building are

provided in the individual RCRA closure reports.

Parcel Building Media Sampled Analytes AIR-11 555 Soil PCBs AIR-13 292 Soil PCBs AIR-18 231 Soil Volatile Organic Compounds (VOCs), Semi-volatile Organic

Compounds (SVOCs), Volatile Petroleum Hydrocarbons (VPH), Extractable Petroleum Hydrocarbons (EPH)

AIR-18 231 Groundwater VOCs, SVOCs, VPH, EPH EDC-15 41 Soil PCBs EDC-15 41 Peeling Paint Toxicity Characteristic Leaching Procedure (TCLP) Metals EDC-15 647 Soil SVOCs, PCBs, Pesticides EDC-15 647 Sump Solids

(interior) TCLP Metals, SVOCs, Pesticides

EDC-34 404 Peeling Paint RCRA 8 Metals, PCBs EDC-34 404 Soil RCRA 8 Metals, PCBs EDC-46 20 Soil PCBs


Wipe samples were collected from floors, walls, and/or work benches inside the buildings listed below to

investigate the potential presence of hazardous waste residues.

Lead results for wipe samples were compared to the MEDEP criteria for lead-contaminated, settled dust

on floors and walls and other flat surfaces applicable for NASB RCRA closures. The other seven RCRA

metals were compared to available World Trade Center (WTC) Settled Dust Screening Values (WTC,

2003). Settled dust screening values are not available for SVOCs and PCBs. Based on the wipe

sampling analytical results, Buildings 611, 63, 555, 45, 647, 44, and 102 required cleaning to meet the

requirements for NASB RCRA closure with respect to hazardous waste residues. Upon completion of all

decontamination activities, the concentrations of RCRA 8 metals in the final post-cleaning wipe samples

collected in all of these buildings except Building 102 were below the associated clearance values. The

Navy encapsulated or applied protective coating to Building 102 floor and wall surfaces where post-

cleaning lead levels were greater than lead clearance values, and also removed range components and

the exhaust air system to complete the Building 102 decontamination. Provisions for future use and

occupation of Building 102 must provide for awareness and maintenance of the protective coatings (see

Exhibit G-2, Item 14).

The hazardous waste closure for the Transfer Parcels was completed in accordance with provisions of

the MEDEP Regulations Chapter 781, Standards for Generators of Hazardous Waste Section 11, and

was included in the RCRA Closure Summary Report for Former Naval Air Station Brunswick, Maine

(Tetra Tech, 2013e) that was accepted by MEDEP in a letter dated June 17, 2013.

Parcel Building Analytes AIR-8 611 RCRA 8 Metals, SVOCs

AIR-10 63 RCRA 8 Metals, SVOCs AIR-11 555 RCRA 8 Metals, SVOCs AIR-13 45 RCRA 8 Metals, PCBs AIR-18 231 RCRA 8 Metals EDC-15 41 RCRA 8 Metals EDC-15 647 RCRA 8 Metals, SVOCs, Pesticides EDC-27 55 RCRA 8 Metals EDC-34 633 RCRA 8 Metals EDC-35 44 RCRA 8 Metals, SVOCs EDC-45 102 RCRA 8 Metals


3.3 Presence of Petroleum Products and Derivatives

Petroleum products have been stored or managed in USTs, ASTs and oil-water separators on the

Transfer Parcels, as described in Section 3.4. Notice of the presence of petroleum products and

derivatives is provided in Exhibit D.

3.3.1 Petroleum Releases Originating on the Transfer Parcels

There are no known or suspected petroleum releases that originated on the Transfer Parcels that are

currently being investigated or cleaned up. Petroleum releases associated with tanks and requiring

excavation of contaminated soil have occurred in the past on Parcel AIR-8, as described in Table B-4.

Furthermore, a 1990 plan indicated contaminated soil should be removed to a depth of 3 feet and

replaced with clean fill in an approximately 5,000 square foot area between Buildings 611 and 555 on

Parcels AIR-8 and AIR-11. It is not known if this soil removal was related to a specific spill or to a former

septic system and/or former dry well located between the buildings. No documentation has been found

confirming that the planned soil removal was completed. This area was included in the soil and

groundwater investigation performed at Buildings 611 and 555 in November and December 2012.As

described in Table B-2, the technical memorandum for the soil and groundwater investigation did not

recommend additional investigation or remediation (Tetra Tech, 2014b).

A small oil spill occurred near Building 231 on Parcel AIR-18 when a pressure backup within an

emergency generator caused motor oil to discharge through the oil dipstick port of the engine. Soil and

groundwater sampling results indicated no impacts to Parcel AIR-18 that would require further action, as

described in Table B-4.

There are no other known or suspected petroleum disposals or releases to the environment that

originated on the Transfer Parcels.

3.3.2 Petroleum Releases Originating on Adjoining Properties

POL Site 1, the ONFF, is approximately 170 feet east of Parcel EDC-45. Petroleum constituents of

concern have been detected in the past in groundwater samples collected from ONFF monitoring well

MW-NASB-210 located near Building 102 (Indoor Small Arms Range) as shown on Figure B-11. Four

remedial actions have been completed at the ONFF to address soil and groundwater contamination.

Long-term monitoring results indicate the groundwater plume is stable and biodegradation is occurring.

No constituents of concern were detected in samples collected in June 2010 from MW-NASB-210 (ECOR

Solutions, 2010). Groundwater flow direction at the ONFF is to the southeast, and Parcel EDC-45 is

located southwest of the ONFF, as described in Table B-2.


MEDEP reported observing petroleum odors in the storm sewer system south of the ONFF

(approximately 450 feet northwest of Parcel EDC-28) in the fall of 2012. The Navy checked the storm

sewer and confirmed a petroleum odor in several catch basins near the ONFF and along First Street, in

one storm sewer inlet that is located on Parcel EDC-28, and in the drainage ditch at the storm sewer

outfall on the east side of First Street.

December 2012 VOC sampling results for the three temporary monitoring wells installed on Parcel EDC-

28 during the former Building 586 investigation did not indicate the presence of fuel contamination. There

were also no VPH or EPH detections in nearby monitoring wells MW-NASB-206 and MW-NASB-207

during the July 2010 ONFF groundwater monitoring event. These wells are on the east and west sides of

Parcel EDC-28, respectively. Furthermore, no significant PID responses, staining or odors were

observed during screening of the soil borings associated with the three temporary wells installed in EDC-

28 in late 2012.

The Navy initiated a limited investigation of the storm sewer system as part of further investigation of the

ONFF in November 2013 to try to determine the source of the petroleum odor. The investigation included

sample locations adjacent to, but not on, Parcel EDC-28. As described in Table B-2, these sample

results, along with the 2010 and 2012 groundwater monitoring results for wells on and near Parcel EDC-

28, do not indicate the parcel has been impacted by petroleum releases on the parcel or on adjacent

properties, including the former ONFF and the storm sewer system..

There are no other known or suspected petroleum disposals or releases to the environment that

originated within 200 feet of the Transfer Parcels.

3.4 Underground Storage Tanks, Aboveground Storage Tanks, and Oil-Water Separators

There are currently no underground storage tanks (USTs) located on the Transfer Parcels. Petroleum

products have been managed and stored in USTs formerly located on Parcels AIR-8, AIR-11, and EDC-

34, as described in Table B-5.

Parcels AIR-13, AIR-18, and EDC-27 each have one active aboveground storage tank (AST), while

Parcels AIR-8, AIR-13, AIR-18, EDC-15, EDC-27, EDC-34, and EDC-45 formerly had multiple ASTs that

stored petroleum products, waste oil, and glycol, as listed in Table B-6.

There are four active OWSs on the Transfer Parcels – one each on Parcels AIR-8 (Building 611), AIR-11

(Building 555), AIR-13 (Building 292), and EDC-34 (Building 635). Additional information about these

OWSs is provided in Table B-7. The OWSs were serviced annually as part of the OWS maintenance

program, which includes removal of accumulated petroleum products and excessive sludge, and proper

disposal of all collected petroleum-contaminated water, petroleum products, and sludge.


3.5 Munitions and Explosives of Concern

There are two MRP sites within the Transfer Parcels - the FMBW site (which includes Building 63, a

former High Explosives Magazine) on Parcel AIR-10 and the Machine Gun Boresight Range (MGBR) on

Parcel EDC-27, as described in Section 3.1.2. No MEC/MDEH was encountered during a surface sweep

and geophysical survey at the FMBW in 2008. One .30 caliber expended blank small arms cartridge case

was the only munitions-related item identified during a 2010 investigation of the subsurface anomalies

identified by the geophysical survey. The remaining anomalies were determined to be non-munitions

items (Tetra Tech, 2012f). Furthermore, site-related impacts were not identified by metals analyses

performed on surface soil samples collected in front of Building 63 in May 2011 (Tetra Tech, 2011r).

Parcel EDC-27 contained multiple ready magazines over time, and guns were handled in Building 55

while it was the base security building. The Navy removed a small amount of lead-contaminated soil (less

than two 55-gallon drums) at two “hot spot” locations on the MGBR in May 2012 to address the impact of

the site on Parcel EDC-27 (Tetra Tech, 2013f). No other impacts to the Transfer Parcels have been

identified from these sites.

Another MRP site, the Orion Street Skeet Range (formerly known as the Main Base Skeet Range),

borders Parcel EDC-27 to the north and east and is currently under investigation. While this site is not

expected to impact the parcel, LUCs may be required to protect the integrity of investigations and

remedies implemented at the site or because it falls within previously established areas requiring LUCs.

Table B-2 provides descriptions of these sites.

A Mobile Shooting Range (MSR) was located on the former Building 41B foundation east of Building 41

on Parcel EDC-15. A ready magazine/weapons pyrotechnics locker was also located on Parcel EDC-15.

The former MSR was situated on a concrete pad exterior to and east of Building 41, and was in operation

from 1993 to 2005. In February 1993, shortly after initiating shooting range operations, the MSR was

shut down due to a suspected exhaust fan leak; subsequently, nine surface soil samples were collected

downwind of the exhaust fan and analyzed for lead via the toxicity characteristic leaching procedure

(TCLP) methodology. TCLP lead concentrations ranged from less than 0.05 parts per million (ppm) lead

to 0.25 ppm lead, which are all below the TCLP lead standard of 5 ppm (DoN, 1993). As TCLP results

cannot be compared to MEDEP Remedial Action Guidelines (RAGs), which are based on total

contaminant concentrations in soil, MEDEP requested that the Navy collect and analyze soil and concrete

surface wipe samples for total lead in the vicinity of the former MSR location. The Navy collected seven

surface soil and two concrete surface wipe samples for total lead analysis in December 2013. Total lead

results for all soil samples collected were below the RAGs, indicating that historical MSR operations have

not adversely impacted surrounding surface soil conditions. The results for surface wipe samples


collected from the outdoor concrete pad where the MSR was located indicated low levels of lead that do

not represent an environmental hazard (Tetra Tech, 2014c).

Building 44 (Fitch Avenue Magazine) on Parcel EDC-35 was associated with weapons storage. Thus, it

was included in an Explosives Safety Inspection Close-Out of Potential Explosion Sites performed by

NOSSA in late March 2010 (NOSSA, 2010). The closeout inspection report indicated that these facilities

were “Empty/Clear of Explosives/Ammunition”, “Clean”, “Fire/Chemical Hazard Symbol Removed”,

“Marked as Empty”, and were “Secured to Prevent Use/Access.” NASB received site approval and

explosives safety certification approval on July 7, 2010 (NAVFAC, 2010) for all the potential explosion

sites included in the close-out inspection. A limited soil and groundwater investigation of the area around

Building 44 was performed at the request of MEDEP after the interior of the magazine required cleaning

when elevated concentrations of metals were identified during the RCRA closure process. The

investigation did not identify evidence of impact to the environment from Building 44 activities, as

described in Table B-2 (Tetra Tech, 2014d).

Building 102 on Parcel EDC-45 served as an indoor small arms firing range for its entire service

timeframe. Lead-contaminated residue from small arms was present inside the building as a result of this

activity. The building interior was decontaminated as part of the RCRA partial closure process (Section

3.2). Surface soil samples were collected in October 2011 to determine if soil had been impacted in the

area of the exhaust fan discharge on the west side of the Building 102 exterior. The samples were

analyzed for RCRA 8 metals and SVOCs (all PAH compounds), and compared to MEDEP RAGs and

representative background values. No exceedances of the RAGs for metals were reported. Lead

detections ranged from 6.6 to 9.3 mg/kg, well below the background level of 17.5 mg/kg. (Tetra Tech,

2012e)

There is no other known evidence of releases to the environment of munitions and explosives of concern

or munitions constituents on the Transfer Parcels.

3.6 Asbestos-Containing Material

Asbestos surveys were completed in 1998 and 2005. The 2005 inventory findings for the buildings and

structures on the Transfer Parcels are presented in Table B-8, along with 2011 Asbestos Containing

Building Materials Summaries prepared for the buildings by the NASB Asbestos Program Manager

(Sanders, 2011) prior to operational closure of NASB in May 2011. No friable, accessible, and damaged

asbestos was reported, other than at Building 20, as described below. The summaries are based on

information in the NASB files and did not include inspection of the buildings. Prior to any future

renovations or demolitions, previously untested materials considered suspect by USEPA, MEDEP, and

Occupational Safety and Health Administration (OSHA) regulations should be sampled and analyzed.


An asbestos warning sign was observed at the entrance to the crawl space beneath the first floor of

Building 20 on Parcel EDC-46 during the RCRA closure site visit. It appeared there could have been a

release of asbestos to the soil in the crawl space. Therefore, the Navy procured the services of a

subcontractor to perform an asbestos survey in June 2012. The contractor reported that the Building 20

crawl space is a level sandy floor with transite (asbestos containing cement board) and thermal system

insulation (TSI) surface debris present. The debris material appeared concentrated at the intersection of

the two wings of the building where the electrical room is located.

The contractor collected 24 soil samples from the crawl space floor for asbestos analysis. Seven of the

samples tested positive for asbestos, including four with a 1 percent or greater asbestos concentration.

The total area of asbestos-contaminated soil and asbestos debris was approximately 11,000 SF. No

suspect pipe insulation was observed on any pipes within the crawl space. Thus there appeared to be no

potential source for further contamination.

A second contractor was hired by the Navy to remove up to 6 inches of soil from the 11,000 square foot

crawl space area that showed visible signs of asbestos contamination and/or tested greater than 1

percent asbestos. Following the removal, 40 confirmation soil samples were collected from the crawl

space soil after it was visually cleared. Upon verification of visual clearance and the receipt of clean soil

sample results, a Certificate of Re-Occupancy for the crawl space was issued for Building 20 by a State of

Maine licensed Asbestos Inspector in January 2013 (AGVIQ, 2013).

Short segments of steam lines associated with the former heating system may be present on some of the

Transfer Parcels. Typically, the steam lines going into the buildings consisted of two steel pipes in

concrete trenches, one approximately 3 to 4 inches in diameter and a larger one 5 to 6 inches in

diameter. Some pipes were insulated with ACM and some were not. Specific documentation for the

Transfer Parcels is not available; therefore, for any work that could impact abandoned steam lines, it must

be assumed that ACM materials may be present (Sanders, 2010).

It is not known if the abandoned-in-place pipelines on Parcel AIR-13 that connected former Hangars 1, 2,

and 3 to the ONFF contained a tar exterior coating and fire-resistant asbestos wrapping, but it should be

assumed that ACM may be present.

The possibility remains for the presence of undiscovered ACM associated with underground utilities,

pipelines, or miscellaneous building materials. While this potential ACM does not pose a hazard to site

users, future renovation or demolition and/or subsurface work performed could result in friable and

damaged ACM hazards. Therefore, the GRANTEE must comply with all applicable State and Federal

laws relating to ACM management in order to ensure future protection of human health and the


environment during any future renovation/demolition activities or underground utility work. An Asbestos

Hazard Disclosure and Acknowledgment Form is included as Exhibit E to this FOST and will be provided

to the GRANTEE for execution at the time of transfer.

3.7 Lead-Based Paint

Federal lead standards established by USEPA and the Department of Housing and Urban Development

(HUD) quantify lead-based paint (LBP) as 0.5 percent lead by dry weight. LBP was banned for residential

use in 1978. Lead-containing paint is any paint which contains lead as determined by a testing laboratory

using a valid test method. OSHA regulations do not indicate a specific level of lead that is permissible

during construction and/or demolition activities. Current manufacturing standards for paint allow up to

0.06 percent lead for residential use. Industrial paint applications can contain much higher

concentrations. Other building materials may contain lead, as in roof flashing, caulking and vent sealant.

The NASB Asbestos Program Manager/Lead Coordinator prepared a Lead and Asbestos Containing

Building Materials Summary for most buildings on the former NASB (Sanders, 2011). Buildings on the

Transfer Parcels where LBP was identified are listed in Table B-3. A LBP Hazard Disclosure and

Acknowledgment Form, Exhibit F to this FOST, will be provided to the GRANTEE for execution at the

time of transfer.

3.8 Polychlorinated Biphenyls

PCB-containing equipment including PCB transformers (containing greater than 500 parts per million

[ppm] PCBs) and PCB-contaminated transformers (containing greater than 50 ppm PCBs but less than

500 ppm) were removed from the former NASB by 1995. According to NASB Environmental Department

personnel, the removal/replacement process began in the mid to late 1980s. A summary of information

provided in the NASB transformer database is presented in Table B-9 for the Transfer Parcels.

Transformers that were removed from service or replaced prior to 1988 are not in the database. Based

on available documentation and discussions with NASB Environmental Department personnel, there have

not been any documented leaks or releases from transformers in past use on the Transfer Parcels.

Areas that historically may have had PCB-containing equipment were tested as part of the RCRA closure

process. Soil samples were collected for PCB analysis around transformer pads or poles on Parcels AIR-

11 (Building 555), AIR-13 (Building 45 and former Building 233), EDC-15 (Buildings 41 and 647), EDC-34

(Buildings 404 and 661), and Parcel EDC-46 (Building 20) to determine if historical leaks from any PCB

transformers that might have been present had occurred. No PCBs were detected in any of the samples,

as described in the applicable RCRA closure reports and in the area investigation reports for the NMCB-

27 Seabee Compound and Former Building 233 (Tetra Tech, 2014d).


USEPA has advised that buildings constructed or renovated between 1950 and 1978 have the potential

to have PCBs contained within the caulking, and that PCBs can migrate from the caulk into air, dust and

surrounding material, such as wood, bricks and soil. Inasmuch as USEPA has yet to establish a link

between PCBs in caulking and public health risk, USEPA presently does not require that caulking in these

buildings be tested for the presence of PCBs. Notwithstanding, the GRANTEE is provided notice by

receipt of this FOST that buildings on the Transfer Parcels may have caulking containing PCBs based on

the year of their construction or possible renovations, and that all damaged caulking in the buildings and

materials in contact with, or soil beneath, the damaged caulking, if encountered, should be handled,

managed, and disposed of properly during maintenance and/or renovations by the GRANTEE.

Ballasts in fluorescent light fixtures manufactured prior to 1979 may contain sealed PCB-containing

components. A survey of station buildings/structures/facilities for PCB-containing light ballasts has not

been conducted; however, it is possible that surplus light fixtures could have been used up to 1982.

Therefore, it is assumed buildings/structures/facilities constructed up until 1982 may have light fixtures

with PCB components; however, many buildings that were constructed prior to 1982 have had interior

renovations and new light fixtures that do not contain PCBs may have been installed.

3.9 Pesticide Notification

The Transfer Parcels may contain pesticide residue from pesticides that have been applied in the

management of the property. A pesticide notification will be provided in the transfer deeds, as described

in Exhibit G.

3.10 Environmental Notices, Restrictions, and Covenants

Based on the current environmental condition of the Transfer Parcels as described in this FOST, certain

environmental notices, restrictions, and covenants will be included in the transfer deeds to ensure the

protection of human health and the environment and to prevent the interruption of any environmental

restoration activities to be conducted by the Navy, if required. Exhibit G contains the environmental

notices, restrictions, and covenants for the Transfer Parcels.

3.11 Environmental Compliance Agreements/Permits/Orders

The former NASB (Main Base) is a National Priorities List (NPL) site under CERCLA of 1980, as

amended. Thus, the Transfer Parcels on the Main Base are subject to the NASB Federal Facility

Agreement (FFA), October 1990, as amended, that was signed by the Navy, USEPA, and MEDEP (DoN,

USEPA, MEDEP, 1990). As indicated in Exhibit G of this FOST, the terms of the deeds for Transfer

Parcels on the former Main Base do not affect the rights and obligations of parties under the FFA. There


are no other environmental compliance agreements, permits, or orders associated with the Transfer

Parcels.

3.12 Availability of References

Select references contained in Exhibit A are available at the public information repository at the Curtis

Memorial Library, 23 Pleasant Street, Brunswick, Maine. With the closure of NASB, references are

available upon request from the Navy Caretaker Site Office located in Building 53 at the former NASB

and the Navy BRAC Program Management Office East, located in Philadelphia, PA.

3.13 Notification to Regulatory Agencies and Public The MEDEP and the USEPA have been advised of the proposed transfer. The USEPA and MEDEP

have reviewed this FOST and its exhibits, and their comments on this FOST have been incorporated or

otherwise addressed as detailed in Exhibit H. The FOST was made available to the public at the Curtis

Memorial Library for a period starting July 9, 2013 and ending August 8, 2013. Notice of the availability of

this FOST was provided in the Times Record (of Brunswick, Maine) on July 9, 2013. Copies of all

transfer deed documentation will be made available to the USEPA and MEDEP representatives upon

request after execution of the same.

4.0 FINDING OF SUITABILITY TO TRANSFER

' Based on the information contained in this FOST, and the notices, restrictions, and covenants that will be

contained in the deed, the Transfer Parcels are suitable for transfer.

Date

W5213868F

David Hellman Deputy Director NAVFAC BRAG Program Management Office

-23- Finding of Suitabllity to Transfer 2013-5

EXHIBIT A

References

1

REFERENCES AGVIQ Environmental Services, 2013. “Construction Completion Report, Asbestos Contaminated Soil Remediation, Building 20 Crawl Space, Former Naval Air Station Brunswick, Maine.” February. Department of Defense Explosives Safety Board (DDESB), 2012. “Memorandum for Commanding Officer, Naval Ordnance Safety and Security Activity, Subject: DDESB Receipt of After Action Report for Munitions Response Action at Former Munitions Bunker West Area, Naval Air Station, Brunswick, ME.” March. Department of the Navy (DoN), United States Environmental Protection Agency Region 1, and the State of Maine. 1990. “Federal Facility Agreement under CERCLA 120(h) as amended.” October. DoN, Base Realignment and Closure (BRAC) Program Management Office (PMO). 2006. “Final (Revision 2) Environmental Condition of Property Report for the Naval Air Station Brunswick, Maine.” May. James W. Sewall Company. 1953. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. June 29. James W. Sewall Company. 1958. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. October 9. James W. Sewall Company. 1978. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. November 22. James W. Sewall Company. 1981. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. October 17. James W. Sewall Company. 1984. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. April 23. James W. Sewall Company. 1989. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. April 2. James W. Sewall Company. 1993. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. November 8. James W. Sewall Company, 1997. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. May 27. James W. Sewall Company. 1997. NAS Brunswick Aerial Photographs. James W. Sewall Company, Old Town, ME. November 8. Maine Department of Environmental Protection (MEDEP). 2013. MEDEP Spills Database, Augusta, ME. Accessed March 2013. Maine Department of Health and Human Services (DHHS), Division of Environmental Health, Radiation Control Program, 2013. “Letter to Paul F. Burgio, NAVFACHQ, BRAC PMO, Subject: Free release of Hangar 4, Building 41, Bunkers 543 and 544, and Bunker 626 at the Former BNAS.” February, 2013. Matrix Design Group. 2007. “BNAS Reuse Master Plan. Prepared for the Brunswick Local Redevelopment Authority.” December.

2

Naval Air Station Brunswick (NASB). 2001. “Consensus Statement. No Further Actions Required Under CERCLA for Sites 14, 15, 16, and 18”. July. NASB Environmental Department Records. 2005. “Environmental Incident Log Books 1 and 2 (July 1988 – July 2005)”. NAS Brunswick, Maine. NASB Environmental Department Records. 2009. Master PCB Transformer Inventory, NAS Brunswick, Maine. April. NASB Environmental Department Records. 2010. Master/Historical Aboveground and Underground Storage Tank Inventory. NAS Brunswick, Maine. November. NASB PWD. 1943. “US Naval Air Station, Brunswick Maine, Building Site Plan Showing Locations of Underground Water Distribution Lines and Hydrants. NAS Brunswick, Maine. September. NASB PWD. 1946. “Map of US Naval Air Station, Brunswick, Maine, Showing conditions on June 30, 1946, NAS Brunswick, Maine. June 30. NASB PWD. 1952. Map of US Naval Air Station, Brunswick, Maine, Showing conditions on June 30, 1952, NAS Brunswick, Maine. June 30. NASB PWD, 1956. General Station Map, Enclosure 2. NAS Brunswick, Maine. NASB PWD, 1957. Map of US Naval Air Station, NAS Brunswick, Maine. NASB PWD, 1962. Map of Streets, US Naval Air Station, Brunswick, Maine. NASB PWD, 1975. General Development, Existing and Planned, Operations Area, US Naval Air Station, Brunswick, Maine. NASB PWD, 1983. Existing Conditions Map. Public Works Department Drawing No. 2157, NAS Brunswick, Maine. NASB PWD, 1989. Existing Conditions Map. Public Works Department Drawing No. 2157, NAS Brunswick, Maine. Revised April 2. NASB PWD, 2006. Brunswick Naval Air Station Base Map, NAS Brunswick, Maine. Naval Energy and Environment Support Activity (NEESA), 1983. “Initial Assessment Study for Naval Air Station Brunswick, Maine”. June. Naval Facilities Engineering Command Mid-Atlantic (NAVFAC Mid-LANT), 2007. “CERFA Identification of Uncontaminated Property at the Naval Air Station Brunswick, Brunswick Maine.” June. Naval Facilities Engineering Command Mid-Atlantic (NAVFAC Mid-LANT), 2010. “Letter to the Commanding Officer, NASB, Subject: Request for Explosives Safety Certification/Site Approval for Closure of Potential Explosion Site, Naval Air Station Brunswick, Maine. Enclosure (1) approved for explosives safety certification and final safety approval. July 7, 2010. Naval Ordnance Safety and Security Activity (NOSSA), 2012. “Memorandum for Chairman, Department of Defense Explosives Safety Board, Subject: After Action Report for Munitions Response Action at Former Munitions Bunker West Area, Naval Air Station, Brunswick, ME.” February. Naval Sea Systems Command (NAVSEA), 2012. “Draft Historical Radiological Assessment, History of the Use of General Radioactive Materials 1943 to 2011. Naval Air Station Brunswick.” May.

3

Sanders, 2011. “Lead and Asbestos Containing Building Materials Summaries.” NAS Brunswick Public Works Department. March and May. Tetra Tech, 2010a. “Third Five Year Review, Naval Air Station Brunswick, Maine”. September. Tetra Tech, 2010b. “Final RCRA Partial Closure Report for Building 20 – Navy College Office Parcel. Naval Air Station Brunswick, Maine.” October. Tetra Tech, 2010c. “Final RCRA Partial Closure Report for Building 551 – Security Generator Building. Naval Air Station Brunswick, Maine.” December. Tetra Tech, 2011a. “Final RCRA Partial Closure Report for Building 63 – West Bunker. Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2011b. “Final RCRA Partial Closure Report for Building 51 – NCIS/Fire Prevention Parcel. Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2011c. “Final RCRA Partial Closure Report for Building 636 – NMCB-27/Supply Building. Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2011d. “Final RCRA Partial Closure Report for Building 611 – AIMD Engine Test Cell Parcel. Naval Air Station Brunswick, Maine.” February. Tetra Tech, 2011e. “Final RCRA Partial Closure Report for Building 404 – NMCB-27/Storage. Naval Air Station Brunswick, Maine.” February. Tetra Tech, 2011f. “Final RCRA Partial Closure Report for Building 55 – Base Security Building Parcel. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2011g. “Final RCRA Partial Closure Report for Building 635 – NMCB-27/Vehicle Maintenance Building. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2011h. “Final RCRA Partial Closure Report for Building 44 – Fitch Avenue Magazine Parcel. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2011i. “Addendum December 2011, RCRA Partial Closure Report for Building 55 – Base Security Building Parcel. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2011j. “Final RCRA Partial Closure Report for Building 555 – Sonobuoy/Vehicle Storage Parcel. Naval Air Station Brunswick, Maine.” April. Tetra Tech, 2011k. “Final RCRA Partial Closure Report for Building 41 – Security Office Parcel. Naval Air Station Brunswick, Maine.” April. Tetra Tech, 2011l. “Final RCRA Partial Closure Report for Building 292 – Fire Department Building Parcel. Naval Air Station Brunswick, Maine.” May. Tetra Tech, 2011m. “Final RCRA Partial Closure Report for Building 647 – Bottled Gas Storage/Pest Control Shop Parcel. Naval Air Station Brunswick, Maine.” May. Tetra Tech, 2011n. “Final RCRA Partial Closure Report for Navy Land/Private Housing Area. Naval Air Station Brunswick, Maine.” May Tetra Tech, 2011o. “Revised Final RCRA Partial Closure Report for Building 45 – Hazardous Waste Transfer Facility Parcel. Naval Air Station Brunswick, Maine.” October.

4

Tetra Tech, 2011p. “Revised Final RCRA Partial Closure Report for West Base Area. Naval Air Station Brunswick, Maine.” November. Tetra Tech, 2011q. “Addendum, Final RCRA Partial Closure Report for Building 292 – Fire Department Building Parcel. Naval Air Station Brunswick, Maine.” December. Tetra Tech, 2011r. “Technical Memorandum, Buildings 62, 63 And 64, Surface Soil Assessment. Former Munitions Bunkers West Area, Former Naval Air Station Brunswick, Maine.” July. Tetra Tech, 2012a. “Addendum 2, RCRA Partial Closure Report for Building 55 – Base Security Building Parcel. Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2012b. “Revised Final RCRA Partial Closure Report for NMCB-27/Seabee Compound Area, Buildings 402, 403, 628, 629, 630, 631, 633, 634, 637, 659, 661, and 662. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2012c. “Final RCRA Partial Closure Report for Additional Transformer Locations. Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2012d. “Final RCRA Partial Closure Report for Former Buildings 14, 15 and 16 Parcel. Naval Air Station Brunswick, Maine.” April. Tetra Tech, 2012e. “Revised Final RCRA Partial Closure Report for Building 102 – Indoor Small Arms Range Parcel. Naval Air Station Brunswick, Maine.” August. Tetra Tech, 2012f. “Report For Munitions And Explosives Of Concern, Time Critical Removal Action At Former Munitions Bunker West Area, Naval Air Station Brunswick, Brunswick, Maine.” January. Tetra Tech, 2013a. “Final Status Survey Report, Building 41, Naval Air Station Brunswick, Brunswick Maine.” February. Tetra Tech, 2013b. “RCRA Partial Closure Report for Building 231 – Air Traffic Control Tower Parcel. Naval Air Station Brunswick, Maine.” March. Tech, 2013c. “Final Technical Memorandum, Former Building 586 Groundwater Assessment, Former Naval Air Station Brunswick, Maine.” March. Tetra Tech, 2013d. “Site Inspection Report for Munitions Response Program Sites Machine Gun Boresight Range and Skeet Range, Former Naval Air Station Brunswick, Brunswick, Maine.” April. Tetra Tech, 2013e. “RCRA Closure Summary Report for Former Naval Air Station Brunswick, USEPA Identification Number ME8170022018, Brunswick, Maine.” May. Tetra Tech, 2013f. “Technical Memorandum, Limited Soil Removal Completion, Machine Gun Boresight Range Munitions Response Site, Former Naval Air Station Brunswick, Brunswick, Maine.” December. Tetra Tech, 2014a. “Site Investigation for Four Areas of Potential Interest and Supplemental Groundwater Characterization of Buildings 225 and 252, Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2014b. “Technical Memorandum, Soil and Groundwater Investigation, Building 611/555 Area, Former Naval Air Station Brunswick, Maine.” January. Tetra Tech, 2014c. “Technical Memorandum, Former Mobile Shooting Range Investigation, Building 41 Parcel, Former Naval Air Station Brunswick, Maine.” January.

5

Tetra Tech, 2014d. “Multiple Area Investigation Technical Memorandum, Former Naval Air Station Brunswick, Maine.” January. U.S. Environmental Protection Agency, Environmental Photographic Interpretation Center,1987. “Site Analysis Brunswick Naval Air Station, Vol. I & 2.

World Trade Center, 2003. Table A-3 Settled Dust Screening Values and Supporting Toxicity Criteria from World Trade Center Indoor Environment Assessment: Selecting Contaminants of Potential Concern and Setting Health-Based Benchmarks, May.

EXHIBIT B

Figures and Tables

¬«24

¬«24

¬«123EDC-27

EDC-45

EDC-34

AIR-18

AIR-10

AIR-8

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FORMER NAVAL AIR STATION BRUNSWICKBRUNSWICK, MAINE

LOCATION MAP

FOST 2013-5 TRANSFER PARCELSFINDING OF SUITABILITY TO TRANSFER

Legend

Former BaseBoundary

Parcel Recipients

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MRRA Airport

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EDC-28EDC-45

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AERIAL VIEW


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Background Imagery: Bing Maps Aerial,2013.Note: Parcel boundary digitized using thehigh resolution orthophotograph (2007)downloaded from the Maine Office of GISwebsite. Distances, azimuths, and acreageare based upon digitized boundary.Actual boundary will need to be

Legend

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Parcel Recipients

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EDC-28

EDC-27

EDC-45

EDC-34

AIR-18

AIR-10

AIR-8AIR-11

EDC-35EDC-46

AIR-13

EDC-15

Former MunitionsBunker West

Site 18

Fire TrainingArea West

Site 13

Site 4

Site 9

Skeet Range Machine GunBore Sight Range

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Hangar 1

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Former Base Boundary

Federal to Federal Transfer

IR, POL, and MRP Sites and AOPIs

Building

Parcel Recipients

MRRA

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Note:IR - Installation RestorationPOL - Petroleum, Oil, LubricantMRP - Munitions Response ProgramAOPI - Area of Potential Interest

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FEATURES MAPPARCELS AIR-8 AND AIR-11


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FEATURES MAPPARCELS AIR-13, EDC-15 AND EDC-35




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Abandoned Fuel Pipeline

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Rail Line

Electrical Lines

Fiber Optic Lines

Sewer Lines

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Electrical Lines

Fiber Optic Lines

Sewer Lines

Steam Lines

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Water Line

Natural Gas

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FEATURES MAPPARCEL EDC-27



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FOST 2013-5 TRANSFER PARCELFINDING OF SUITABILITY TO TRANSFER



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@A Monitoring Well


Abandoned Fuel Pipeline

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Former Base Boundary

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@A Monitoring Well

Electrical Lines

Fiber Optic Lines

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Storm Lines

Water Line

Natural Gas



!( !( Fenceline


Building

Parcel Recipients

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MRRA Airport

Parcel IDEDC-45

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"/

"/

EDC-46(Building 20 and Land within the Building Footprint)

11

20

585583

31

24

³

0 100 20050

Feet

FIGURE NUMBER

SCALE

FILE

DATEREV

PER SCALE BAR


0 06/28/13

B-12






Legend

@A Monitoring Well


!( !( Fenceline

Rail Line

Electrical Lines

Fiber Optic Lines

Sewer Lines

Steam Lines

Storm Lines

Water Line

Natural Gas


Building

Parcel Recipients

MRRA

MRRA Airport

Parcel IDEDC-46

TABLE B-1 CURRENT AND FORMER BUILDINGS AND LAND AREAS

FOST 2013-5 TRANSFER PARCELSFORMER NAVAL AIR STATION BRUNSWICK, BRUNSWICK, MAINE

PAGE 1 OF 9

Parcel ID Building and Surrounding

Land

Year Constructed

Year Demolished

Approximate Building Area

(SF)Description

AIR-8 611 1967 NA 2,484

T-56 Engine Test Facility: Single-story building on concrete slab foundation; comprised of a large, out-of-airframe, engine test room, and a control room. The engine test cell is a corrugated, galvanized-steel structure having a semi-circular cross-section; trench drains are present inside and outside the building; natural-gas-fired boilers are located in a small, detached, boiler building at the southwest corner of B611; underground storage tanks (USTs), above-ground storage tanks (ASTs), an oil-water separator (OWS), electrical transformers, and a septic tank system are or have been associated with B611.

AIR-8Former Storage

StructureUnknown Between 1981

and 1984 Unknown Small storage structure located 60 feet southeast of Building 611.

AIR-10 63 1943 NA 1,010

Storage Facility: former High Explosives Magazine: also known as the West Bunker; earth-covered, metal-arch-roof on a concrete slab foundation with a steel-plate wing wall and security/blast door in front; interior has four areas created by wooden partitions and shelving; located within the FMBW Site; converted from a magazine to a storage facility between 1976 and 1983; most recently used by units on deployment for storage of gear, such as flight clothing, and for storage of spare parts.

AIR-10 Open Land NA NA NA Open, grassy land west of runways that includes B63; part of FMBW Site, and the Fire Training Area - West AOPI.

AIR-10 Former 137 Unknown After 1952 Unknown Abandoned residence west of runways south of B63.

AIR-11 555 1959 NA 6,400

Sonobuoy/Vehicle Storage: Single-story building on a concrete slab foundation.Original location was east of B250 and it was moved to current location in early1980s. The walls are constructed of metal siding with metal girts spanning betweenrigid frames. B555 was insulated some time after construction and has two rooms:the northern part was used for sonobuoy storage, and the southern part (originallythe sonobuoy shop) was most recently used for storage by the NAS Brunswick FirePrevention Department. The building was originally heated by two oil-fired hangingheaters and was converted to natural gas heat in approximately 2002. Two natural-gas-fired heaters are suspended from the ceiling in the central portion. B555 hasair conditioning.

W5213868F Finding of Suitability to Transfer 2013-5



PAGE 2 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

AIR-11Former Mobile Engine Test

Cell

1982 (Approximate) Unknown Unknown Engine Test Cell: formerly on a concrete pad southwest of B555. Included a 100-

gallon gas and oil interceptor that was connected to a drywell near Building 611.

AIR-13 45 1992 NA 3,000

Hazardous Waste Transfer Facility: Single-story building is a steel-framed structure on a concrete foundation. Personnel entrances and large garage doors are located on the northeast and southwest sides of the building. B45 contains an enclosed office and an enclosed flammable storage room, with the remainder of the space used as open waste storage areas. The small, exterior-entrance boiler room was added at the south corner of the building in 1999. B45 was heated by steam until 1999, and then by an oil-fired boiler until the base was converted to natural-gas heat in 2001. The concrete vault connection to the inactive central steam-heating system is located on the northwest side of the building.

AIR-13 292 1957 NA 10,665

Fire/Rescue Facility: The building consists of a three-story, steel-framed structureand a four-story, fire-hose drying tower with stucco siding on a concrete foundation.The first floor space consists of apparatus bays for housing fire fighting andemergency vehicles and equipment; office spaces; a dispatch room; a fitness room;a restroom; a mechanical room; and the hose-drying tower. A workbench area islocated along the northwestern wall of the apparatus bay area. The partial secondfloor space consists of a training room, kitchen, dining room and restroom, and thepartial third floor space consists of berthing rooms, a toilet and washroom, andoffices. There is an attached boiler room with similar construction. Three additionalstructures are located on the parcel, including a generator building, Structure I4(storage), and Structure Q (smoking area). B292 was originally heated via steam,and later by an oil-fired boiler, until the base was converted to natural-gas heat in2001.

AIR-13 Former 6 1943 Between 2000 and 2002 1,973 Bomb Sight Shop/Public Works Electrical Shop

AIR-13 Former 8 1943 Between 2000 and 2002 18,428 Public Works Administrative Office and Shops




PAGE 3 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

AIR-13 Former 48 1943 Between 2000 and 2002 3,260 Public Works Carpenter Shop

AIR-13 Former 254 Before 1976 Approximately 2002 Unknown Pump Test Pit/Drafting Tank used to store water for testing fire engine pumps

AIR-13 Former 450 1980 2011 375 Fire Department Alert Response OfficeAIR-13 Former 451 1980 2011 375 Fire Department Alert Training Office

AIR-13 Former 564 1965 Between 1983 and 1989 Unknown Radar Tower

AIR-18 231 2005-2006 NA 15,661

Air Traffic Control Tower: The building consists of a single-story, ground level,15,600-square-foot slab on-grade reinforced concrete and masonry structure and an84-foot-tall air traffic control (ATC) tower. The building housed offices and radarapproach control (RAPCON) equipment used to monitor NAS Brunswick air traffic.The eight-level ATC tower structure is located on the east side with the control cabon the eighth level. B231 has a natural-gas-fired boiler heating system, with theboiler room located in the building’s northern section. . An attached garage islocated at the southern end of the building. The building is on the basewidepotable water system and has a septic system for sewage. The building’s coolingequipment plant and emergency backup-power generator are located immediatelynorth of B231

EDC-15 41 1943 NA 10,526

Security Office: Also known as the Police Station, historically it was used astraining facility for the Fleet Airborne Electronics Training Unit Atlantic, and the westside (originally called B43) was a parachute maintenance shop. The building is asingle story with a wood-frame roof and wood-siding exterior on a concrete slabfoundation containing office spaces. B41 has a fuel-oil-fired furnace and waspreviously heated via steam heat. At the time of RCRA inspection, B41 was in poorcondition; the building contained office furniture and a large amount of generaldebris and trash.




PAGE 4 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-15 647 1978 NA 1,541

Bottled Gas Storage/Pest Control Shop: B647 is a one-story, concrete masonry unitwall structure on a concrete slab foundation. Interior space consists of an office,mixing room, mechanical room, utility room, storage rooms, locker room, restroom,and garage. An exhaust hood and a workbench with chemical sink were installed inthe mixing room. An oil-fired boiler heats B647. Structures A19 and A20 locatedsouth of B647 are steel hazardous material storage lockers with plywood floors andsteel, spill-containment bottoms. Each structure is 36 sq ft in area. The lockers wereused to store pesticides and related equipment and were still present at the time ofthe RCRA closure.

EDC-15 Former 41A 1943 Between 1966 and 1972 Unknown Supply / Classrooms located east of B41

EDC-15 Former 41B 1943 Between 1966 and 1972 Unknown Supply / Classrooms located east of B41

EDC-15 Former Mobile

Shooting Range

1993 2005 Unknown

Mobile Small Arms Shooting Range (indoor): Trailer placed on the concrete pad and foundation of former B41B, located east of B41. It was shut down between February and March 1993 to address problems with the ventilation system that potentially impacted soil in the area of the exhaust fan.

EDC-15 Former 51 1943 2000 1,870 Public Works Paint Locker/Paint ShopEDC-15 Former 73 1943 2000 64 Ready Magazine/Weapons Pyrotechnics LockerEDC-15 Former 74 1943 2000 3,072 Public Works Lumber ShedEDC-15 Former 75 1943 2000 332 Ammunition Belting Shop/Public Works Paint StorageEDC-15 Former 88 1943 2000 1,462 Maintenance Trainer Building/Public Works Storage

EDC-15 Former T-205 Between 1952 and 1956

Between 2002 and 2009 1,474 Public Works Storage/Pesticide Storage

EDC-15 Former 210 1943 Between 2002 and 2009 Unknown Beacon Tower




PAGE 5 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-27 55 2003 NA 10,014

Base Security Building: Former recycling facility from 2003 to 2005. Single-story,steel-framed, metal building on a concrete slab foundation. The eastern and centralinterior portions of the building consist of multiple offices and a classroom, and thewestern interior of the building includes storage and utility space, a restroom, amen’s locker room, and a gun-cleaning room. Access to the building is secure. B55 is heated by four natural-gas furnaces. Four exterior, pad-mounted, condensingunits, located on the northern side of B55, provide air conditioning to the building.

EDC-27 551 2005 NA 105

Security Generator Building: Wood-framed, wooden building (with sheetrock interior walls) was constructed on a concrete slab-on-grade foundation. B551 has a wooden awning on the northern side that covers an exterior, 250-gallon, double-walled steel, AST that stores fuel for the generator. B551 is not heated.

EDC-27 Former 69 Between 1943 and 1946

Between 2002 and 2009 68 Ready Magazine

EDC-27 Unknown Unknown Between 2002 and 2009 Unknown Small structure observed west of former B69

EDC-27 Former Ready Magazines 1987 Between 2002

and 2009 49 Ten 7' x 7' Ready Magazines

EDC-28 Land N/A NA N/ANorth side of parcel is open, grassy land and south side is wooded. Southeast of the corner of Admiral Fitch Avenue and Anchor Drive and East of abandoned fuel pipeline.

EDC-28 Former 586 Between 1943 and 1946

Between 1981 and 1984 821

Air Force Transmitter Building/Ham Shack/Amateur Radio Shack: Originally an Air Force transmitter building until approximelty 1965 when it was transferred to the Navy.

EDC-34 404 2004 NA 288NMCB-27/Storage: One-room, wood-sided and wood-framed structure, with a wood floor and asphalt shingles, mounted on concrete blocks. The interior is unfinished and unheated and is cold-storage space.

EDC-34 629 1974 NA 960

NMCB-27/Administration Building: Single-story, metal-sided structure on a concrete slab-on-grade foundation. The building interior consists of three office spaces and one reception area. The building is heated by natural gas-fired wall-mount heat and by electric baseboard heat.




PAGE 6 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-34 630 1974 NA 960NMCB-27/Administration Building: Single-story, metal-sided structure on a concrete slab-on-grade foundation. The building interior consists of three office spaces. The building is heated by natural gas-fired wall-mount heat and electric baseboard heat.

EDC-34 631 1974 NA 960

NMCB-27/Administration Building: Single-story, metal-sided structure on a concrete slab-on-grade foundation. The building interior consists of three office spaces. The building is heated by natural gas-fired wall-mount heaters and an electric baseboard heater.

EDC-34 633 1974 NA 2,640

NMCB-27/Administration, Communications and Garage Building: Single-story, metal-sided structure on a concrete slab-on-grade foundation. The eastern side of the B633 interior consists of two office spaces, one communication room, and one garage space. The center area (the portion joining the former B632 area with B633) consists of a communication area for repair of electronic equipment. The western side consists of a garage with a painted floor and plywood interior walls. B633 is heated by natural gas-fired wall-mount heaters and electric baseboard heaters. The garage area is unheated.

EDC-34 634 1974 NA 960

NMCB-27/Garage and Tool Storage Building: Single-story, metal-sided structure on a concrete slab-on-grade foundation. The building interior consists of a garage bay on the western side of the building, a tool storage room on the eastern side of the building, and a flammable materials room in the southeast corner of the building. Each of the rooms has particle-board interior walls, and there is an electrical service panel. The building is heated by two ceiling-mounted, natural gas-fired heaters.




PAGE 7 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-34 635 1974 NA 4,700

NMCB-27/Vehicle Maintenance Building: Steel-framed, metal building on a concrete slab-on-grade foundation. The interior of the building consists of two sections. One section is a large, open, vehicle maintenance area, with various support areas along its perimeter (work bench, tool storage, metal grinding, welding, parts washing, bermed oil-storage, tire changing, bathroom); the other is an internal, wood-framed, two-story section comprised of storage and office spaces located along the western and southern walls of B635. The interior walls of the building are constructed of sheetrock. A ceiling-mounted gas heater provides heat in the maintenance area and fluorescent lights are present throughout the building. The mezzanine area in the western end of the building houses a carpeted office area, while the southern mezzanine area (above the operations, training, and dispatcher’s offices) is used for storage.

EDC-34 636 1988 NA 3,900

NMCB-27/Supply Building: Metal-sided, steel-framed structure on a concrete slab on-grade. The interior features two sections: a vehicle-loading area, and an internal, wood-framed, two-story section comprised of storage and office spaces. The two-story, wood-framed section is located along the northern and western walls of B636. Within the loading area, B636 is currently heated by natural-gas, ceiling-mounted, space heaters; the office spaces are heated by electric baseboard heaters. A concrete pad, formerly used for equipment storage, abuts the building on the south side.

EDC-34 659 1984 (Approximate) NA 970

NMCB-27/Wood Shop: steel-framed, metal building on a concrete slab-on-grade foundation. The interior of the building consists of two sections: one section is a large, open, wood-shop area in the southeast portion of the building. The wood-shop area had five wood-working stations, as identified by the safety markings remaining on the shop floor. The other section is an internal, wood-framed, one-story section consisting of wood-framed, painted, sheetrock walls, which houses three office spaces and two building entrance/egresses.

EDC-34 661 1980 NA 600

NMCB-27/Storage Shed: Single-story, metal-sided structure constructed with wood columns over asphalt pavement. The B661 interior consists of five garage bays used for the temporary storage of NMCB-27 vehicles and/or equipment. The building is not heated.




PAGE 8 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-34 662 1997 NA 540

NMCB-27/Vehicle Storage Shelter: Single-story, metal-sided structure constructed with wood columns over asphalt pavement. The B662 interior consists of two garage bays used for the temporary storage of NMCB-27 vehicles and/or equipment. The building is not heated.

EDC-34 Former 632 1974 N/A 970 NMCB-27 Building combined with B633 in 1980

EDC-34 Former Trailer Park

Between 1952 and 1956

Between 1966 and 1974 Unknown Residental Trailer Park

EDC-35 44 1943 NA 1,258

Fitch Avenue Magazine: Earth-covered, metal-arch-roof magazine (bunker) built on a concrete slab foundation. The front of the structure is constructed of a steel-plate wing wall, with a security/blast door, and the interior walls are constructed of corrugated, galvanized steel sheets. B44 is not heated, and has a ventilation stack through the roof. Since the mid-1960s, B44 has not been used for torpedo or other munitions storage, but has been used as a personnel shelter, and for the storage of small-engine lawn mowers and snow blowers.

EDC-35 556 1957 NA 1,760Loading Dock: Cast-in-place concrete end and side loading dock, located north ofB44. This structure was used for loading and unloading materials and equipmentfrom rail lines formerly located east of the structure.

EDC-45 102 2004 NA 4,675

Indoor Small Arms Range: One story, with a rubber-membrane roof and precast-concrete exterior on a concrete slab foundation. B102 has a natural-gas-firedheating system. Used as a small arms firing range until 2009; the interior of thebuilding was decontaminated, dismantled, and decomissioned as a firing range in2012.

EDC-45 Former 13 1943 1998 6,049 Paint and Oil Storehouse/former hazardous materials supply storage EDC-45 Former 50 1943 1979 370 10,000-Gallon Used Oil Tank/Pump HouseEDC-45 Former 125 1943 1979 N/A 10,000-Gallon Aviation Lube Oil Tank

EDC-45 Former 224 Between 1952 and 1956 1999 4,000 Training Building

EDC-45 Former 559 unknown 1979 N/A 5,000 Gallon Used Aviation Lube Oil ASTEDC-45 Former 560 unknown 1979 N/a 5,000 Gallon Used Aviation Lube Oil AST




PAGE 9 OF 9


Land

Year Constructed

Year Demolished


(SF)Description

EDC-4620

(Building Footprint Only)

1943 NA 25,871

Navy College Office: Originally constructed as barracks. Two-story wood framedstructure on a concrete block foundation. Recently the building has been used forcollege/university classrooms, a bank branch office, a post office, and a militaryrelief center. The interior space includes office, classroom, bank and postal officespaces. B20 is heated by two natural-gas-fired hot water boilers located in anattached boiler room.

Notes:

AOPI - Area of Potential Interest OWS - oil water separators

AST - aboveground storage tank NMCB - Naval Mobile Construction Battalion

ATC - air traffic control PW - Public Works

FMBW - Former Munitions Bunker West RAPCON - radar approach control

NA - Not Applicable UST - underground storage tank


TABLE B-2SUMMARY OF ENVIRONMENTAL SITES AND OTHER INVESTIGATION AREAS ON OR NEAR TRANSFER PARCELS

FOST 2013-5 TRANSFER PARCELSFORMER NAVAL AIR STATION BRUNSWICK, MAINE

PAGE 1 OF 18


Site Numberand Name

Location Site ConcernInvestigation and Remedial Action Summary and

StatusSite-SpecificRestrictions

Site Impact on TransferParcel(s)

MRP Sites

Orion StreetSkeet Range,

(formerly calledthe Main BaseSkeet Range)

The OrionStreet SkeetRange isadjacent toParcel EDC-27to the northand east.

The Orion Street SkeetRange, formerly calledthe Main Base SkeetRange, was used inthe 1940s and 1950s.The primaryconstituents ofconcern are lead fromthe shotgunammunition and PAHsfrom the clay targets.Lead shot is not MEC.The site boundaryencompasses two 900foot overlapping semi-circles around a firingpoint. Previousdirections of fire facednorth (pre-1950) andeast (post-1950). Thelikely shot fall zoneextends approximately680 feet from the firingpoint.

An SI conducted in 2010 identified shallow surfacesoil (0 to 3 inches bgs) with antimony, arsenic, leadand PAHs (primarily benzo(a)pyrene) atconcentrations exceeding screening levels (TetraTech, 2013f). Additional sampling was conducted forthe 2011 RI within the 900 foot semi-circles. Sampleresults for 10 of 11 locations within the former BEQarea in the northeast part of the site were belowscreening criteria. The criterion for benzo(a)pyrenewas exceeded at one location. Additional samplingand a “hot spot” soil removal were performed at thislocation in May 2012 to facilitate property transfer ofthe BEQ portion of the site.

Since 2012, additional soil has been removed at theat the non-BEQ portion of the Site. The RI, which willinclude a risk assessment incorporating post-removalsample results, is in progress.

The Navy willcontinue to maintaina soil disturbance/excavation restrictionon most of the siteuntil site closure. Thenortheastern portionof the Orion StreetSkeet Range thatoverlapped theformer BEQ housingarea was found to besuitable for transferafter the hot spotremoval withconcurrence of theNavy, USEPA, andMEDEP.

No impacts to Parcel EDC-27 from the adjacent OrionStreet Skeet Range havebeen identified.

However, there is a base-wide groundwater userestriction on the NASBMain Base to preventimpact to the existinggroundwater flow systemand ongoing investigationsand/or remedial actions.



PAGE 2 OF 18


Site Numberand Name




Machine GunBoresight

Range(MGBR)

The MGBR islocated withinParcel EDC-27

The range was used inthe 1950s to align andtest fire aircraft-mounted guns into aberm. It may also havebeen used as a pistolrange. Reportedly ithas been inactive forthis use since early1960s. Based onreview of aerialphotos, the berm itselfwas intact in 1966,was present in the1970s and through1984; but may havebeen excavated by1989. Concernsincluded possibleimpacts of metals,propellants,nitroglycerin, orperchlorate to soil orgroundwater. The sitehas been investigatedunder the MRP.

The SI was conducted 2009-2010; the final SI reportwas issued in 2013. At two sample locations elevatedlead and other metals in soil were identified. Minorexceedances of MEDEP MEGs for chromium andmanganese in groundwater but there were no MCLexceedances. In May 2012 the Navy removed soil(4.5 and 2.25 cubic ft) at the two “hot spot” locationsin order to reduce overall soil lead concentrations atthe site. The final technical memorandumdocumenting the removal was issued in December2013.

None wererecommended in theSI or the TechnicalMemorandum. Basedon the two hot spotsoil removals and thesubsequent con-firmation samplingresults, soils at theformer MGBR havebeen adequatelyaddressed, and thereare no further soilissues of concern atthe site.

Impacts to Parcel EDC-27from the MGBR have beenaddressed through the “hotspot” soil removal. Noother impacts to soil orgroundwater wereidentified.




PAGE 3 OF 18


Site Numberand Name




FormerMunitions

Bunker West(FMBW)

The FMBWSite is partiallywithin ParcelAIR-10

The FMBW area wasused by Marines forweapons trainingbetween 1980 and2000. The site wasinvestigated under theMRP.

The 2008 Site Inspection (SI) included a surfacesweep and geophysical survey. 2008. No MEC wereencountered. A Time Critical Removal Action (TCRA)was conducted in 2010 to investigate subsurfaceanomalies identified through geophysics (Tetra Tech,2012g). One .30 caliber expended blank small armscartridge case was the only munitions-related itemidentified during investigation of the subsurfaceanomalies. The other anomalies were determined tobe non-munitions items, including nails, scrap metal,wire, fencing, a brass plate, metal chain with hooks,steel bars/posts, hydraulic cylinders, and wire rope.No MEC, nor material documented as an explosivehazard (MDEH), was found; therefore, there were noMEC/MDEH clearance operations required and theabsence of MEC was confirmed.

Surface soil was sampled for metals in May 2011near the bunkers (B62, B63 and B64). A TechnicalMemorandum noted that no exceedances ofscreening criteria were identified at B63, which islocated in Parcel AIR-10. Only arsenic and cadmiumwere present at concentrations exceeding criteria atB64 (south of the parcel), but average concentrationswere consistent with background. Site-relatedimpacts were not identified. No further action wasrecommended for the FMBW. MEDEP and EPAagreed with the NFA recommendation. In 2012, NavalOrdnance Safety and Security Activity submitted theafter action report to the DoD Explosives SafetyBoard, which filed the report with no issues noted.

No site-specific LUCsare required for theFMBW.

No impacts to Parcel AIR-10 from the FMBW wereidentified.




PAGE 4 OF 18


Site Numberand Name




Petroleum/Oil/Lubricant Sites

POL Site 1Old Navy FuelFarm (ONFF)

The ONFF islocated within 200feet of ParcelEDC-45. ParcelEDC-28 is southof and 450 ft awaythe ONFF but thestormwaterdrainage systemthat originates atONFF crosses theparcel.

A release of JP-5 from a567,000 gallon tankresulted in a dissolved-phase hydrocarbongroundwater plume andsoil contamination.Groundwater flows towardthe southeast, away fromEDC-45.

In 2012, petroleum odorswere detected in catchbasins at the ONFF anddowngradient, includingone stormwater inletlocated on Parcel EDC-28.

Biosparging, soil vapor extraction, air sparging, and soilremovals were conducted at the ONFF. Ground-water LTM wasconducted between 2000 and 2010. The area impacted byground-water contamination was further reduced due to bio-degradation. No EPH or VPH were detected in groundwaterdowngradient of the site in June 2010. Results fromsupplemental soil and groundwater studies conducted in July2011 indicated residual petroleum contamination in sub-surfacesoil and groundwater at several locations within the siteboundaries. A 2012 Technical Memorandum recommendedland use controls and continued monitoring for VPH. The Navyis considering removing additional soil within the ONFF.

The Navy investigated the storm sewer system within anddownstream of the ONFF in late 2013 to investigate thepetroleum odors in catch basins. Samples analyzed for PAHs,EPH and VPH were collected adjacent to, but not on, ParcelEDC-28 from catch basins, near a former OWS and in thestormwater ditch on the north side of First Street per the 2013ONFF Workplan. Results do not show petroleum impacts toParcel EDC-28. EPH and VPH were not present in any of thesamples except at very low levels in ditch sediment. PAHconstituents were rarely detected in most samples or were atlow levels, except in the ditch samples. The only PAHexceedance in ditch sediment was benzo(a)pyrene at 640 µg/kgat the outfall structure, and may be partly attributable to runofffrom First Street. No evidence of a significant petroleumrelease to the environment associated with the petroleum odorsin the catch basins was identified. The Navy plans to issue atechnical memorandum in 2014.

The ONFF will haverestrictions on subsurfacesoil, groundwater use,and residentialdevelopment. In addition,design of future buildings,structures or subsurfaceutilities/drains must takeinto considerationpotential methane/petroleum vapor buildupand include vapor barriersor other measures tomitigate vapor intrusion.

No current impacts togroundwater or soil have beenidentified on Parcel EDC-45from the nearby ONFF.Groundwater at the ONFF flowstoward the southeast, andParcel EDC-45 is southwest ofthe ONFF, not downgradient.

Parcel EDC-28 is southeast ofthe ONFF but groundwaterimpacts to the parcel from theONFF have not been observed.No indication of a majorpetroleum release to theenvironment or impact to ParcelEDC 28 was identified duringthe 2013 investigation ofpetroleum odors in the ONFFstorm drain system, nor duringthe 2012 soil and groundwatersampling investigation of theB586 area on Parcel EDC-28(see Page 13 of 18 of thistable).

There is a base-widegroundwater use restriction onthe NASB Main Base to preventimpact to the existinggroundwater flow system andongoing investigations and/orremedial actions.



PAGE 5 OF 18


Site Numberand Name




IR Program Sites

IR Site 4Acid/CausticDisposal Pit

Site 4 is eastand within 200feet of ParcelAIR-11

Liquid wastes, batteryacid, caustics,solvents, and paintthinners werereportedly disposedinto a pit. Building 584overlies the former pit.Building 584 and theDRMO laydown areawere identified in theHRA as potentiallyhaving radiologicalimpact. The potentialimpact toenvironmental mediawas considered lowbut warranting furtherassessment, and ascoping survey wasrecommended.

The No Further Action (NFA) ROD for soil was signedin 1998. Groundwater has been addressed as part ofthe Eastern Plume. However, if Building 584 isremoved, further investigations and remedial actionfor soil may be required per the ROD. The Navyconducted a limited geophysical survey withinBuilding 584 to more precisely identify the location ofthe former pit as part of the Data Gap Work Plan.

Soil excavation hasbeen restricted forsoils located directlybeneath the easternfoundation of Building584. The Navy is inthe process ofrevising the LUCs forSite 4. Changes willbe documented in anExplanation ofSignificantDifferences to theROD.

No impacts on Parcel AIR11 from Site 4 have beenidentified. Parcel AIR-11 isside gradient to Site 4.




PAGE 6 OF 18


Site Numberand Name




IR Site 9Neptune DriveDisposal Area

Site 9 is within200 feet ofParcel EDC-27.

Incinerator ash wasreportedly disposed intrenches in the early1940s; also paintsludge and metal shopwaste were disposed.Solvents were burnedon the ground withimpacts to soil,groundwater, andsediment. Thepotential forradiological impactfrom disposal of ash atSite 9 was identified inthe HRA. The potentialfor impact toenvironmental mediawas considered lowbut warrantinginvestigation, and ascoping survey wasrecommended.

ROD signed in 1999. LTM started in March 1999 andis ongoing. Extensive soil removal has beenconducted; 2008/2009 sampling confirmed the siteboundary to the south. The study identified additionalareas of ash present to the north. Additional work wasconducted in 2010 (Site 9 Soil Data GapInvestigation) to confirm the extent of ash-impactedsoil. The Navy’s findings indicate that the Site 9landfill area has been delineated, and does notextend to Parcel EDC-27.

Soil excavation/disturbance, ashlandfill disturbance,and groundwater useare restricted per theROD. Site 9 is alsolocated within theEastern Plumegroundwaterrestriction zone.

No impacts to Parcel EDC-27 from Site 9 soil orgroundwater have beendocumented based oninvestigations conducted todate.




PAGE 7 OF 18


Site Numberand Name




IR Site 13Defense

Reutilizationand Marketing

Office Area(DRMO)

Site 13 islocated within200 feet ofParcel AIR-11.

Site 13 containedthree USTs (10,000-gal fuel oil; 5,000-galwaste oil; and 5,000-gallon solvent storagetank). The USTs wereremoved in the late1980s but no soil wasremoved. Site 13 isone of three sources ofgroundwatercontamination in theEastern Plume. TheDRMO laydown areawas identified in theHRA as potentiallyhaving radiologicalimpact. The potentialimpact to environ-mental media wasconsidered low, butwarranting furtherassessment, and ascoping survey wasrecommended.

The RI was conducted and indicated some fuelconstituents and low levels of DDT in soil, and VOCsin groundwater. The ROD was signed in 1998. Theremedy selected was NFA for soil. The remedy forgroundwater is ongoing treatment in conjunction withthe Eastern Plume remedy. ROD signed 1998 andrequired evaluation in 5-yr reviews.

The 2nd 5-yr reviewrequired thatinstitutional controlsfor soils at Sites 4,11, and 13 bedeveloped. Thesewere established inthe Base Instruction.Groundwater use isrestricted per theEastern Plumeremedy. The Navy isin the process ofredefining LUCs forSite 13. Changes willbe documented in anExplanation ofSignificantDifferences to theROD.

There is no impact toParcel AIR-11 from Site13. The parcel is west andupgradient of the Site.




PAGE 8 OF 18


Site Numberand Name




IR Site 17Former

Building 95

IR Site 17 islocated east ofand adjacent toParcel EDC-45.

B95 housed base pestcontrol operations thatincluded storage,mixing, and disposal ofpesticides andherbicides from 1955until 1985, when theseoperations wererelocated to Building647.

The RI was conducted in 2008 and the report wasfinalized in July 2011. Approximately 1,350 cubicyards of contaminated soil and debris were removedin 1994; 117 tons of soil were removed south ofAvenue B in 2009; and 287 tons of soil were removednorth of Avenue B in 2010. An NFA ROD for soil wassigned in September 2011. The ROD for groundwateris pending results of LTM, which will continue foradditional rounds. The fall 2011 LTM results indicatedthat low levels of pesticides at concentrationsexceeding screening criteria are present at 3 Site 17groundwater sample locations.

Navy maintained soilexcavation ordisturbance andgroundwaterrestrictions at Site 17while the site wasunder investigation.

No LUCs are requiredfor soil in accordancewith NFA ROD forSite 17 soil.Groundwater is stillbeing monitored, anda use restriction isrequired pendingcompletion of theROD forgroundwater.

No impacts on ParcelEDC- 45 from Site 17 havebeen identified.Groundwater at Site 17flows toward the southeast,away from the transferparcel.




PAGE 9 OF 18


Site Numberand Name




IR Site 18 WestRunway Study

Area

Site 18 islocated at thenorth end ofthe FMBW Siteand issurrounded byParcel AIR-10property.

A sheen was observedon a seep along roadat the north edge ofthe FMBW in 1992. Asample collected in aused soda bottlecontained detectableVOCs but the resultswere not repeatable.Site 18 was identifiedin the HRA aspotentially havingradiological impact dueto the unknowncontents of the debrisobserved. Thepotential impact toenvironmental mediawas considered lowbut warranting furtherassessment, and ascoping survey wasrecommended.

A geophysical survey was performed and additionalsamples were collected. Test pits indicated thepresence of fill soil and some construction and metaldebris. Lab results for surface water, seep water, soil,and sediment were below federal standards. Also in1994, a radiological survey (for gamma radiation atthe surface) was conducted. All results wereconsistent with background. Some debris had beenremoved. No further action was required underCERCLA per 2001 Consensus Statement signed byEPA, MEDEP, and Navy (NASB, 2001).

None. No impacts to Parcel AIR-10 from Site 18 have beenidentified.

There is a base-widegroundwater use restrictionprohibiting access toground-water for anypurpose without priorwritten approval from theNavy and the applicableregulatory agencies toprevent impact to adjacentareas with ongoingremedial actions orinvestigations.



PAGE 10 OF 18


Site Numberand Name




Areas of Potential Interest and Other Site Investigation Areas

AOPI FormerHangars 1, 2, 3

The FormerHangars 1,2,3AOPI is locatedadjacent toParcels AIR-13and EDC-15.

The identifiedconcerns were thatgroundwater beneaththe apron might havebeen impacted byhistorical operationsand/or disposalpractices at thehangars, and thatthere potentially mighthave been leakagefrom fueling pitsassociated with a now-abandoned World WarII era fuel pipeline.

Results of a screening level groundwater investigationconducted in 2011 were reported in a TechnicalMemorandum. Minor exceedances of screeningcriteria for VOCs and EPH/VPH were found ingroundwater near former Hangar 1, which issouthwest of Parcels AIR-13 and EDC-15 andhydrologically downgradient. VOCs and EPH/VPHwere not detected above screening criteria ingroundwater near former Hangars 2 or 3, upgradientof Parcels AIR-13 and EDC-15. Inorganics with theexception of manganese were all reported atconcentrations below background values. No furtherinvestigation was required.

No action to addressVOCs, EPH/VPH, ormanganese ingroundwater wasrecommended in theapproved TechnicalMemorandum. Thearea is mostlycovered with theconcrete apron.Groundwater userestrictions havebeen included indeeds for the AOPIHangars 1, 2, 3 andadjacent parcels.

No impacts to Parcels AIR-13 or EDC-15 from theAOPI have been identified.

A soil disturbancerestriction will be placed onParcel EDC-15 because itis located in the historicallyindustrial area of the MainBase.

Also, there is a base-widegroundwater use restrictionon the NASB Main Base toprevent impact to theexisting groundwater flowsystem and ongoinginvestigations and/orremedial actions.



PAGE 11 OF 18


Site Numberand Name




AOPI FormerBuildings 7 and

10

AOPI FormerBuildings 7 and10 is southwestand within 200feet of ParcelEDC-35.

The concerns werebased on allegationsof dumping and leaksat undergroundstorage tanks at theformer aircraft andother maintenanceshops on the B7 & B10parcel.

A soil and groundwater investigation was conductedin October 2010 for B7 and B10. The final reportissued January 2014 noted that VOCs (primarily PCEand benzene), PAHs, and metals at levels exceedingscreening criteria were present in subsurface soilsamples (primarily at one boring location) and ingroundwater on the B7 and B10 AOPI. In May 2011,as part of the RCRA Closure, a test pit excavationconfirmed that a former B7 and B10 UST suspectedto be present (based on geophysical screening) hadbeen previously removed. The Navy is planning toconduct an investigation of low levels of VOCs ingroundwater which will include AOPI FormerBuildings 7 and 10.

A groundwater userestriction wasrecommended forAOPI B7 & B10.

No impacts to Parcel EDC-35 from the B7 & B10AOPI have been identified.The parcel is upgradient ofthe site. However, there isa base-wide groundwateruse restriction on theNASB Main Base toprevent impact to theexisting groundwater flowsystem and ongoinginvestigations and/orremedial actions.

AOPI FireTraining Area -

West(FTA-W)

The FTA-WAOPI is withinParcel AIR-10

Reportedly, wasteliquid was transportedto a concrete pad andignited for the firedepartment toextinguish. The exactlocation of the reportedFTA was not identified.

Soil borings were installed and ground-watersampling was conducted in autumn 2010. Results ofsampling issued May 2011. Trace levels of VOCs(tetrachloroethene, toluene) and SVOCs(naphthalene, 4-nitroanaline) were reported in soil.Trace levels of methylene chloride and the SVOCcaprolactam were detected in groundwater at levelsbelow screening criteria. Two perfluorinatedcompounds associated with fire-fighting foam wereanalyzed for but were not detected in the groundwatersample. No further action was recommended for theFTA-W (Tetra Tech 2014a).

Groundwaterrestrictions will beimplementedbasewide which willaddress MEDEPconcerns regardingthe exceedance ofthe EPA leaching togroundwater criterionfor tetrachloroethenein soil.

No impacts to Parcel AIR-10 were identified from theFTA-W AOPI and noactions were required.However, there is a base-wide groundwater userestriction on the NASBMain Base to preventimpact to the existinggroundwater flow systemand ongoing investigationsand/or remedial actions.



PAGE 12 OF 18


Site Numberand Name




FormerBuilding 13

AreaInvestigation

The FormerB13 waslocated inParcel EDC-45, partially inthe footprint ofcurrent B102

The parcel has alwaysbeen used forindustrial activities.Former B13 was aSupply Departmenthazardous materialsstorehouse whereincoming productswere temporarilystored prior todistribution to shopsacross the base.According to Mr.Edward Vigneault ofMEDEP, Former B13contained a 55-gallondrum crusher, andduring a 1990s sitevisit, he observed oilleakage under thedrum crusher insidethe building and notedcracks in the concretefloor. Drum storagemay have occurredwest of former Building13 based on an aerialphotograph. The Navyconducted moreextensive soilsampling than wastypical as part of theRCRA closureprocess.

Three surface and 16 subsurface soil samples werecollected in 2011 and analyzed for VOCs, EPH, VPH,SVOCs, RCRA 8 Metals and PCBs. Surface soilsamples were also analyzed for pesticides. VOCs,VPH, and PCBs were not detected in surface soil.Pesticide detections were below MEDEP residentialRAGs. Only arsenic at 16.5 mg/kg exceeded theMEDEP RAG (background value) at one location.Five PAHs were detected in soil samples at levelsexceeding the RAGs. In subsurface soil, VPH, andPCBs were not detected; and VOCs, EPH, SVOCsand metals were all below RAGs, except at 1 location,where 3 PAHs slightly exceeded the RAGs. Fouradditional surface soil samples were collected todetermine if soil had been impacted by the exhaustfan discharge on the west side of Building 102.Metals including lead were all below RAGs; PAHconcentrations were consistent with those identified inthe previous samples.

Based on sample results, soil contamination isprimarily PAHs confined to surface soil. The datawere presented in the RCRA Closure Report forBuilding 102. The report noted that the presence ofPAHs in soil is commonly the result of anthropogenicactivities, including combustible engine emissions.Specific potential sources include airplane, railroad,vehicle and central heating plant emissions (TetraTech, 2012e).

The investigationarea is not a Site andas such there are nosite-specificrestrictions. Due tothe industrialoperations in the areaand presence ofPAHs in soil identifiedduring the RCRAinvestigation, anotification of thepresence of PAHs insoil and requirementfor management ofsoil in Parcel EDC-45in accordance withthe MRRA MaterialsManagement Plan isrecommended.

PAHs are present insurface soil in Parcel;EDC-45 at levels thatexceed residentialscreening criteria. TheGrantee will need tomanage soil in accordancewith the MRRA MaterialsManagement Plan.

Reuse of the parcel isrestricted to excluderesidential and childcare(and similar) activities.

A soil disturbancerestriction will be placed onthe parcel because it islocated in the historicallyindustrial area of the MainBase.

There is a base-widegroundwater use restrictionon the NASB Main Base toprevent impact to theexisting groundwater flowsystem and ongoinginvestigations and/orremedial actions.



PAGE 13 OF 18


Site Numberand Name




FormerBuilding 586Investigation

Area

The areacomprisesParcel EDC-28

Former B586 wasidentified as an AirForce transmitter, aradio transmitter, anda “ham shack.” The AirForce operated aControl and WarningFacility (radar station)at the site from 1946until1965, and then itwas transferred to theNavy. A study wasconducted to addressMEDEP concernsabout potentialgroundwater impactsbased on experienceat other Air Forcefacilities.

In 2012, petroleumodors were reported incatch basins at theONFF and down-stream, including onestormwater inletlocated on ParcelEDC-28.

A screening level investigation was conducted in 2012to determine if there were impacts to soil andgroundwater from former Air Force operations. Therewas no evidence of VOC or petroleum contamination(i.e., elevated PID responses, odors, staining)observed in soil borings. Four groundwater samples(including one duplicate) from former Building 586 sitewere analyzed for VOCs in 2012. Only one VOC,carbon disulfide, was detected at a trace-level, 0.26ug/L, which is below all screening criteria. Twotargeted surface soil samples were analyzed formetals and PCBs. No exceedances of screeningcriteria were identified. No further action wasrecommended for the area (Tetra Tech, 2013c).

See also the POL Site 1, Old Navy Fuel Farm (ONFF)(Page 4 of 18 of this table) for a discussion of the2013 study of the storm water system on anddownstream of the ONFF, to investigate petroleumodors in stormwater catch basins. Evidence of apetroleum release to the environment associated withthe petroleum odors in the storm water catch basinswas not identified in the study.

None identified forthe former Building586 area.

No impacts to Parcel EDC-28 from former Air Force orNavy operationsassociated with formerB586 were identified.




PAGE 14 OF 18


Site Numberand Name




NMCB-27SeabeeCompoundInvestigationArea

The areacomprisesEDC-34

Buildings 633, 634,and 635 on theSeabee Compoundwere multi-use ormaintenance buildingsthat included garagesor maintenance areas.A pole-mountedtransformer thatpotentially containedPCBs was near B661.MEDEP requestedinvestigation of theseareas based on theirhistorical uses and toaddress a few datagaps identified duringthe RCRA partialclosure process.

Screening level investigation of soil and groundwaterwas conducted in 2012. Soil borings were installed at9 locations, and surface soil samples were collectedat 6 locations. Groundwater was sampled at only 2locations because water was not encountered aboveclay layers (8-15 ft thick) in three borings. Sampleswere analyzed for RCRA 8 metals, EPH, and VOCsand for PCBs near the transformer.

Arsenic and chromium were the only metals detectedin soil samples at concentrations exceedingresidential screening criteria. Arsenic levels werebelow NASB background values for mixed soil. Totalchromium concentrations were compared to criteriafor the more toxic hexavalent chromium but werebelow the residential Maine RAG and the NASBbackground value for mixed soil.

Acetone, carbon disulfide, and 2-butanone were theonly VOCs detected in soil but at levels well belowscreening criteria. EPH constituents were detected inseveral soil samples at levels below screeningcriteria. PCBs were not detected in the surface soilsamples collected near the transformer.

In groundwater, only 1 VOC (acetone) was detectedat both locations at levels below residential screeningcriteria. EPH fractions were not detected. Metalsdetected were at concentrations below residentialscreening criteria except for chromium. Dissolvedtotal chromium results in one sample exceededresidential RSL for hexavalent chromium, but not theMaine MEG or the federal MCL. Based on theseresults, NFA was recommended for the SeabeeCompound Investigation Area (Tetra Tech, 2014d).

None identified. No impacts to Parcel EDC-34 from former Seabeeactivities were identified.However, there is a base-wide groundwater userestriction on the NASBMain Base to preventimpact to the existinggroundwater flow systemand ongoing investigationsand/or remedial actions.



PAGE 15 OF 18


Site Numberand Name




Former Building233

InvestigationArea

Located north ofBuilding 9 andsouth of ParcelAIR-13. Theinvestigationarea is not onthe TransferParcels, exceptfor a formertransformer padlocation onParcel AIR-13.

Parcels EDC-15and EDC-35 areadjacent to theinvestigationarea.

The Former Building233 Investigation Areacontained former coaland oil-fired centralpower plants andassociated fuel storageUSTs, ash silos, andelectrical substations.Tank closures wereconducted inaccordance with staterequirements; but therewas still concern aboutsoil in the formerbuilding footprint, ashsilos, and at locationswith electricalequipment.

A geophysical survey and soil and groundwater samplingwere conducted in 2012. Eight borings installed informer B233 footprint, ash silos, and UST locations.Surface and subsurface samples were field screened forlead with XRF and petroleum products if odors or PIDreadings were indicated. Soil samples were analyzed forVOCs, SVOCs, EPH, PCBs and RCRA 8 metals. Leadlevels (XRF) were all below screening criteria. Evidenceof petroleum was only identified at one location. FivePAHS (primarily benzo(a)pyrene) were detected in soil atconcentrations exceeding MEDEP outdoor commercialworker RAGs. All PAH levels were less than MEDEPconstruction worker RAGs. VOCs, other SVOCs, andmetals were detected at levels below screening criteriaexcept for arsenic and chromium. The maximum arsenicconcentration (8.9 mg/kg) and maximum total chromiumvalue (23.6 mg/kg) were both below the respectiveNASB background UPLs for mixed soil. The maximumtotal chromium concentration exceeded the commercialRSL for hexavalent chromium but not the RAGs. NoPCBs were detected in any of 9 samples collected nearformer substations and transformers. Two samples werecollected at a former transformer pad location in thesouthern part of Parcel AIR-13. PCBs were also notdetected in any of the other soil boring samples.Groundwater was sampled at 3 locations; at one,petroleum constituents and 2 PAHs were detected atlevels exceeding screening criteria and petroleum odorswere noted. Total chromium concentrations exceededthe EPA RSL for hexavalent chromium but not the MaineMEG or MCL. Additional limited characterization of soiland groundwater was recommended for the portion ofthe investigation area south of, but not on, Parcel AIR-13due to presence of PAHs and petroleum residuals (TetraTech, 2014d).

None have beenidentified.

No impacts on Parcels AIR13, EDC-15 or EDC-35 fromthe Former Building 233Investigation Area wereidentified. Groundwaterflows to the southwest atB233. The transfer parcelsare upgradient of the FormerBuilding 233 InvestigationArea.




PAGE 16 OF 18


Site Numberand Name




Building 44InvestigationArea

The area islocated withinParcel EDC-35.

Four metals (arsenic,cadmium, chromiumand lead) were presentin settled dust in thebunker interior, whichwas cleaned perRCRA closureprotocols for NASB.MEDEP requested thatsoil and groundwatersampling beconducted on theexterior of B44,independent of RCRAclosure to determine ifelevated levels ofmetals were present inthese media, given theage and historical useof the building.

Composite soil samples were collected from 0-1 and1-2 ft bgs at 4 locations near the entrance to B44 formetals analysis. One groundwater sample wasanalyzed for dissolved metals. All metals detected insoil samples were at concentrations lower thanscreening criteria except for arsenic. Arsenic wasdetected in all samples at concentrations ranging from2 to 7.9 mg/kg, consistent with NASB site specificbackground UPL 5.6 mg/kg for upper sand and lessthan 14.2 mg/kg UPL for mixed soils. All values wereless than the Maine soil background. In groundwater,all concentrations of dissolved metals were lower thanthe applicable residential/drinking water screeningcriteria (Tetra Tech, 2014d). The final reportrecommended no further action.

None. No evidence ofimpact to theenvironment fromBuilding 44 activitieswas identified.

No impacts to Parcel EDC-35 from B44 activities wereidentified.

A soil disturbancerestriction will be placed onthe parcel because it islocated in the historicallyindustrial area of the MainBase.

Also, there is a base-widegroundwater use restrictionon the NASB Main Base toprevent impact to theexisting groundwater flowsystem and ongoinginvestigations and/orremedial actions.



PAGE 17 OF 18


Site Numberand Name




Building611/555InvestigationArea

The area islocated withinParcels AIR-8and AIR-11.

The area wasinvestigated todetermine if there wereimpacts due tooperations at theBuilding 611 enginetest cell and a formermobile engine test celllocated adjacent toBuilding 555. Spillsand UST/AST releaseswere addressed at thetime they occurred butthere wereuncertaintiesassociated with a 1990contaminated-soilcleanup, an historicaldrywell, an existing oil-water separator(OWS), a former septicsystem, and a spill ofAFFF, which may havecontainedperfluorinatedcompounds.

Soil (surface and subsurface) and groundwater weresampled in late fall 2012. Ten wells were installed at 6locations. Five PAHs were detected in one or moresurface soil samples at levels greater than theirrespective MEDEP commercial worker criteria. Theengine testing and general airfield operations wouldhave resulted in the deposition of PAH-containingparticulates from engine exhaust produced duringthese activities. Therefore, the presence of PAHs insurface soils was not unexpected.

In surface soil, arsenic exceeded the commercialworker RAG and the NASB Upper Sand backgroundUPL at one location. Subsurface soil arsenic levelswere less than the Maine commercial worker RAG.EPH fractions and several VOCs were detected belowresidential screening criteria. Perfluorooctanic acid(PFOA) and perfluorooctanesulfonic acid (PFOS)were detected in soil samples at trace levels (< 1ug/kg) and below their calculated screening values. Ingroundwater, EPH fractions and 3 VOCs werereported; only chloroform exceeded a residential RSL.Arsenic, manganese and sodium were present atconcentrations exceeded screening criteria, but weregenerally consistent with background. Trace levels ofPFOA and PFOS were detected in 6 of 10groundwater samples, at concentrations slightlyexceeding the EPA preliminary health advisory valuein 2 samples. While PFOS was detected at levelsslightly greater than its EPA Provisional HealthAdvisory (PHA) in two wells, the overall level of PFCdetections were very low and are not indicative of asignificant PFC release in this area (Tetra Tech,2014b).

Potential risk tocommercial,industrial, orconstruction workersfrom exposure tosoils containing PAHsat levels that mayexceed human healthexposure guidelinesshould be managedin accordance with anapproved soilmanagement plan.

Parcels AIR-8 and AIR-11have been impacted byengine testing and generalairfield operations thathave resulted in thedeposition of PAH-containing particulates insoil from engine exhaust.PAHs in soil should behandled in accordance withthe Materials ManagementPlan for MRRA Property,Brunswick Landing,Brunswick, Maine.

Residential reuse isprohibited in all of the AIRparcels.




PAGE 18 OF 18


Notes:

This is a summary of the current or former IR Program (IR) Sites Munitions Response Program (MRP) Sites, Petroleum, Oil, and Lubricant (POL) Sites, and Areas of PotentialInterest (AOPIs) located within, adjacent to, or within 200 feet of the Transfer Parcels. Site-specific restrictions currently in effect for the Sites are as noted in Site-specific RODsor summarized in the NASB Third Five-Year Review. Table B-2 indicates if restrictions are also warranted on the Transfer Parcels to prevent impact to ongoing investigations orto protect the integrity of existing remedies at adjacent Sites. This information is current as of January 2014.

Acronyms:

AFFF – Aqueous film forming foamAOPI – Area of Potential InterestAST – Above ground storage tankbgs – Below ground surfaceEPA – Environmental Protection AgencyEPH – Extractable Petroleum HydrocarbonsHRA – Historical Radiological AssessmentLTM – Long-term monitoringLUC – Land use controlMEC – Munitions and explosives of concernMEDEP – Maine Department of Environmental ProtectionMEG – Maximum Exposure GuidelinesMRP – Munitions Response Program

NASB – Naval Air Station BrunswickNFA – No further actionNMCB – Navy Mobile Construction BattalionONFF – Old Navy Fuel FarmOWS – Oil water separatorPAHs – Polycyclic aromatic hydrocarbonsPCBs – Polychlorinated biphenylsPFCs – Perfluorinated compoundsPFOA – Perfluorooctanic acidPFOS – perfluorooctanesulfonic acidPID – Photoionization DetectorPOL – Petroleum, Oil, Lubricant

RAGs – Remedial Action GuidelinesRCRA – Resource Conservation and Recovery ActROD – Record of DecisionRSL – Regional Screening LevelSVOCs – Semi-volatile organic compoundsUPL – Upper Prediction LimitUST – Underground storage tankVI – Vapor IntrusionVOC– Volatile organic compoundsVPH – Volatile petroleum hydrocarbonsXRF – X-ray fluorescence

TABLE B-3

ENVIRONMENTAL ISSUES BY BUILDING AND LAND AREA

FOST 2013-5 TRANSFER PARCELS

FORMER NAVAL AIR STATION BRUNSWICK, BRUNSWICK, MAINE

PAGE 1 OF 2

ParcelBuilding and

Surrounding LandYr Constr

Hazardous

Substances

Stored,

Released, or

Disposed of ?(1)

Petroleum

Products or

Derivatives

Released?

(see UST/AST

for Storage)

USTs(2)

ASTs(3)

OWSs(4)

Munitions(5)

LBP(6)

ACM(7)

Dielectric

Fluid

Equipment(8)

HRA(9)

AIR-8 611 1967 N Y Y Y Y N N Y Y N

AIR-10 63 1943 N N N N N Y Y Y N N

AIR-10 Open land NA N N N N N Y N N N N

AIR-11 555 1959 N Y Y N Y N N Y Y N

AIR-13 45 1992 Y N N Y N N N N N N

AIR-13 292 1957 N N N Y Y N Y N Y N

AIR-18 231 2005-2006 N N N Y N N N N Y N

EDC-15 41 1943 N N N Y N Y Y Y Y Y

EDC-15 647 1978 N N N Y N N N N Y N

EDC-27 55 2005 N N N Y N Y N N Y N

EDC-27 551 2005 N N N Y N Y N N N N

EDC-27

Open Land/ Machine

Gun Boresight

Range/Ready

Magazines

1940s Y N N N N Y N N N N

EDC-28 Former 586 1940s N N N N N N N N N N

EDC-34 404 2004 N N N N N N N N N N

EDC-34 629 1974 N N N N N N Y Y Y N

EDC-34 630 1974 N N N N N N Y Y N N

EDC-34 631 1974 N N N Y N N Y Y Y N

EDC-34 633 1974 N N N N N N Y Y Y N

EDC-34 634 1974 N N N N N N Y Y N N

EDC-34 635 1974 N N Y Y Y N Y Y N N

EDC-34 636 1988 N N N Y N N Y Y Y N

EDC-34 659 1984 N N N N N N Y Y N N

EDC-34 661 1980 N N N N N N Y Y N N


TABLE B-3

ENVIRONMENTAL ISSUES BY BUILDING AND LAND AREA



PAGE 2 OF 2

ParcelBuilding and

Surrounding LandYr Constr

Hazardous

Substances

Stored,

Released, or

Disposed of ?(1)

Petroleum

Products or

Derivatives

Released?

(see UST/AST

for Storage)

USTs(2)

ASTs(3)

OWSs(4)

Munitions(5)

LBP(6)

ACM(7)

Dielectric

Fluid

Equipment(8)

HRA(9)

EDC-34 662 1997 N N N N N N Y Y N N

EDC-35 44 1943 N N N N N Y Y Y N N

EDC-35 556 1957 N N N N N N N N N N

EDC-45 102 2004 Y N N Y N N N N Y N

EDC-46 20 1943 Y N N N N N Y Y N N

Notes:

Y/N - Yes, No NA - Not Applicable

(1) See Exhibit C regarding storage and release thresholds.

(2) All USTs have been removed; see Table B-5 for details.

(3) Includes former (removed) and current (closed or active) ASTs. See Table B-6 for details.

(4) See Table B-7 for current or closed OWSs.

(5) MRP Site or weapons assembly, handling, or storage.

(6) LBP was banned for consumer use in 1978; Y signifies LBP present based on testing or construction date (pre-1978) of building; N signifies LBP not present based on testing or

construction date (post-1978) of building. Established Federal lead standards by EPA/HUD quantify Lead Based Paint as 0.5% lead dry weight. Lead Containing Paint is any paint which

contains lead as determined by a testing laboratory using a valid test method. Occupational Safety and Health Administration regulations do not indicate a specific level of lead that is

permissible during maintenance, renovation, construction and demolition activities. Current manufacturing standards for paint allow up to 0.06% lead for residential use. Industrial paint

applications can contain much higher concentrations. All painted surfaces should be considered to contain some level of lead. See Exhibit F.

(7) While ACM may not have been identified in a building, analyses may not have been performed on all building materials such as sheetrock, joint compound, roofing shingles and

sealant or window caulking. Former steamlines with ACM may be present. ACM may be present on the subsurface abandoned-in-place avgas pipeline that is present in Parcel AIR-13.

Many materials continue to be manufactured containing asbestos. Materials considered suspect by EPA, MEDEP, and OSHA regulations should be sampled and analyzed prior to

maintenance, renovation and demolition activities, and should be presumed to contain ACM. See Table B-8 and Exhibit E.

(9) All buildings and land areas were reviewed for the HRA conducted at the former NASB. A "Y" in this column signifies that a location was identified for further evaluation in the HRA

and that a scoping survey was performed. A "N" indicates there is no reasonable possibility of residual radioactive contamination, based on historical documentation or results of

previous radiological survey information. As described in Section 3.1.2, the scoping survey for Building 41 found no evidence of radioactivity on building surfaces resulting from Navy

operations. All readings were consistent with background, with no readings exceeding the release criteria.

(8) Transformers, regulators and switches as indicated in NASB Master PCB Transformer Inventory Database, except as noted.


TABLE B-4SUMMARY OF DOCUMENTED SPILLS


PAGE 1 OF 3


Parcel IDLocation Date Material

Quantity(gallons)

MEDEP SpillID

Notes Source(1)(2)

AIR-8 B611 12/15/1988Hydraulic

fluidUnknown NA

Spill near OWS, backed up due to snow and rain the previousnight. Ordered Speedi Dry clean up.

NASBEnvironmentalIncident Log

AIR-8 B611 1/11/1989 JP-5 15-20 NAPersonnel overfilled fuel tank. Some discharged to stormdrain. Fire Department and test cell personnel used SpeediDry, covered drain with plastic and cleaned up.


AIR-8 B611 2/14/1989 Oil/fuel Unknown NAOWS backup due to flooding in storm drain. Absorbent padsapplied to recover as much oil as possible.


AIR-8 B611 6/19/1991 JP-5 Unknown P-619-1991

Originally thought to be jet fuel with waste oil and/or solvent.Reported to be petroleum constituents only. The release wasidentified when the OWS appeared to be backing up but wasactually associated with underground piping for an AST.About 50 cubic yards of impacted soil excavated anddisposed per report.

MEDEP SpillsDatabase.

AIR-8 B611 1/3/1994 Hydraulic oil 20 NAHydraulic lines ruptured during test. Quick response tocleanup/contain spill. Drains were plugged.


AIR-8 B611 5/5/1995No. 2 Fuel

OilUnknown

NA

Spill observed during tank removal (UST 10045-070).Contaminated soil was stockpiled in lined excavation andscheduled for removal on May 8, 1995.MEDEP notified.


AIR-11B555 2/16/1995

50/400gallons

Heating oil/oilywater

NA

Leaking furnace fuel-line discharged oil to a floor drain andthen to OWS; water with some oil pumped from sanitarysewer lift station; Navy personnel think migration contained atthe lift station. Note: see MEDEP spill record for 2/17/1995.


AIR-11 B555 2/17/1995 130 gallons No. 2 fuel oil P-102-1995Oil likely released into sanitary system. Note: see NASB spilllogbook entry for 2/16/1995.

MEDEP SpillsDatabase

AIR-11B555 10/5/2001 40 gallons AFFF NA

AFFF (aqueous film forming foam) released to OWS andlikely to sanitary sewer system.




PAGE 2 OF 3



Quantity(gallons)

MEDEP SpillID

Notes Source(1)(2)

AIR-13 Former B8 12/25/1998 200 gallons Transformer Oil NATransformer fell off lowboy. <1 ppm PCBs. Cleaned up. Norelease to the environment.


AIR-13 B292 5/30/1989 5-10 gallons JP-5 NARelease on fire department ramp as a result of an overfill of aBritish aircraft. No liquid entered storm drain. Cleaned withSpeedi Dry.


AIR-18 B231 UnknownEstimated 15

gallons

Oil fromgenerator

engineNA

An oil spill was identified during a March 31, 2009 site visit byCredere Associates at the emergency generator shed northof Building 231. Wet oil and oil staining were observed onthe floor of the shed in the area around the generator.Staining was observed outside the generator shed in a pavedwalkway area leading to a lawn but the spill did not appear toimpact a large area of soil. NASB Public Works Departmentindicated that an exhaust vent froze during the winter causinga pressure backup within the generator, and motor oildischarged through the oil dipstick port of the engine. Soiland groundwater were sampled. A Phase II ESA concludedthat contamination was not present and recommended nofurther action for the spill area. As part of the RCRA closurefor the Building 231 Parcel, soil closer to the location of thegenerator spill was sampled for VOCs, SVOCs, PAHs andEPH. Results indicated primarily low level EPH fractions insurface soil. PAHs were present at concentrations thatexceeded residential RAGs but not the Petroleum RAGs foran outdoor worker scenario. Groundwater underlying theBuilding 231 parcel is not impacted. No action for thegenerator spill was recommended.

RCRA PartialClosure Report forB231

Phase I EDDAPhase II ESA

EDC-15

FormerMobile

ShootingRange,

Former 41Blocation

BetweenFebruary andMarch 1993

Potentiallead release

Unknown NA

A Mobile (indoor) Shooting Range was located on the formerBuilding 41B foundation east of Building 41 between 1993and 2005. It was shut down between Feb and Mar 1993 toaddress concerns that exhaust was contaminating soil withlead. Nine soil samples from east of the exhaust fan wereanalyzed for TCLP lead. Results ranged from <0.05 parts permillion (ppm) to 0.25 ppm lead, below the TCLP standard (5ppm). No further action was taken or required by MEDEP. In2013, MEDEP requested that total lead samples be collectedprior to property transfer. The Navy collected 7 surface soiland 2 concrete surface wipe samples for total lead analysis inDecember 2013. Lead results for all soil samples were belowall MEDEP RAGs, indicating that historical mobile shootingrange operations had not adversely impacted surroundingsurface soil conditions. The results for surface wipe samples

NASBEnvironmental files:Memo dated August25, 1993 from theNavy to MEDEP

2014 TechnicalMemorandum,Former MobileShooting RangeInvestigationBuilding 41 Parcel(Tetra Tech 2014c)



PAGE 3 OF 3



Quantity(gallons)

MEDEP SpillID

Notes Source(1)(2)

from the outdoor concrete indicate presence of low levels oflead that do not represent an environmental hazard. Basedon these results no further action is warranted.

EDC-34NMBC-27Compound

8/15/2003 Sewerage unknown NASewer line/water main leak reported. No release of sewerageto waters or sediment


EDC-34NMBC-27Compound

9/8/2003 Oil unknown NA

POL (petroleum/oil/lubricants) reportedly spilled in adumpster truck due to improper disposal in dumpster. Spillscovered with sand. No POL found along the road. No releaseto waters of the United States.


EDC-45 Former B13 2/2/2000Oil from Non-

PCBtransformer

3 gallons NA

A non-PCB transformer damaged by a contractor leaked intothe sump below the transformer. The oil was cleaned up, thetransformer was replaced. No release to the environmentwas noted in the report.


Notes:

(1) Documents Reviewed: NASB Environmental Incident Log, Book 1, July 1988 to November 1999; NASB Environmental Incident Log, Book 2; February 2000 toJuly 2005. NASB Fire Department Spill Run Files 2002-2008. MEDEP Spills Database accessed March 13, 2013, contains reports for spills reported inBrunswick from March 1979 through 2012.

(2) DON (Department of the Navy), 1993. Memorandum from Chief Warrant Officer J.H. Bond, Assistant Public Works Director (NAS Brunswick) to Mike Hudson,Bureau of Oil and Hazardous Substances (MEDEP) regarding potential lead release at Mobile Shooting Range. August 25

Acronyms:

AST – aboveground storage tankEDDA – Environmental Due Diligence AssessmentEPH – Extractable Petroleum HydrocarbonsESA – Environmental Site AssessmentID – IdentificationMEDEP – Maine Department of Environmental ProtectionNA – Not applicableNASB – Naval Air Station BrunswickPAH – Polycyclic aromatic hydrocarbons

PCB – Polychlorinated BiphenylPOL – Petroleum, oil, lubricantsRAGS - Remedial Action GuidelinesSVOCs – Semi-volatile organic compoundsTCLP – toxicity characteristic leaching procedureVOC – Volatile organic compounds

TABLE B-5

UNDERGROUND STORAGE TANKS



Parcel Id

Building

/Tank

Number

Location

Tank

Registration

Number

Size (Gal) Product Year InstalledYear

RemovedStatus Remarks

611Engine Test

Cell10045-070 1,000 Fuel Oil #2 1983 1995 Removed Removed in May 1995; replaced with AST.

611.0Engine Test

CellN/A 1,000 JP#8 Jet Fuel 1967 2009 Abandoned

Tank was above-ground with underground piping. Piping abandoned in

place.

555.0Sonobuoy

Locker10045-065 2,000 Fuel Oil #2 1960 1990 Removed Removed in November of 1990; replaced with UST 555.1

555.1Sonobuoy

Locker10045-485 2,000 Fuel Oil #2 1990 2003 Removed Removed in October of 2003

635.0 NMCB-27 10045-072 5,000 Fuel Oil #2 1974 1990 Removed Removed in October of 1990

635.1 NMCB-27 10045-429 250 Lube Oil 1973 1989 Removed Removed in October of 1989

Notes:

Acronyms:

N/A - Not Applicable

NMCB - Navy Mobile Construction Battalion

AIR-11

AIR-8

UST data from NASB Environmental Department Master UST/AST database, updated by NASB Environmental Personnel 11/18/2010. Includes USTs installed from 1943 until 1999, and removed between 1988 and November 2010.

AST- Aboveground Storage Tank

EDC-34


TABLE B-6

ABOVEGROUND STORAGE TANKS

FOST 2013-5 TRANSFER PARCEL


PAGE 1 OF 2

Parcel IDTank

Number

Location

(Building)Size (Gal) Product Purpose Year Installed

Year

Removed

/Closed

Status(1) Remarks

AIR-8 A611.0 611 1000 JP#8 Jet FuelFuel for Testing of

Engines1967 2009 Removed

AST with underground piping. Formerly

located on containment pad east of Building

611.

AIR-8 A611.1 611 185 Waste Oil Waste Storage 1994 Unknown ClosedLocated on containment pad east of Building

611.

AIR-8 A611.2 611 1,000 #1 Oil Heating 1994 1999 Removed Relocated to Hangar 5

AIR-8 A611.3 611 100 JP#8 Jet FuelAPU Test Bench

Integral TankUnknown 2009 Removed

AIR-8 A611.4 611 330 #1 Oil Heating 1998 2002 Removed Formerly located in boiler room

AIR-8 A611.5 611 330 #1 Oil Heating 1998 2002 Removed Formerly located in boiler room

AIR-13 A45.0 45 1,000JP#8 Jet Fuel /

OilWaste Storage 1996 1999 Removed Relocated to Building 27

AIR-13 A45.1 45 250 #1 Oil Heating 1996 2011 Closed Located southwest of Building 45

AIR-13 A45.2 45 1,000Waste Fuel Oil

and Used OilWaste Storage 1996 2011 Removed Formerly located south of Building 45

AIR-13 A45.3 45 1,000Waste Fuel Oil

and Used OilWaste Storage 1999 2011 Removed Formerly located south of Building 45

AIR-13 A45.4 45 500

Used Oil, Aircraft

Fuel, Hydraulic

Fluid, and Engine

Oil

Waste Storage 2001 2011 Closed Located south of Building 45

AIR-13 A292.0 292 25 Diesel Generator Unknown 1998 Removed

AIR-13 A292.1 292 200 Diesel Generator 1998 N/A Active Good condition

AIR-13 A292.2 292 2,000 #1 Oil Heating 1999 2009 Closed Good condition

AIR-18 231.0 231 100 Hydraulic Oil Elevator 2005 N/A Active Located in elevator sump

EDC-15 A41.1Mobile Firing

Range60 Diesel Generator 1994 2009 Removed

EDC-15 A41.2 41 275 #1 Oil Heating 1999 2009 Removed

EDC-15 A41.3 41 275 #1 Oil Heating 1999 2009 Removed

EDC-15 A647.0 647 275 #1 Oil Heating 1999 2011 Closed Located in garage area of Building 647

EDC-27 A55.0 55 550 #1 Oil Heating 1999 2004 RemovedAssociated with Building 55 when use was

recycling center.

EDC-27 A55.1 55 550 #1 Oil Heating 1999 2004 RemovedAssociated with Building 55 when use was

recycling center.

EDC-27 A55.2 55 250 Waste Oil Waste Storage 2001 2004 RemovedAssociated with Building 55 when use was

recycling center.


TABLE B-6

ABOVEGROUND STORAGE TANKS

FOST 2013-5 TRANSFER PARCEL


PAGE 2 OF 2

Parcel IDTank

Number

Location

(Building)Size (Gal) Product Purpose Year Installed

Year

Removed

/Closed

Status(1) Remarks

EDC-27 A55.0 551 250 #1 Oil Generator Unknown 2006 ActiveAssociated with Building 55 emergency

generator (Building 551)

EDC-27 A55.1 551 275 Diesel Generator 2006 2006 RemovedAssociated with Building 55 emergency

generator (Building 551)

EDC-34 A631.1 631 275 #1 Oil Heating Unknown 1997 Removed

EDC-34 A635.1 635 70 Lube OilVehicle

MaintenanceUnknown 2010 Removed

Formerly located in vehicle maintenance

area inside Building 635

















EDC-34 A635.6 635 70 GlycolVehicle








EDC-34 A635.11 635 55 Waste Oil Waste Storage Unknown 1996 Removed

EDC-34 A635.12 635 25 Diesel Generator Unknown 2005 Removed

EDC-34 A635.13 635 30 Diesel Generator Unknown 2005 Removed

EDC-34 A635.14 635 250 Waste Oil Waste Storage 1996 2011 Closed Located southeast of Building 635

EDC-34 A636.0 636 550 #1 Oil Heating Unknown 2003 Removed Formerly located south of Building 636

EDC-45 N/A 125 10,000

Used Lube

Oil/Aviation Lube

Oil

Waste Storage 1943 1979 RemovedRemoval date approximate, based on 1979

historical aerial photograph and base maps.

Notes:

(1) Updated as of April 2013. AST data from NASB Master UST/AST database, which includes ASTs installed from 1967 through 2006 (or unknown) and removed or cleaned and closed

between 1993 and 2011.ST data from NASB Master UST/AST database, which includes ASTs installed from 1967 through 2006 (or unknown) and removed or cleaned and closed between 1993

and 2011.

NA = Not Applicable


TABLE B-7

OIL-WATER SEPARATORS


FORMER NAVAL AIR STATION BRUNSWICK, MAINE

Parcel ID LocationBuilding/ Area

Description

OWS

Number

Current

(2008 list) /

Former

(1996 List

or ECP)

Type

Discharge

point

(Sanitary or

Storm)

Volume

(gal)

Source

DescriptionDisposition/Notes Source of Information

AIR-8 611 Building 611, Test Cell 7/8Concrete

Chamber

Sanitary

Sewer1,000

Interior trench

DrainsActive. Cleaned 6/3/10 OWS List 1/1/08

AIR-8 611 Building 611, Test Cell NA Drywell Unknown UnknownGas and oil

interceptorFormer

RCRA Partial Closure

Report and Public

Works Drawings

AIR-11 555 Sonobuoy Locker 14/20Steel Box

in FloorSanitary 150 Floor Drains Active OWS List 1/1/08

AIR-11

555 Former

Mobile Engine

Test cell

Sonobuoy Locker NAGas and oil

interceptor

Drywell near

B611100

West side of

engine test cellFormer

RCRA Partial Closure

Report and Public

Works Drawings

AIR 13 292 Fire Station 10/15Concrete

ManholeSanitary 400 Floor Drains Active. Cleaned 10/25/11

OWS List 1/1/08; RCRA

Partial Closure Report

Addendum

EDC-34 635 Seabee Compound 8/13Concrete

ChamberSanitary 150

Repair Bay Floor

DrainsActive OWS List 1/1/08

Notes: Data current as of May 2013.

W5213868F Finding of Suitability Transfer 2013-5

TABLE B-8

SUMMARY OF ASBESTOS CONTAINING MATERIALS



PAGE 1 OF 4

Transfer

Parcel

Building

Number

Building

Identification

Construction

Date2011 Asbestos Containing Building Materials (ACM) Summary

(2)(3)(4)(5)

AIR-8 611T-56 Engine Test

Facility1967

PLM analysis indicates that peg board (transite board) in the control room contains asbestos, and acoustical panel, floor

coating, roof tar, vinyl tile and mastic do not. However, roof tar, tile and mastic will remain suspect until TEM analysis is

performed, in accordance with EPA recommendations.

AIR-10 63

Storage Facility

(Former High

Explosives

Magazine)

1943

ACM have been identified in some of the magazines. Laboratory analysis indicates that the caulking used to seal wall

panels and the tar sealant (expansion joint material) located at the slabs and at the exterior exhaust of some of the

magazines contain asbestos.

AIR-11 555Sonobuoy/Vehicle

Storage1959

PLM analysis indicates that the window glazing contains asbestos. Gypsum board and joint compound analyzed by PLM

were negative. Floor tile and mastic within office area have not been sampled and will remain suspect until laboratory

analysis is performed. Sprayed on asbestos insulation was abated during renovations and roof repairs. However, there

may be some remaining insulation along purloins and building frame behind fiberglass insulation and sheetrock.

AIR-13 45Hazardous Waste

Transfer Facility1992

ACM have not been identified in the building. In 1998 an Asbestos Survey was conducted. PLM analysis was performed

on gypsum board and joint compound with negative results. Materials considered suspect by EPA, MEDEP and OSHA

regulations shall be sampled prior to maintenance, construction or demolition, in accordance with EPA

recommendations.

AIR-13 292 Fire/Rescue Facility 1957

Suspect ACM have been identified in B292. In 1998 an Asbestos Survey was conducted for Operations and

Maintenance (O&M). Analysis was performed on building materials such as gypsum board, joint compound, plaster and

acoustical fife by PLM, and the results were negative. PLM analysis was also performed on the various colors of floor tile

and associated mastic with both positive and negative results. Major renovations have been conducted in the building

including abatement and replacement of floor tiles. However, asbestos-containing floor tile and mastic are still being

manufactured. Therefore, all floor tile and mastic shall remain suspect and should be sampled and analyzed prior to any

maintenance, renovation or demolition activities that have the potential to disturb the suspect material, in accordance

with EPA recommendations

AIR-18 231 Air Traffic Control 2005-2006

Analysis has not been performed on building materials to date. However, many materials are still manufactured that

contain asbestos. Materials considered suspect by EPA, MEDEP and OSHA regulations should be sampled and

analyzed prior to maintenance, renovation and demolition activities, in accordance with EPA recommendations.

EDC-15 41 Security Office 1943

Laboratory analysis using TEM indicates that approximately 7000 sq ft of asbesto-containing vinyl tile and mastic are

present in multiple layers throughout B41. Some areas of vinyl tile have negative results but the associated black mastic

is positive for asbestos. PLM analysis indicates there are approximately 1000 sq ft of asbestos-containing transite

material throughout the building located in the basement ceiling and some interior walls on the main floor. There are

approximately 1000 LF of asbestos-containing insulation on straight piping and pipe fittings. Records indicate that

asbestos abatement has been performed during numerous renovation activities. The potential exists for some remaining

asbestos containing materials that are inaccessible without destructive testing.

EDC-15 647

Bottled Gas

Storage/Pest

Control Shop

1978

ACM have not been identified in B647. An Asbestos O&M survey performed in 1998 indicated that gypsum board, ceiling

tiles and joint compound were found to be negative for asbestos. PLM analysis on reddish vinyl tile, beige vinyl tile, and

associated mastics was negative. However, until TEM analysis is performed on the floor tiles and mastic, shall remain

suspect, in accordance with EPA recommendations.

2005 Inventory Findings

ACM or PACM(1)

VFT, Mastic, Transite Board,

Straight Piping, Pipe Joints

Window Glazing

No known ACM

Renovated 1998; no known

ACM

PACM VFT, Mastic

None (new construction)

Caulk/Sealant

Transite Board


TABLE B-8




PAGE 2 OF 4

Transfer

Parcel

Building

Number

Building

Identification

Construction


(2)(3)(4)(5)2005 Inventory Findings

ACM or PACM(1)

EDC-27 55 Security Office 2005ACM have not been identified in the building. Materials considered suspect by EPA, MEDEP and OSHA regulations shall

be sampled prior to maintenance, construction or demolition, in accordance with EPA recommendations.

EDC-27 551Security Generator

Building2005

ACM have not been identified in B551. Sheetrock, spackling compound, and insulation were analyzed by PLM with

negative results. Materials considered suspect by EPA, MEDEP and OSHA regulations shall be sampled prior to

maintenance, construction or demolition, in accordance with EPA recommendations.

EDC-34 404 NMCB 27 Storage 2004ACM have been not been identified in B404. Results of pre-demolition sampling and analysis by TEM of roofing

materials were negative.

EDC-34 629 Administration 1974

ACM have been identified. The aluminum roof coating contains asbestos, as well as the caulking on the vent pipes and

siding panels. Laboratory analysis using PLM indicated that wallboard, joint compound and white floor tile were negative

but the associated black mastic contains asbestos. However, all floor tiles shall remain suspect until TEM analysis is

performed. Materials considered suspect by EPA, MEDEP and OSHA regulations should be sampled prior to

maintenance, renovation and construction or demolition, in accordance with EPA recommendations.

EDC-34 630Administration

Building1974






EDC-34 631 Administration 1974






EDC-34 632 NMCB 27 Storage 2006ACM have not been identified. Materials considered suspect by EPA, MEDEP and OSHA regulations should be

sampled prior to maintenance, renovation and construction or demolition, in accordance with EPA recommendations.

EDC-34 633

Administration,

Communication, and

Garage

1974






EDC-34 634Garage and Tool

Storage1974






None (new construction

2005)

Not included in table

VFT, Mastic, Aluminum

Coating Roofing, Caulk,

Sealant




Sealant



Sealant

New 2006



Sealant



Sealant


TABLE B-8




PAGE 3 OF 4

Transfer

Parcel

Building

Number

Building

Identification

Construction



ACM or PACM(1)

EDC-34 635NMCB 27 Vehicle

Maintenance1974

ACM have been identified. Laboratory analysis using PLM indicated that wallboard, joint compound and white floor tile

were negative but the associated black mastic contains asbestos. However, all floor tiles shall remain suspect until TEM

analysis is performed. Materials considered suspect by EPA, MEDEP and OSHA regulations should be sampled prior to


EDC-34 636 NMCB 27 Supply 1988




performed. Materials considered suspect by EPA, MEDEP, and OSHA regulations should be sampled prior to


EDC-34 659 Woodshop 1984

ACM have been identified in the building. The aluminum roof coating contains asbestos, as well as the caulking on the

vent pipes and siding panels. Laboratory analysis using PLM indicated that wallboard, joint compound, and white floor

tile were negative but the associated black mastic contains asbestos. However, all floor tiles shall remain suspect until

TEM analysis is performed. Materials considered suspect by EPA, MEDEP, and OSHA regulations should be sampled

prior to maintenance, renovation and construction or demolition, in accordance with EPA recommendations.

EDC-34 661 Storage Shed 1980

ACM have been identified in the [metal] buildings of the NMCB compound. The aluminum roof coating contains

asbestos, as well as the caulking on the vent pipes and siding panels. Laboratory analysis using PLM indicated that

white floor tile was negative but the associated black mastic contains asbestos. However, all floor tiles shall remain

suspect until TEM analysis is performed, in accordance with EPA recommendations.

EDC-34 662 Vehicle Storage 1997

ACM have been identified in the [metal] buildings of the NMCB compound. The aluminum roof coating contains

asbestos, as well as the caulking on the vent pipes and siding panels. Laboratory analysis using PLM indicated that

white floor tile was negative but the associated black mastic contains asbestos. However, all floor tiles shall remain

suspect until TEM analysis is performed, in accordance with EPA recommendations.

EDC-35 44Fitch Avenue

Magazine1943

Laboratory analysis using PLM indicates that asbestos-containing caulking was used to seal panels, and asbestos-

containing tar sealant is located at the slab.

EDC-35 556 Loading Dock 1957 No data summary available. Concrete loading dock.

EDC-45 102Indoor Small Arms

Range2004

Analysis has not been performed on building materials such as floor tile and mastic, joint compound, roofing sealant or

window caulking, to date. Many of these materials continue to be manufactured containing asbestos. Materials

considered suspect by EPA, MEDEP and OSHA regulations should be sampled and analyzed prior to maintenance,

renovation and demolition.

None (new construction

2004)


PACM Calk, Tar


Unknown

Unknown



Sealant

Unknown


TABLE B-8




PAGE 4 OF 4

Transfer

Parcel

Building

Number

Building

Identification

Construction



ACM or PACM(1)

EDC-46 20 Navy College Office 1943

Laboratory analysis using TEM indicates that ACM vinyl tile and mastic are present in multiple layers throughout the

building. Some of areas of vinyl tile have negative results but the associated black mastic is positive for asbestos. PLM

analysis indicates there are approximately 550 square feet of asbestos containing transite material between the ceiling of

the 1st and the flooring on 2nd floor, in one location. The soil in the crawl space is contaminated from thermal systems

insulation debris. Records indicate that during renovation activities, some asbestos abatement may have been

performed. Therefore, the potential exists for some remaining asbestos containing materials that are inaccessible

without destructive testing. During the September 2010 RCRA partial closure inspection, the entrance to the crawl space

had an asbestos warning sign indicating the presence of asbestos fibers, and the dirt floor of the crawlspace was

covered with plastic sheeting (approximately 12,500 square feet). Per recommendations of the June 1998 asbestos

inspection, the entrance to the crawl space should be sealed and a sign posted at the entrance to indicate that only

workers with proper protective equipment should be allowed to enter the crawl space.

EDC-46 20Navy College Office

(Crawl Space)1943

Based on the conditions reported above, the Buildings 20, 200, and 211 crawl space asbestos survey was conducted in

June 2012 by EMI, an MEDEP-licensed asbestos consultant. The total area of asbestos-contaminated soil and asbestos

debris in the crawl space of B20 was approximately 11,000 SF. No suspect pipe insulation was observed within the crawl

space. Based on the results, the Navy conducted a crawl space soil removal in three buildings including B20 in the fall of

2012. A certificate of re-occupancy dated 1/7/2013 was issued based on confirmation sample results documented in the

Construction Completion Report(3)

.

(1)

(2)

(3)

(4)

(5)

EPA - United States Environmental Protection Agency OSHA - Occupational Safety and Health Administration

FOST - Finding of Suitability to Transfer

MEDEP - Maine Department of Environmental Protection

NASB - Naval Air Station Brunswick

NMCB - Navy Mobile Construction Battalion

O&M = Operations and Maintenance

Transite, VFT, Mastic, Soil

TEM = Transmission Electron Microscopy

VFT = Vinyl Floor Tile

Construction Completion Report, Asbestos Contaminated Soil Remediation, Building 20 Crawl Space, issued February 2013.

Not applicable

EPA recommends that bulk materials found negative for asbestos or less than one percent asbestos by polarized light microscopy (PLM) that fall into any of five dominantly nonfriable categories be

analyzed by an additional method, such as transmission electron microscopy (TEM).

For some buildings, analysis has not been performed on building materials such as floor tile and associated mastic, joint compound, roofing sealant or window caulking, to date. Many of these materials

continue to be manufactured containing asbestos, including gaskets for piping and boilers. Materials considered suspect by EPA, MEDEP and OSHA regulations should be sampled and analyzed prior to

maintenance, renovation and demolition activities, in accordance with EPA recommendations.

Acronyms:

Notes:

ACM - Asbestos Containing Material

PACM = Presumed Asbestos Containing Material

PLM = Polarized Light Microscopy

From Environmental Condition of Property Report Table 4-13 for the Naval Air Station, Brunswick, Maine, May 2006 as compiled by Carla Sanders, NASB Asbestos Program Manager, 2005.

Existing Conditions-Lead and Asbestos Containing Building Materials Summaries based on historical files and prepared for individual buildings by Carla Sanders, NASB Asbestos Program Manager in

2010 and 2011.


TABLE B-9

SUMMARY OF CURRENT AND REMOVED EQUIPMENT CONTAINING DIELECTRIC FLUID



PAGE 1 OF 2

Parcel ID Building Description/Location Status Serial Number Type Class

PCB

Concentration

(PPM)

Date

Removed Or

Disposed

AIR-8 611 38-kVa non-PCB-containing, pole mounted R GE G567256-66Y Transformer Non-PCB <50 Unknown

AIR-8 611 38-kVa, non-PCB-containing, pole mounted R GE G567255-66Y Transformer Non-PCB 0 Unknown

AIR-8 611 38-kVa, non-PCB-containing, pole mounted R GE G567254-66Y Transformer Non-PCB <50 Unknown

AIR-8 611 37.5-kVa, non-PCB-containing, pole mounted I ME 90NA074-016 Transformer Non-PCB <1 NA



AIR-11 555 15-kVa, unknown capacity, pole mounted I Unknown Transformer Non-PCB <50 NA

AIR-11 555 15-kVa, 14-gallon, pole-mounted R NO28120YASA Transformer Non-PCB 0

AIR-13 292 10-kVa, pad mounted R C520337 Transformer PCB 160 1/9/1990



AIR-13 292 75-kVA, padmounted I 906005657 Transformer Non-PCB <2 NA

AIR-13 292 300-kVA, padmounted I 906005744 Transformer Non-PCB <2 NA

AIR-13 233 750-kVa, pad mounted/southeast of B233 R 906009620 Transformer Non-PCB <2 12/18/2002

AIR-18 231Pad mounted, installed 2006, presumed to be Non-

PCBI Unknown Transformer Non-PCB NA

EDC-15 41 75-kVa, non-PCB-containing, pad mounted I 906003910 Transformer Non-PCB <2 NA

EDC-15 41 50-kVa, PCB-containing R C579146 Transformer PCB 220 1990



EDC-15 64725-kVa, non-PCB-containing, pole mounted/SW of

B647I 901018283 Transformer Non-PCB <1 NA





EDC-27 55

No transformers associated with B55 in database.

Three transformers mounted on one pole are present

in the southwest corner of EDC-27. Presumed to be

Non-PCB.

I Unknown Transformer Non-PCB NA

EDC-34 629 25-kVa, pole mounted I 2454-17 Transformer Non-PCB 19 NA

EDC-34 629 25-kVa, pole mounted I 2454-19 Transformer Non-PCB <50 NA

EDC-34 629 25-kVa, pole mounted I 2454-4 Transformer Non-PCB 4 NA

EDC-34 631 25-kVa, pole mounted R 6962929 Transformer PCB 580 1991

EDC-34 633 pole mounted/southeast of B633 I 94113284 Transformer Non-PCB Mineral Oil NA


TABLE B-9

SUMMARY OF CURRENT AND REMOVED EQUIPMENT CONTAINING DIELECTRIC FLUID



PAGE 2 OF 2

Parcel ID Building Description/Location Status Serial Number Type Class

PCB

Concentration

(PPM)

Date

Removed Or

Disposed

EDC-34 633 50-kVa, pole mounted/southeast of B633 D 6954550 Transformer PCB 280 9/15/1995

EDC-34 63650-kVa, pole mounted located north of B661 and NE

of B659 and B636.I 941132918 Transformer Non-PCB Mineral Oil NA

EDC-34 636 38-kVa, pole mounted/across the street from B636 R E999218-63P Transformer PCB 130 1995

EDC-34 636 Pole mounted R 411 Transformer PCB 9/15/1995

EDC-34 None ID'ed RMCB-27 R 2643-3-2 Transformer PCB 1300 7/3/1991



EDC-45 102

None identified in database, but a pad-mounted

transformer is present in the northwest portion of the

parcel. Presumed to be non-PCB.

I Unknown Transformer Non-PCB Unknown NA

EDC-45Former

B13B-13 R 5/1/2643 Transformer PCB 77 6/1/1990

EDC-45Former

B13B-13 R 2643-5-7 Transformer PCB 79 6/1/1990

EDC-45Former

B13B-13 R 2643-5-8 Transformer PCB 77 6/1/1990

Notes:

(3) Symbols and Shading

Acronyms:

NA - Not Applicable

PCB - Polychlorinated BiphenylI - Installed/In Service

PPM - Parts per million

R - Removed

D - Disposed

(1) Information provided from NASB Environmental Department PCB Master Inventory (Removed Transformer Database) dated 2/02/2011, which primarily tracked transformers and other equipment (ballasts; switches)

removed between 1988 and 1995. Most PCB equipment, PCB transformers and PCB-contaminated transformers were removed from NAS Brunswick by October, 23 1995. The database indicates that other equipment,

primarily ballasts from unidentified locations were removed between 1996 and 1999. Transformers and other equipment removed and replaced prior to 1989 were not tracked in the database.

(2) The NASB Environmental Department PCB Master Inventory (the database) designates the Class "PCB" to mean both "PCB transformers" (PCB concentrations greater than 500 parts per million [ppm]) and “PCB-

contaminated transformers” (PCB concentrations greater than 50 ppm, but less than 500 ppm). The database uses the class "Non-PCB" to indicate equipment with PCB concentrations less than 50 ppm.

Shaded rows indicate known PCB or PCB-contaminated transformers that were removed.


TABLE B-10

MONITORING WELL LOCATIONS ON TRANSFER PARCELS



Transfer

Parcel

Well

Identification(1)

Shown on

FOST

Figure

Easting(2)

Northing(2) Location

B611-MW02 B-4 3015020.33 384370.14 Southeast of B611

B611-MW03 B-4 3015019.34 384335.35 Southeast of B611

AIR-10 FTA-MW08 B-5 3012125.52 384076.14 South end of Fire Training Area WestB611-MW01D B-4 3015060.51 384391.96 West of B555

B611-MW01S B-4 3015059.27 384392.01 West of B555

B611-MW04D B-4 3015075.88 384292.46 Southwest of B555

B611-MW04S B-4 3015078.21 384292.54 Southwest of B555

B611-MW05D B-4 3015174.88 384333.82 East of B555

B611-MW05S B-4 3015172.62 384333.52 East of B555

MW-301 B-8 3016074.92 385058.42 Southeast of Machine Gun Boresight Range

NASB-MGBR-MW01 B-8 3015688.71 385272.07 Machine Gun Boresight Range





B586-MW01 B-9 3017254.81 388758.79 North of Former B586

B586-MW02 B-9 3017406.12 388718.93 South of Former B586

B586-MW03 B-9 3017377.24 388654.29 South of Former B586

EDC-45 MW-NASB-210 B-11 3015812.56 388510.63 West of B102

Notes:

(1) Wells as identified in Tetra Tech's database. Presence and condition of wells has not been field verified.

(2) Coordinate System is North American Datum, 1983, State Plane Coordinate System, Maine West (Feet)

AIR-8

AIR-11

EDC-27

EDC-28


EXHIBIT C

CERCLA Hazardous Substance Notice

CERCLA HAZARDOUS SUBSTANCE NOTICE FOST 2013-5 TRANSFER PARCELS


W5213868F 1 Finding of Suitability to Transfer 2013-5

Parcel ID

Location Substance

Name

CAS Registry Number

40 CFR 302.4

Regulatory Synonyms

RCRA Waste

Number

Quantity Stored

Date of Storage

Quantity Released

Date of Release

Remedial Action Taken

AIR-13

B45, Hazardous

Waste Transfer Facility

Various hazardous

wastes - see attached lists

--- --- See

attached list

Unknown 1992 to 2011

Not Applicable

Not Applicable

None required.

EDC-27

Machine Gun

Boresight Range

Lead 7439921 --- ---

Not

Applicable

Not

Applicable Unknown 1950 to 1960s

Two hot spot soil removals conducted in May 2012 to reduce overall soil lead concentrations at site. Dimensions of soil removal areas were approximately 3'x'3'x6".

EDC-45

Former B13,

Hazardous Materials Storage

and Drum Crusher

Various products

containing hazardous substances

and unknown

drum contents

--- --- --- Unknown 1943 to 1998

Unknown Unknown

Non-residential use restriction will be applied due to PAHs in soil identified by 2011 soil sampling investigation.

EDC-46

B20, Navy

College Office

Asbestos 1336363

Not

Applicable

Not

Applicable

Not

Applicable

Not

Applicable Unknown Unknown

ACM released to soil in crawl space of building removed in October 2012.

CERCLA HAZARDOUS SUBSTANCE NOTICE FOST 2013-5 TRANSFER PARCELS


W5213868F 2 Finding of Suitability to Transfer 2013-5

NOTE: The table identifies those hazardous substances that it is known, based upon a complete search of agency files, were stored for one year or more in quantities greater than or equal to 1,000 kg (or greater than or equal to 1 kg if designated an acutely hazardous waste under 40 CFR Part 261.30) and/or were released or disposed of on the property to be transferred in quantities greater than or equal to their respective reportable quantities under 40 CFR 302.4. The information in this notice is required under the authority of regulations promulgated under Section 120(h) of the Comprehensive Environmental Response, Compensation and Liability Act ("CERCLA" or "Superfund"), 42 U.S.C. Section 9620(h).

2006 Hazardous Waste Database

Former Naval Air Station, Brunswick, Maine

WASTE STREAM NOMENCLATURE WASTE CODE

Acid Batteries Damaged BATTERY LEAD (DAMAGED) D002 D008

Acid Batteries Damaged Battery lead acid D002 D008

ACID, CHROMIC ACID SOLUTION (ALODINE) ALODINE D002 D007

ACID, MISC. (INORGANIC) ACID D002 D006

ACID, MISC. (INORGANIC) ACID D002 D006 D007

ACID, MISC. (INORGANIC) ALODINE D002 D006 D007

ACID, MISC. (INORGANIC) SOAP D002 D006 D007

ACID, SULFURIC <51% Sulfuric acid D002

ADHESIVE ADHESIVE D001 D007 D035

ADHESIVE ADHESIVES, NON-FLAMMABLE D007 D035

ADHESIVE SEALANT D001 D007 D035

ADHESIVE SEALANT D007 D035

ADHESIVE SEM PEN D001 D007 D035

ADHESIVES, MISC. FLAMMABLE ADHESIVE D001 D007 D035

ADHESIVES, MISC. FLAMMABLE SEALANT D001 D007 D035

ADHESIVES, MISC. FLAMMABLE SEMPEN D001 D007 D035

Aerosols D001 D006 D007 D035

Aerosols AEROSOL D001

Aerosols AEROSOL D001 D006 D007 D035

Aerosols AEROSOL D001 D006 D007 D35

Aerosols AEROSOL D001 D006 D007 DO35

Aerosols AEROSOL EMPTY D001 D006 D007 D035

AMYL ACETATE AMYL ACETATE D001

ANTIFREEZE ANTIFREEZE (REGULATED) D004 D008

ANTIFREEZE GLYCOL D004 D008

BARIUM BARIUM D005

BATTERIES, LEAD ACID (DAMAGED) BATTERY LEAD (DAMAGED) D002 D008

blast media BLAST MEDIA D006 D007

blast media BLAST MEDIA MAVERIC D006 D007

Blast Media drums BLAST BOOTH FILTER D006 D007

Blast Media drums BLAST MEDIA D006 D007

Blast Media drums DENTAL SUPPLIES D006 D007

BLASTING GRIT (REGULATED) BLAST MEDIA D006

BLASTING GRIT (REGULATED) BLAST MEDIA D006 D007

Broken Light Bulbs LAMPS, FLUORESCENT BROKEN D009

Caustic Solutions ANTIFREEZE NRCR D002

Caustic Solutions CAUSTIC CLEANER D002

Page 1



Caustic Solutions CAUSTIC SOLUTION D002

Caustic Solutions DEGREASER D002

Caustic Solutions SOAP D002

Caustic Solutions SODIUM HYDROXIDE D002

Caustic Solutions WAX FLOOR D002

Caustic Solutions WAX STRIPPER D002

CLEANING COMPOUND DEGREASER D002 D006 D008 D010

CLEANING COMPOUND, AIR CRAFT SURFACE JET WASHER SOLVENT (REGULATED) D004 D006 D007 D008 D010

CORROSIVE SOLIDS (SODIUM HYDROXIDE) DEGREASER D002

Corrosive Solids Sodium Hy SODIUM HYDROXIDE D002

CORROSIVE SOLIDS, OXIDIZER CORROSIVE SOLIDS D001

CORROSIVE SOLIDS, OXIDIZER CORROSIVE SOLIDS MA99

CORROSIVE SOLIDS, OXIDIZER POTASSIUM PERMANGANATE D001

EEBD EEBD D001 D003 D005

Engine Wash ENGINE WASH D004 D006 D007 D008 D010

ENGINE WASH JET WASHER SLUDGE D004 D006 D007 D008 D010

ENGINE WASH JET WASHER SOLVENT (REGULATED) D004 D006 D007 D008 D010

ENGINE WASH OXYGEN CLEANING COMPOUND D004 D006 D007 D008 D010

FILTERS PAINT BOOTH FILTERS D006 D007 D008 D009

FLAMABLE LIQUIDS METHANOL, CYLOHERANONE U154 U057

FLAMABLE LIQUIDS,CORROSIVE FLAMABLE LIQUIDS,CORROSIVE D001 D002

Flammable Liquids corrosive BOILER CHEMICALS D001 D002

Flammable Liquids corrosive FLAMABLE LIQUIDS,CORROSIVE D001 D002

FLOOR CLEANING COMPOUND DEGREASER D002 D006 D008 D010

Formaldehyde (Formalin) FORMALDAHIDE U122

FREON FREON F002

FUEL FUEL D001 D018

FUEL/DIESEL/DEBRIS FUEL FILTERS D001 D018

FUEL/DIESEL/DEBRIS GAS SOKED RAGS D001 D018

FUEL/DIESEL/DEBRIS JP RAGS D001 D018

HYDROGEN PEROXIDE SOLUTION HYDROGEN PEROXIDE SOLUTION D001 D002

Hypo Solution Corrosive WAX STRIPPER D002 D004 D006 D011

Hypo Solution Neutral BOILER CHEMICAL D009 D010 D011

Hypo Solution Neutral FIXER AND DEVELOPER D009 D010 D011

HYPO SOLUTION, ALKALINE FIXER AND DEVELOPER D002 D004 D006 D010 D011

HYPO SOLUTION, ALKALINE FIXER AND DEVELOPER D002 D004 D006 D011

HYPO SOLUTION, ALKALINE WAX STRIPPER D002 D004 D006 D011

HYPO SOLUTION, ALKALINE DOUBLE ENTRY FOR 1100 FIXER AND DEVELOPER D002 D004 D006 D011 D010

Page 2



HYPO SOLUTION, NEUTRAL FIXER AND DEVELOPER D009 D010 D011

HYPO SOLUTION, NEUTRAL (ADDED TO 1101) FIXER AND DEVELOPER D009 D010 D011

JP FUEL SPILL JP RAGS D001 D018

JP Rags JP RAGS D001 D006 D007 D035

LAMPS, FLUORESCENT BROKEN LAMPS, FLUORESCENT BROKEN D006 MRD009

LAMPS, FLUORESCENT BROKEN LAMPS, FLUORESCENT BROKEN NRCR

Lead AIR FILTERS D008

LEAD LEAD D008

LEAD PAINT CHIPS D008

Lead/Asbestos Debris LEAD D008

LIQUID WITH HEAVY METALS LIQUIDS NON-REG D008 D010

Liquids containing Silver and Mercury WATER WITH MERCURY AND SILVER D009 D011

MAERCURIC NITRITE MARCURIC NITRITE D001, D009

MAGNESIUM TURNINGS MAGNESIUM TURNINGS D001,D003

Misc acids ACID D002 D006 D007

Misc acids ALODINE D002 D006 D007

Misc acids CLEANER D002 D006 D007

Misc acids CONCRETE HARDNER D002 D006 D007

OBA Canisters EEBD D001 D003 D005

PAINT (CONSOLIDATION DRUM) AEROSOL D001 D006 D007 D008 D035

PAINT (CONSOLIDATION DRUM) PAINT CONSOLIDATION D001 D006 D007 D008 D035

PAINT (CONSOLIDATION DRUM) PAINT WASTE D001 D006 D007 D008 D035

PAINT (LOOSE PACK) PAINT AIRCRAFT D001 D006 D007 D008 D035

PAINT (LOOSE PACK) RTV D001 D006 D007 D008 D035

PAINT (LOOSE PACK) SEALANT D001 D006 D007 D008 D035

PAINT (LOOSE PACK) THINER D001 D006 D007 D008 D035

PAINT BOOTH FILTERS PAINT BOOTH FILTERS D006 D007 D008 D009

PAINT BOOTH FILTERS LAMPS, FLUORESCENT BROKEN D006 D007 D008 D009 D011

Paint Booth Filters PAINT BOOTH FILTERS D001 D006 D007 D035

PAINT BOOTH FILTERS PAINT BOOTH FILTERS D006 D007 D008 D009 D011

PAINT BOOTH FILTERS SOLIDS RCRA MAVERIC D006 D007 D008 D009 D011

PAINT CORROSIVE FLAMABLE LIQUIDS,CORROSIVE D001 D002

Paint Loose Pack D001 D006 D007 D008 D035

Paint Loose Pack ALCOHOL D001 D006 D007 D008 D035

Paint Loose Pack EPOXY LAB PACK D001 D006 D007 D008 D035

Paint Loose Pack PAINT D001 D006 D007 D008 D035

Paint Loose Pack PAINT AIRCRAFT D001 D006 D007 D008 D035

Paint Loose Pack PAINT STRIPPER D001 D006 D007 D008 D035

Page 3



Paint Loose Pack PLASTIC POLISH D001 D006 D007 D008 D035

Paint Loose Pack RTV D001 D006 D007 D008 D035

Paint Loose Pack SEALANT D001 D006 D007 D008 D035

Paint Loose Pack SEALANT KIT LAB PACK D001 D006 D007 D008 D035

Paint Loose Pack SEM PEN D001 D006 D007 D008 D035

Paint Loose Pack SOLVENT D001 D006 D007 D008 D035

Paint Loose Pack THINER D001 D006 D007 D008 D035

Paint Loose Pack THINER LAB PACK D001 D006 D007 D008 D035

Paint Rags D001 D006 D007 D035

PAINT RAGS JP RAGS D001 D006 D007 D035

Paint Rags PAINT BOOTH FILTERS D001 D006 D007 D035

PAINT RAGS PAINT RAGS D001 D006 D007 D035

PAINT RAGS PAINT RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS SEALANT D001 D006 D007 D035

Paint Rags SEALANT LAB PACK D001 D006 D007 D035

PAINT STRIPPER PAINT STRIPPER D002

PAINT STRIPPER PAINT STRIPPER D002, F002

PAINT/SOLVENT CONSOLIDATION DRUM METHANOL D001 D006 D007 D035 F002 F003 F005

PAINT/SOLVENT CONSOLIDATION DRUM PAINT CONSOLIDATION D001 D006 D007 D035 F002 F003 F005

PAINT/SOLVENT CONSOLIDATION DRUM THINER D001 D006 D007 D035 F002 F003 F005

Paint/Solvent Cosolidate THINNER D001 D006 D007 D035 F002 F003 F005

Parts Washer ENGINE WASH D004 D006 D007 D008 D010

Parts Washer JET WASHER SLUDGE D004 D006 D007 D008 D010

Parts Washer JET WASHER SOLVENT (REGULATED) D004 D006 D007 D008 D010

Parts Washer Parts Washer Fluid D004 D006 D007 D008 D010

PESTICIDES LIQUID, FLAMMABLE INSECTICIDE D001

PESTICIDES LIQUID, FLAMMABLE PESTICIDES LIQUID D001

Pesticides, Solid Toxic TURCAM U278

POTASSIUM CHLORATE CORROSIVE SOLIDS D001

POTASSIUM CHLORATE POTASSIUM CHLORATE D001

Potassium Chlorate POTASSIUM DICHROMATE D001

Potassium Chlorate SODIUM CHLORATE D001

POTASSIUM CYANIDE POTASSIUM CYNIDE D003

RCRA Antifreeze ANTIFREEZE (REGULATED) D004 D008

Rcra Antifreeze ANTIFREEZE NRCR D004 D008

Rcra Solids Drums AIR FILTERS D006 D007 D008 D009 D011

Rcra Solids Drums amalgam D006 D007 D008 D009 D011

Rcra Solids Drums Broken fluorescent lamp D006 D007 D008 D009 D011

Page 4



Rcra Solids Drums LAMPS, FLUORESCENT BROKEN D006 D007 D008 D009 D011

Rcra Solids Drums LEAD D006 D007 D008 D009

Rcra Solids Drums LEAD D006 D007 D008 D009 D011

Rcra Solids Drums LEAD CONTAMINATED DEBRIES D006 D007 D008 D009 D011

Rcra Solids Drums LEAD DEBRIS D006 D007 D008 D009 D011

Rcra Solids Drums PAINT BOOTH FILTERS D006 D007 D008 D009 D011

Rcra Solids Drums SOLDER D006 D007 D008 D009 D011

Rcra Solids Drums SOLIDS RCRA MAVERIC D006 D007 D008 D009 D011

Rcra Solids Drums Thermometer, broken D006 D007 D008 D009 D011

Rcra Solids Maveric LAMPS, FLUORESCENT BROKEN D006 D007 D008 D009

Rcra Solids Maveric LEAD D006 D007 D008 D009

Rcra Solids Maveric PAINT BOOTH FILTER D006 D007 D008 D009

Rcra Solids Maveric PAINT BOOTH FILTERS D006 D007 D008 D009

Rcra Solids Maveric PISTOL RANGE FILTERS D006 D007 D008 D009

Rcra Solids Maveric SOLIDS RCRA MAVERIC D006 D007 D008 D009

SEALANTS SEALANT D001 D007 D035

SELANT RAGS PAINT RAGS D001 D006 D007 D035

SELANT RAGS SEALANT LAB PACK D001 D006 D007 D035

SODIUM CHLORATE CORROSIVE SOLIDS D001

SODIUM CHLORATE POTASSIUM CHLORATE D001

SODIUM CHLORATE SODIUM CHLORATE D001

SODIUM HYDROXIDE ACID D002

SODIUM HYDROXIDE DEGREASER D002 D006 D008 D010

SODIUM HYDROXIDE PATASSIUM HYDROXIDE D002 D006 D008 D010

Sodium/Potassium hydroxide BOILER CHEMICALS D002 D006 D008 D010

SOLIDS, RCRA HAZARDOUS D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS BLAST BOOTH FILTER D006 D007 D008

SOLIDS, RCRA HAZARDOUS Boiler Ash D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS LAMPS, FLUORESCENT BROKEN D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS LEAD D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS LEAD SOLDER D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS PAINT BOOTH FILTERS D006 D007 D008 D009

SOLIDS, RCRA HAZARDOUS SOLIDS RCRA HAZARDOUS D006 D007 D008 D009

Sulfuric acid Sulfuric acid D002

TRICHLOROETHYLENE TRICHLOROETHYLENE D040

URINAL DEODORANT BLOCK URINAL DEODERANT BLOCK U072

WASH WATER FROM LAMELLA CHANGE OUT LEAD D008 D010

WASTE DIESEL/GASOLINE/KERO CONTAMINATED OIL D001 D018

Page 5



WASTE DIESEL/GASOLINE/KERO MO GAS D001 D018

WASTE DIESEL/GASOLINE/KERO NUMBER 2 FUEL D001 D018

WASTE DIESEL/GASOLINE/KERO WASTE GAS D001 D018

WATER CONTAMINATED WITH GASOLINE WATER CONTAMINATED WITH GASOLINE D018

BATTERIES, Ag AIR CRAFT BATTERIES MRD002 MRD006

BATTERIES, Ag BATTERIES, Ag MRD002 MRD006

BATTERIES, HG BATTERIES, HG MRD009

BATTERIES, Hg MERCURY BATTERIES MRD009

BATTERIES, Li MRD003

BATTERIES, Li BATTERY LITHIUM

BATTERIES, Li BATTERY LITHIUM MRD003

Batteries, Magnesium Batteries, Magnesium MRD005 MRD007

BATTERIES, NI CAD MRD006

BATTERIES, NI CAD BATTERY LITHIUM MRD006

BATTERIES, NI CAD BATTERY NI-CAD MRD006

BATTERIES, NI CAD BATTERY NI-MH MRD006

BATTERIES, NI CAD SEALED LEAD ACID MRD006

BATTERIES, ni-cad BATTERY NI-CAD MRD006

CATHODE RAY TUBES (CRTS) CATHODE RAY TUBES (CRTS) D008

CATHODE RAY TUBES (CRTS) CATHODE RAY TUBES (CRTS) D008UW

CATHODE RAY TUBES (CRTS) CATHODE RAY TUBES (CRTS) MRD008

LAMP, HIGH PRESSURE SODIUM LAMPS, HIGH PRESSURE SODIUM MRD008 MRD009

LAMP, HIGH PRESSURE SODIUM LAMPS, HIGH PRESSURE SODIUM MRD008, MRD009

LAMPS, FLUORESCENT (ODD SHAPES) LAMPS, FLUORESCENT ODD SHAPES D009

LAMPS, FLUORESCENT (ODD SHAPES) LAMPS, FLUORESCENT ODD SHAPES MRD009

LAMPS, FLUORESCENT (ODD SHAPES) LAMPS, FLUORESCENT ROUND MRD009

LAMPS, FLUORESCENT (ODD SHAPES) LAMPS, FLUORESCENT U TUBE MRD009

LAMPS, FLUORESCENT (STICK) LAMPS, FLUORESCENT STICK MRD009

LAMPS, FLUORESCENT (U TUBE) LAMPS, FLUORESCENT U TUBE MRD009

LAMPS, FLUORESCENT 1 FOOT LAMPs, FLUORESCENT 1 FOOT MRD009

LAMPS, FLUORESCENT 10 FOOT LAMPS, FLUORESCENT 10 FOOT MRD009

LAMPS, FLUORESCENT 18 INCH LAMPS, FLUORESCENT 1 FOOT MRD009

LAMPS, FLUORESCENT 18 INCH LAMPS, FLUORESCENT 18 INCH MRD009

LAMPS, FLUORESCENT 18 INCH LAMPS, FLUORESCENT 2 FOOT MRD009

LAMPS, FLUORESCENT 2 FOOT LAMPS, FLUORESCENT 18 INCH MRD009


LAMPS, FLUORESCENT 3 FOOT LAMPS, FLUORESCENT 18 INCH MRD009


Page 6





LAMPS, FLUORESCENT 4 FOOT LAMPS, FLUORESCENT 4 FOOT MD009


LAMPS, FLUORESCENT 4 FOOT LAMPS, HIGH PRESSURE SODIUM MRD009





LAMPS, FLUORESCENT ROUND LAMPS, FLUORESCENT ROUND MRD009

LAMPS, FLUORESCENT STICK LAMPS, FLUORESCENT STICK MRD009

LAMPS, FLUORESCENT STICK LAMPS, FLUORESCENT U TUBE MRD009

LAMPS, FLUORESCENT U TUBE LAMPS, FLUORESCENT ODD SHAPE MRD009

LAMPS, FLUORESCENT U TUBE LAMPS, FLUORESCENT U TUBE MRD009

LAMPS, SODIUM HIGH PRESSURE LAMPS, HIGH PRESSURE SODIUM MRD008 MRD009

LAMPS, SODIUM HIGH PRESSURE LAMPS, LOW PRESSURE SODIUM MRD008 MRD009

MERCURY THERMOMETERS THERMOMETERS MRD009

MERCURY THERMOSTATS/SWITCHE MERCURY THERMOSTATS/ SWITCHES MRD009

MERCURY THERMOSTATS/SWITCHE THERMOMETERS MRD009

PCB BALLAST BALLAST PCB None

PCB BALLAST PCB BALAST NRCR

PCB BALLASTS BALLAST PCB None

WASTE CATHODE RAY TUBES (CRTS) CATHODE RAY TUBES (CRTS) MRD008

Page 7


Former Naval AIr Station, Brunswick, Maine

NOMENCLATURE STANDARD NOMENCLATURE COMPOS1 WASTE CODE

1,1,1 TRICHLOETHANE SOLVENT HALOGENATED D001

1,1,1 TRICHLOETHANE SOLVENT HALOGENATED F001

1,1,1 TRICHLOETHANE SOLVENT HALOGENATED 1,1,1 TRICH F001

1,1,1 TRICHLOETHANE SOLVENT HALOGENATED 1,1,1 TRICHLORETHANE F001

1,1,1 TRICHLOETHANE SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, SPENT, DIRTY F002

1,1,1 TRICHLORETANE SOLVENT HALOGENATED D001

1,1,1 TRICHLORETHAN SOLVENT HALOGENATED D001

1,1,1 TRICHLORETHAN SOLVENT HALOGENATED 1,1,1 TRICHLORETHANE F001

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLORETHANE F002

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE F001

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, DIRTY, SPENT F001

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, SPENT F001

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, SPENT F002

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, SPENT, DIRTY F001

1,1,1 TRICHLOROETHA SOLVENT HALOGENATED 1,1,1 TRICHLOROETHANE, SPENT, DIRTY F002

1,1,1, TRICH SOLVENT HALOGENATED 1,1,1, TRICHLOROETHANE, SPENT F002

1,1,1,TRICHLOROETHA SOLVENT HALOGENATED 1,1,1, TRICHLOROETHANE, SPENT F001

A/C CLEANING CMPD SOAP D001

A/C CLEANING CMPD SOAP ORMA

A/C CLEANING CMPD SOAP A/C CLEANING COMPOUND D001

ACETIC ACID ACETIC ACID GLACIAL TECHNICAL D001 DOO2

ACETONE SOLVENT D001

ACETONE SOLVENT ACETONE, CONTAMINATED D001

ACETONE SOLVENT ACETONE, CONTAMINATED F003

ACETONE SOLVENT ACETONE,CONTAMANATED D001

ACETONE SOLVENT ACETONE,CONTAMANATED F003

ACETONE SOLVENT CONTAMINATED ACETONE D001

ACETONE, CONTAM. SOLVENT ACETONE, CONTAMINATED D001

ACETONE, CONTAM. SOLVENT ACETONE, CONTAMINATED D001 F003

ACETONE, CONTAM. SOLVENT ACETONE, CONTAMINATED W/ WATER & JP-5 F003

ACETONE, CONTAM. SOLVENT ACETONE, CONTAMINATED W/WATER & JP-5 D001 F003

ACETONE, CONTAMIN. SOLVENT ACETONE, CONTAMINATED D001 F003

ACETONE, CONTAMINAT SOLVENT ACETONE CONTAMINATED WITH WATER D001 F003

ACETONE, CONTAMINAT SOLVENT ACETONE, WATER (1%), JP5 (3%) D001 F003

ACETONE,CONTAM SOLVENT ACETONE, JP-5, WATER D001 F003

ACID ACID D002

ACID ACID ACETIC ACID FROM MEDICAL D001 D002

ACID ACID ACETIC ACID PHOTO GRADE D001 D002

ACID ACID ACETIC ACID,GLACIAL D001 D002

ACID ACID ACID D002

ACID ACID ALODINE D002 D007

ACID ACID ALODINE & WATER D007

ACID ACID ALODINE AND WATER D007

ACID ACID ALODINE PH=4 D002 D007

ACID ACID ALODINE WASTE D002 D007

ACID ACID ALODINE WASTE D007

ACID ACID ALODINE WASTE AND WATER D007

ACID ACID ALUMINIZED COMPOUND D002

Page 1



ACID ACID ARCHER ETCHANT D002

ACID ACID BATTERY ACID PH2 D002

ACID ACID CHROMIC ACID D002 D007

ACID ACID CONCENTRATED FLOOR CLEANER D002

ACID ACID CORROSIVE LIQUID D002

ACID ACID CUPROUS CHLORIDE D002

ACID ACID FERRIC CHLORIDE SOLUTION D002

ACID ACID FERRIC CHLORIDE SOLUTION D002

ACID ACID HAZMAT D002

ACID ACID HYDROCHLORIC ACID D002

ACID ACID HYDROCHLORIC ACID LEFT BEHIND BY CONTRACTORS D002

ACID ACID INHIBITOR 46 D002

ACID ACID LDC 01 ELECTROCLEAN D002

ACID ACID LEMON TUB TILE CLEANER D002

ACID ACID MURATIC ACID D002

ACID ACID MURIATIC ACID D002

ACID ACID MURIATIC ACID D002

ACID ACID NITRIC ACID D002

ACID ACID NITRIC ACID D002

ACID ACID PC BOARD ETCHING SOLUTION D002

ACID ACID POTASSIUM HYDROXIDE D002

ACID ACID SCM 4200 ACTIVATOR SOLUTION D002

ACID ACID SCM4100 SELECTRON SOLUTION D002

ACID ACID SOLDERING FLUX D002

ACID ACID SULFURIC ACID D002

ACID ACID SULFURIC ACID FROM TREATMENT PLANT D002

ACID ACID WASTE ACID D002

ACID ACID WASTE ALODINE D007

ACID ACID WASTE FERRIC CHLORIDE/DRILLING WASTE D002 MA99

ACID ACID WASTE NITRIC ACID FROM DECON D002

ACID ACETIC ACID ACETIC ACID GLACIAL D001 D002

ACID BATTERY ACID BATTERY ACID D002

ACID SULFURIC ACID SULFURIC ACID D002

ADESILEX B (MAPEI) ADHESIVE ADHESIVE D001

ADHESIVE D001

ADHESIVE D007 D035

ADHESIVE D007 D035

ADHESIVE 1030 ADHESIVE TOLUENE D001

ADHESIVE 2 PART KIT D001

ADHESIVE 2TQ SEALER D001

ADHESIVE AC-102 ACCELERATOR D001

ADHESIVE ACCUMULATION D001

ADHESIVE ACCUMULATION BARREL OF ADHESIVE D007 D035

ADHESIVE ACCUMULATION CONTAINER D001 D007 D035

ADHESIVE ACTIVATOR PART B D001 D035

ADHESIVE ADHESIVE D001

ADHESIVE ADHESIVE D001 D005 D007 D035

ADHESIVE ADHESIVE D001 D007


Page 2







ADHESIVE ADHESIVE D001 D035 F003

ADHESIVE ADHESIVE D001 D035 F003 F005

ADHESIVE ADHESIVE D001 F002

ADHESIVE ADHESIVE D001 F002 F003


ADHESIVE ADHESIVE D001 F003 F005








ADHESIVE ADHESIVE D011 D018 F005


ADHESIVE ADHESIVE F002

ADHESIVE ADHESIVE F003

ADHESIVE ADHESIVE FOO5


ADHESIVE ADHESIVE - OVER-AGE HAZMAT * RETURNED TO COMPANY F005 F027

ADHESIVE ADHESIVE - SEALANT, OVER-AGED U244

ADHESIVE ADHESIVE - SILVER, CHROMIUM D007 D011

ADHESIVE ADHESIVE VP8-68 VPU1-6 VP92-15 VP8-10 VP92-20 D007 D035

ADHESIVE ADHESIVE AEROSOL D001

ADHESIVE ADHESIVE ASPHALT D001

ADHESIVE ADHESIVE- FLAMMABLE LIQUID D001

ADHESIVE ADHESIVE KIT D002

ADHESIVE ADHESIVE MIL-S-8802 D001 D007 D008

ADHESIVE ADHESIVE PART A, MEK, CARBON TET. D001 D019 D035

ADHESIVE ADHESIVE PART B, MEK, LEAD MONOXIDE, TOLUENE D001 D008 D035

ADHESIVE ADHESIVE PRIMER D001

ADHESIVE ADHESIVE PROMOTER D001 D035

ADHESIVE ADHESIVE RESIN D001

ADHESIVE ADHESIVE SEALANT D001

ADHESIVE ADHESIVE SEALANT D001 D018

ADHESIVE ADHESIVE SEALANT, MEK D001 D035

ADHESIVE ADHESIVE SEALENT FOO5

ADHESIVE ADHESIVE VP26-22 VQ11-20 AIMD-2 VP10-14 VP92-13 D007 D035

ADHESIVE ADHESIVE WASTE MEK D001 D035

ADHESIVE ADHESIVE, FLAMMABLE LIQUID D001

ADHESIVE ADHESIVE, OVER-AGED D001

ADHESIVE ADHESIVE, SEALING COMPOUND D001

ADHESIVE ADHESIVE, SPENT D001

ADHESIVE ADHESIVE, SPENT D001 F003 F005

ADHESIVE ADHESIVE, SPENT D001 F005

Page 3



ADHESIVE ADHESIVE, SPENT D006

ADHESIVE ADHESIVE, SPENT U041

ADHESIVE ADHESIVE, XYLENE D001

ADHESIVE ADHESIVE,SPENT D001

ADHESIVE ADHESIVES D006

ADHESIVE ADHESIVES D007 D035

ADHESIVE ADHESIVE-SEALANT D001

ADHESIVE ADHESSIVE D001

ADHESIVE ASBESTOS D001

ADHESIVE ASPHALT ROOF CEMENT D001

ADHESIVE ASSORTED ADHESIVES D001 D035



ADHESIVE BASE COMPOUND D001 D007

ADHESIVE BOSCODUR #9 D001 D008 D035

ADHESIVE BOSTICK 1096 D001 D019 D035

ADHESIVE BOSTIK 1007 PRIMER D001 D035

ADHESIVE BOSTIK ADHESIVE 1095 PART A D001 D019 D035

ADHESIVE BOSTIK ADHESIVE 1095 PART B D001 D008 D035

ADHESIVE BRQQC BQYLB BNRSV CCCBY CBTFS CJFBB D007 D035

ADHESIVE BZFXX D007 D035

ADHESIVE CARBON TETRACHLORIDE, MEK, TOLUENE, D001 D019 D035

ADHESIVE CARBON TETRACHLORIDE, MEK, TOLUENE, XYLENE, ETHYL D001 D019 D035

ADHESIVE CBTFS CFJTD BRQQC BQYLB CCCBY D007 D035

ADHESIVE CCCBY BAQQC BQYLB CBTFS/T CFJTD/C DOO7 D035

ADHESIVE CCCBY BRQQC CFJTD CBTFS BQYLC CBKBP 44201 D007 D035

ADHESIVE CERAMIC ADHESIVE D001 D035

ADHESIVE CERAMIC TILE MASTIC D001

ADHESIVE CLIFTON ADHESIVE D001 D035

ADHESIVE CONDUCTIVE COATING D001

ADHESIVE CONSOLIDATION DRUM D007 D035

ADHESIVE COURTALDS ADHESIVE D007 D035

ADHESIVE CS3204 D001

ADHESIVE CURING AGENT D001 D008 D035

ADHESIVE DAPACAST D008

ADHESIVE DAPCO 18-4 D008

ADHESIVE DAPCO FIREWALL SEALANT D008

ADHESIVE EPI SEAL D005

ADHESIVE EPI SEAL PART B D005

ADHESIVE EPI SEAL PLUS D001

ADHESIVE EPI SEASL D005

ADHESIVE EPOXY D001

ADHESIVE EPOXY CEMENT D005

ADHESIVE EPOXY REPAIR KIT D001

ADHESIVE EPOXY RESIN, ADHESIVE D001

ADHESIVE ETHANOL, TRICHLOROETHANE D001 F002

ADHESIVE EXCESS SEALANT ACCELRATOR D007

ADHESIVE EXCESS SEALANTS D001 D007 D035

ADHESIVE EXPIRED ADHESIVES D001 D035

Page 4



ADHESIVE EXPIRED ADHESIVES D001 D007 D035

ADHESIVE EXPIRED DUE TO POOR MANAGEMENT D007 D035

ADHESIVE FA 1030 NEUTRAL D001

ADHESIVE FIREWALL SEALING COMPOUND D001 D035

ADHESIVE GF8 ASPHALT CUTBACK D001

ADHESIVE HAZMAT D007

ADHESIVE HEAT TRANSFER CEMENT D001

ADHESIVE HENRY 232 D001

ADHESIVE HI-VIS CLEAR SEALER D001

ADHESIVE LAMINAR X 500 D001 D018

ADHESIVE LEAK LOSKPIPE JOINT COMPOUND D001

ADHESIVE LIQUID NAILS D001

ADHESIVE LX-500 HARDNER D005

ADHESIVE MEK D001 D035

ADHESIVE MEK, CYCLOHEXANONE, RESINS, TETRAHYDROFURAN D001 D035 F005

ADHESIVE MEK, TOLUENE, XYLENE D001 D035

ADHESIVE MIKED SEALANTS D007 D035

ADHESIVE MIL-81733 D007

ADHESIVE MIL-8802F D035

ADHESIVE MIL-L-81733C D007

ADHESIVE MIL-L-8802 D001 D035

ADHESIVE MIL-L-8802F D007

ADHESIVE MILL-S-8802 D001 D035

ADHESIVE MIL-S-38249 D001 D035

ADHESIVE MIL-S-81733 38249 8802 D001 D007 D035

ADHESIVE MIL-S-81733C DO35

ADHESIVE MIL-S-8802 D001 D007 D035

ADHESIVE MISC ADHESIVES/SEALANTS/VARNISH D001 D018 D035

ADHESIVE NAPTHA, TOLUENE D001

ADHESIVE NEOPRENE PHENOLIC RESIN D001

ADHESIVE NEOPRENE RUBBER ADHESIVE D001

ADHESIVE NEOPRENE SOLVENT PART A D001

ADHESIVE NEOPRENE SOLVENT PART B D001

ADHESIVE PATCH KIT FUEL D007 D035

ADHESIVE PATCH KIT PART B D001 D035

ADHESIVE PERMATEX SEALANT 1372 D001

ADHESIVE PETROLEUM SOLVENTS D001

ADHESIVE PLASTIC PIPE ADHESIVE D001

ADHESIVE PLASTIC PIPE ADHESIVE D001 D035 D043

ADHESIVE POLY SILOXANE PART A D008

ADHESIVE POLYCHLOROPRENE ADHESIVE D001

ADHESIVE POLYURETHANE ACCELERATOR D001 D035

ADHESIVE PR 1426 ADHESIVE PROMOTOR D001

ADHESIVE PR 1440 PART A D001 D035

ADHESIVE PR-1422 A-2 PART A D007

ADHESIVE PR-1422 PART B D001 D035

ADHESIVE PR-1440 PART A D001

ADHESIVE PR-1440 PART B D001 D035

ADHESIVE PR-1440 PT B D001 D035

Page 5



ADHESIVE PR1463 D001 D007

ADHESIVE PRIMER ADHESIVE D001 D019 D035

ADHESIVE PRIMER ADHESIVE D001 D035

ADHESIVE PRIMER SEALING COMPOUND U226

ADHESIVE PRIMER WASH PRETREATMENT D001 D007

ADHESIVE PRO SEAL D001 D007

ADHESIVE PRO SEAL D001 D007 D035

ADHESIVE PRO SEAL D007

ADHESIVE PRO SEAL D007 D035

ADHESIVE PRO SEAL D035

ADHESIVE PRO SEAL 81733C D007

ADHESIVE PRO SEAL 870 PART B D035

ADHESIVE PRO SEAL 8802F D035

ADHESIVE PRO SEAL MIL S 8802F D035

ADHESIVE PRO SEAL PART A D007

ADHESIVE PRO SEAL PART B D001

ADHESIVE PROSEAL D001 D007

ADHESIVE PROSEAL D001 D035

ADHESIVE PROSEAL D007

ADHESIVE PROSEAL D035

ADHESIVE PROSEAL 870 B1/2 D035

ADHESIVE PROSEAL BASE D001 D035

ADHESIVE PROSEAL SEAL D035

ADHESIVE PVC CEMENT D001 D035

ADHESIVE PVC SOLVENT CEMENT D035

ADHESIVE RAIN EROSION KIT D001 D005 D035

ADHESIVE RUBBER ADHESIVE D001 D007 d035

ADHESIVE RUBBER BASE ADHESIVE D001

ADHESIVE S-90 ADHESIVE D001

ADHESIVE SAEALING COMPOUND D035

ADHESIVE SCOTCH GRIP ADHESIVE D001

ADHESIVE SCOTCHBRAND SEALER D001

ADHESIVE SCOTCHGUARD 1099 D001




ADHESIVE SEALANT- ADHESIVE D001

ADHESIVE SEALANT MIL-S-733C D007 D035

ADHESIVE SEALANT MIL-S-8802 D001 D007

ADHESIVE SEALANT MIL-S-8802F D001 D007 D035

ADHESIVE SEALANTS D001 D007 D008 D035

ADHESIVE SEALANTS D007 D008 D035

ADHESIVE SEALIND COMPOUND D007

ADHESIVE SEALING COMPOUIND MIL-S-8802F D035

ADHESIVE SEALING COMPOUND D001

ADHESIVE SEALING COMPOUND D001 D007

ADHESIVE SEALING COMPOUND D001 D007 D008



Page 6








ADHESIVE SEALING COMPOUND D007 DO35




ADHESIVE SEALING COMPOUND (PART A) D001

ADHESIVE SEALING COMPOUND (PART B) D008

ADHESIVE SEALING COMPOUND 8802F D001 DO35

ADHESIVE SEALING COMPOUND ACETONE D001

ADHESIVE SEALING COMPOUND CARTRIDGE D001 D007 D035

ADHESIVE SEALING COMPOUND MIL 81733C D007

ADHESIVE SEALING COMPOUND MIL S 81733C D007

ADHESIVE SEALING COMPOUND MIL-S-45180 D001


ADHESIVE SEALING COMPOUND MIL-S-7124B D008

ADHESIVE SEALING COMPOUND MIL-S-81733C D007 D035


ADHESIVE SEALING COMPOUND MIL-S-8802 PART A D007

ADHESIVE SEALING COMPOUND MIL-S-8802 PART B D001 D035

ADHESIVE SEALING COMPOUND PART A D001

ADHESIVE SEALING COMPOUND PART A D001 D007


ADHESIVE SEALING COMPOUND PART A D007 D035


ADHESIVE SEALING COMPOUND PART B D001

ADHESIVE SEALING COMPOUND PART B D001 D007

ADHESIVE SEALING COMPOUND PART B D001 D035



ADHESIVE SEALING COMPOUND PART B DOO7

ADHESIVE SEALING COMPOUNDS D001 D007 D008

ADHESIVE SEALING COMPOUNDS D007 D035

ADHESIVE SEE ATTACHED D007 D035

ADHESIVE SEE DUMP LOGS D007 D035

ADHESIVE SEE WASTE LOGS D007 D035

ADHESIVE SILICONE ADHESIVE D001

ADHESIVE SILICONE ADHESIVE D001 D018

ADHESIVE SILVER, COPPER D011

ADHESIVE SOLVENT BORNE ACCELERATOR PART B D001

ADHESIVE SOLVENT BORNE ADHESIVE PART A D001

ADHESIVE SPLICING ADHESIVE D001

ADHESIVE SSEALING COMPOUND MIL S 8802F D001 D035

ADHESIVE TAMPER PROOF SEALANT D035

ADHESIVE TOLUENE 40-45%, HEXANE 30-36% D001 F005

ADHESIVE TOLUENE, ACETONE, TEXTILE SPIRIT D001 F003 F005

Page 7



ADHESIVE TOLUENE, ALIPHATIC PETROLEUM NAPTHA D001 F003 F005

ADHESIVE TOLUENE, HEXANE, MAPTHA, MEK D001 D019 D035 F005

ADHESIVE TOLUENE, HEXANE, MEK D001 D035 F005

ADHESIVE TOLUENE, METHANOL, POLYCHLOROPRENE ELASTOMER F003 F005

ADHESIVE TOPCOAT ADHESIVE D001

ADHESIVE TOPCOAT ADHESIVE D001 D035

ADHESIVE TRICHLOROEHTYLENE D001

ADHESIVE USED SEALANT D001

ADHESIVE USED SEALANTS FROM SCA D007 D035

ADHESIVE VARIOUS ADHESIVES D001

ADHESIVE WASTE BOSCODUR 9 D001 D008 D035

ADHESIVE WASTE SEALANT D005 D007 D035

ADHESIVE WELD-ON 28 PART A&C D001

ADHESIVE WELD-ON 28 PART B D001 D003

ADHESIVE WELDWOOD CEMENT, BONDING AGENT D001 D035

ADHESIVE ADHESIVE ADHESIVE D001

ADHESIVE ADHESIVE ADHESIVES AND SEALANTS D001 D005 D035

ADHESIVE ADHESIVE MIL A 5540B CLASS 3 D001

ADHESIVE ADHESIVE SEALING COMPOUND D001

ADHESIVE ADHESIVE SEALING COMPOUND D001 D035

ADHESIVE ADHESIVE SEALING COMPOUND 81733 D007

ADHESIVE - A ADHESIVE - PART A D001

ADHESIVE - B ADHESIVE - PART B D001

ADHESIVE - B OILS, CONTAMINATED W/ SOLVENTS D001

ADHESIVE - PART A ADHESIVE - PART A , SPENT F005

ADHESIVE - PART A ADHESIVE - PART A , SPENT U055

ADHESIVE - PART A ADHESIVE - PART A RCRA F005

ADHESIVE - PART A ADHEWSIVE - PART A , SPENT D001

ADHESIVE - PART B ADHESIVE - PART B , SPENT D008

ADHESIVE - PART B ADHESIVE - PART B, SPENT U201

ADHESIVE - PART B ADHESIVE- PART B , SPENT D008

ADHESIVE ACCELERATO ETHANOL, POLYMERIC ALIPHATIC AMINE D001

ADHESIVE CEMENT ADHESIVE CEMENT D001

ADHESIVE CONTACT SOLVENTS D001

ADHESIVE FLOOR NAPTHA 3.4%, METHANOL 1.7% F003

ADHESIVE MMM-A-121 SOLVENTS D001

ADHESIVE PART A D001 D005

ADHESIVE PART A ADHESIVE- PART A D001

ADHESIVE PART A TOLUENE, HEXANE D001

ADHESIVE PART A TOLUENE, HEXANE D001 F003 F005

ADHESIVE PART B ADHESIVE PART B D001

ADHESIVE PART B ETHYL ALCOHOL, POLYMERIC ALIPHATIC AMINE D001 F003 F005

ADHESIVE PART B METHANOL, ALIPHATIC AMINE D001

ADHESIVE PART B TOLUENE D001

ADHESIVE POLY ADHESIVE D001

ADHESIVE POLY ADHESIVE POLYCHLOROPRENE D001

ADHESIVE POLY ADHESIVE POLYCHLOROPRENE FLAMABLE D001

ADHESIVE POLY RESIN ADHESIVE POLY RESIN D001

ADHESIVE PVC MEK, VINYL CHLORIDE, CYCLOHEXANONE D001 D035 D043

Page 8



ADHESIVE SPRAY D001

ADHESIVE WASTES ACETONE, HEXANE, RESIN, DECANE, ALUMINUM OXIDE D001

ADHESIVE, ADHESIVE, RESIN POLYESTER D001

ADHESIVE, ASPHALT ASBESTOS, PETROLEUM DISTILLATES D001

ADHESIVE, CLEAR NAPTHA D001

ADHESIVE, DENTAL TOLUENE, ACETONE, METHYL ETHYL KETONE D001 D035

ADHESIVE, E-1293 MEK, TOLUENE, ACETONE D035

ADHESIVE, EXCESS ADHESIVE, EXCESS D001 D035 F005

ADHESIVE, EXCESS ADHESIVE, EXCESS D007

ADHESIVE, HENRY-232 PETROLEUM DISTILLATE D001

ADHESIVE, MMM-A-110 ASBESTOS, PETROLEUM DISTILLATE D001

ADHESIVE, PRIMER D001

ADHESIVE, PRIMER D001 F002

ADHESIVE, PVC TETRAHYDROFURIN, PROPYLENE OXIDE D001

ADHESIVE, SB-709 PETROLEUM DISTILLATE D001

ADHESIVE, SEALANT ADHESIVE, SEALANT D001

ADHESIVE, WELDWOOD MEK, TOLUENE, HEXANE D001

ADHESIVE,SEALING CD ADHESIVE, SEALING COMPOUND D001

ADHESIVES ADHESIVES, DIRTY D001

ADHESIVE-VOID ADHESIVE D001

AEROSOL AEROSOL 1 1 1 TRICH U226

AEROSOL AEROSOL AEROSOL D001

AEROSOL AEROSOL AEROSOL PAINT CANS D001 D007 D008

AEROSOL AEROSOL AEROSOL STARTING FLUID D001

AEROSOL AEROSOL AEROSOLS D001 D007 D008

AEROSOL AEROSOL AREOSOL SPRAY CANS D001

AEROSOL AEROSOL ASSORTED SPRAY CANS D001

AEROSOL AEROSOL COND-X D001

AEROSOL AEROSOL CORROSION PREVENTIVE COMPOUND D001 D005

AEROSOL AEROSOL DUSTER REFILL GAS U075

AEROSOL AEROSOL EXPIRED INSECTICIDE U226

AEROSOL AEROSOL EXPIRED PAINT D001

AEROSOL AEROSOL EXPIRED PAINT D001 D008 D035

AEROSOL AEROSOL FREEZING COMPOUND U075

AEROSOL AEROSOL LHB INDUSTRIES SPRAY PAINT D001

AEROSOL AEROSOL LUBRICANT D001 D008 D035

AEROSOL AEROSOL LUBRICANT AEROSOL D005 D008

AEROSOL AEROSOL MISC AERSOLS FLAMMABLE D001

AEROSOL AEROSOL OVEN CLEANER D002

AEROSOL AEROSOL PAINT AEROSOLS D001

AEROSOL AEROSOL PEPPER SPRAY D001

AEROSOL AEROSOL WASTE AEROSOL D001

AEROSOL AEROSOL WHITE ENAMEL PAINT D001

AEROSOL AEROSOL ZYGLO PENETRANT D001

AEROSOL START FLUID AEROSOL STARTING FLUID D001

AEROSOL, SOLVENTS AEROSOL AEROSOL, SOLVENTS D001

AFFF AFFF/JP8 AT FUEL FARM MA01

AL ROOF COATING ASBESTOS, ALUMINUM, ASPHAULT, MINERAL SPIRITS D001

ALCOHOL ALCOHOL D001

Page 9



ALCOHOL DEICING FLUID D001

ALCOHOL DENATURED ALCOHOL D001

ALCOHOL DETECTOR TICKETS, METHYL ALCOHOL, LIGROINE D001

ALCOHOL ETHYL ALCOHOL D001

ALCOHOL ISOPROPANOL D001

ALCOHOL ISOPROPYL ALCOHOL D001

ALCOHOL ISOPROPYL ALCOHOLS D001

ALCOHOL METHANOL D001 U154

ALCOHOL METHANOL TECHNICAL D001 U154

ALCOHOL WASTE ALCOHOL D001

ALCOHOL, DENATURED ALCOHOL, DENATURED D001 F003

ALCOHOL, DENATURED ALCOHOL, DENATURED, DIRTY D001

ALCOHOL, DENATURED METHANOL, ETHANOL D001

ALKALINE CO & O2 ABSORBER D002

ALKALINE TY-ION-20 7520 D002

ALKYD SATIN ENAMEL MINERAL SPRITS, LIGHT PETROLEUM, TITANIUM DIOXIDE D001

ALODINE D002

ALODINE ALODINE D002

ALODINE ALODINE D002 D006 D007

ALODINE ALODINE D002 D007

ALODINE ALODINE D007

ALODINE ALODINE + WATER D002

ALODINE ALODINE AND WATER D007

ALODINE ALODINE PH2 D002

ALODINE ALODINE POWDER D007

ALODINE ALODINE WASTE PH 4 DOO7

ALODINE CHROMIC ACID D001 D002 D007

ALODINE CHROMIC ACID D002 D007

ALODINE CHROMIC ACID DRY MIXTURE D001 D007

ALODINE EXPIRED ALODINE PENS D002

ALODINE OVERAGE ALODINE D002 D007

ALODINE USED ALODINE D002 D007

ALODINE USED ALODINE D007

ALODINE WASTE ALODINE D007

ALODINE WASTE ALODINE PH4 D007

ALODINE (CHROMIC A) CHROMIC ACID (1%) D002 D007

ALODINE 1202 ALODINE 1202 D002

ALODINE AND WATER CHROMIC ACID D002 D007

ALODINE WASTE ALODINE D001 D007

ALODINE WASTE CHROMIC ACID D002 D007

ALODINE, SPENT ALODINE, SPENT D002

ALODINE, SPENT ALODINE, SPENT, DIRTY D002

AMALGAM, DENTAL SILVER, MERCURY D009 D011

AMLGARD 1,1,2 TRICHLORO-1,2,2 TRIFLUOROETHANE, BARIUM D005

AMM0NIUM HYDROXIDE AMMONIA HYDROXIDE D002

AMMONIUM HYDROXIDE AMMONIUM HYDROXIDE D002

AMMONIUM HYDROXIDE AMMONIUM HYDROXIDE D002

AMMONIUM HYDROXIDE AMMONIUM HYDROXIDE SOLUTION D002


Page 10




ANTI SEIZE COMPOUND ANTI SEIZE COMPOUND D001

ANTIFREEZE ANTIFREEZE ANALYSIS D006

ANTIFREEZE ANTIFREEZE ANALYSIS AE02498 D004 D008

ANTIFREEZE ANTIFREEZE ARRESTING GEAR D010

ANTIFREEZE ANTIFREEZE AWAITING ANALYSIS D004 D008

ANTIFREEZE ANTIFREEZE BDGNL BJYSL D004 D008

ANTIFREEZE ANTIFREEZE FROM DIV 900 D008

ANTIFREEZE ANTIFREEZE FROM RANGELY DOO8

ANTIFREEZE ANTIFREEZE HOBBY SHOP D004 D008

ANTIFREEZE ANTIFREEZE MWR HOBBY SHOP D004 D008

ANTI-FREEZE ANTI-FREEZE D001

ANTIFREEZE EXTENDER ANTIFREEZE EXTENDER FROM HOBBY SHOP D002

ANTISTATIC FLUID ANTISTATIC FLUID D001

ANTI-STATIC SPRAY ANTI-STATIC SPRAY - AEROSOL CANS D001 D007 D035

ARMOR KOTRLINE FINI ISOBUTYL ALCOHOL, ISOBUTYL ACETATE, CELLUSOLVE ACE D001 F005

ARSENIC STANDARD ARSENIC STANDARD D002 D004

ASBESTOS ASBESTOS ASBESTOS FROM BUILDING DEMOLITION CONTRACT

ASBESTOS DEBRIS ASBESTOS ASBESTOS DEBRIS ORMC

ASBESTOS DROSS ASBESTOS ASBESTOS DROSS ORMC

ASBESTOS DROSS ASBESTOS ASBESTOS DROSS ORME

ASH BOILER ASH D006

ASH SOOT AND ASH FROM BOILER CLEANING D010

ASH SOOT FROM BOILER CLEANING D010

ASHESIVE USED SEALANTS D007 D035

ASPHALT ADHESIVE ASPHALT ADHESIVE, CONTAMINATED W/ DIRT D001

B & B WASH B&B WASH B & B WASH D006

B & B WASH B&B WASH B B WASH D006

B&B Wash B&B WASH AIMD W/C 414 D006

B&B Wash B&B WASH ANALYSIS D006

B&B WASH B&B WASH B&B ENGINE WASH D006

B&B WASH B&B WASH B&B WASH D006

B&B Wash B&B WASH ENGINE WASH D006

B&B Wash B&B WASH ENGINE WASH D006

B&B WASH B&B WASH ENGINE WASH D006

B&B WASH B&B WASH ENGINE WASH ACCUMULATION D006

B&B WASH B&B WASH ENGINE WASH AFFLUENT D006

B&B WASH B&B WASH ENGINE WASH RESIDUE D006

B&B WASH B&B WASH FLIGHT LINE D006

B&B Wash B&B WASH SEE ANALYSIS DOO6

B&B Wash B&B WASH SQUADRONS D006

B&B Wash B&B WASH SQUADRONS D006

B&B Wash B&B WASH WC 414 D006

BALLAST PCB CONTAMINATED BALLAST M002

BALLASTS, PCB CONTA BALLASTS, CONTAMINATEED W/ PCBS M002

BARIUM CHLORIDE BARIUM CHLORIDE D005

BARIUM STANDARD BARIUM STANDARD D002 D005

BASE, CORROSIVE BASE, CORROSIVE SOLID D002

BATTERY BATERY ALKALINE ALKALINE BATTERY, MERCURY, LEAD, CADMIUM, KOH D006 D008 D009

Page 11



BATTERY BATERY ALKALINE STORAGE BATTERY, KOH D002

BATTERY BATERY NI-CAD BATTERY, NI-CAD D002 D006

BATTERY ACID ACID D002

BATTERY ACID ACID BATTERY ACID ELECTROLYTE, SPENT D002

BATTERY ACID ACID LEAD, SULFURIC ACID D002 D008

BATTERY ACID ACID USED BATTERY ACID D002

BATTERY ACID ELECTR ACID BATTERY ACID ELECTROLYTE D002

BATTERY DRY BATTERY ALKALINE POTASSIUM HYDROXIDE, MANGANESE DIOXIDE, ZINC, D002 D009

BATTERY FLUID, ACID ACID PH 0.356 D002

BATTERY FLUID, ACID ACID SULFERIC ACID 37%; LEAD <4.12 PPM; PH 0.356 D002

BATTERY GEL ACID BATTERY SULFURIC ACID/IN GEL D009

BATTERY LEAD BATTERY LEAD AIRCRAFT BATTERY LEAD SULFURIC ACID D002 D008

BATTERY LEAD BATTERY LEAD BATTERY D002 D008

BATTERY LEAD BATTERY LEAD BATTERY DEBRIS D008

BATTERY LEAD BATTERY LEAD BATTERY DRAINED D008

BATTERY LEAD BATTERY LEAD BATTERY LEAD D008

BATTERY LEAD BATTERY LEAD BATTERY RECHARGEABLE D002 D008

BATTERY LEAD BATTERY LEAD EXPLODED BATTERY D008

BATTERY LEAD BATTERY LEAD GEL CELL BATTERY D002 D008

BATTERY LEAD BATTERY LEAD GEL TYPE ACID BATTERIES D008

BATTERY LEAD BATTERY LEAD LEAD ACID BATTERIES D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID BATTERY D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID BATTERY LEAD & SULFURIC ACID D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID BATTERY, LEAD, SULFURIC ACID D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID BATTERYS D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID GEL BATTERY D002 D008

BATTERY LEAD BATTERY LEAD LEAD ACID GEL BATTERY D006

BATTERY LEAD BATTERY LEAD LEAD, ARSENIC, SULPHURIC ACID, ANTIMONY D002 D004 D008

BATTERY LEAD BATTERY LEAD RECHARGEABLE BATTERY D002 D008

BATTERY LEAD BATTERY LEAD SONOBUOY BATTERIES D008

BATTERY LEAD ACID BATTERY LEAD D008

BATTERY LEAD ACID BATTERY LEAD ARSENIC, LEAD, ANTIMONY, SULFURIC ACID D002 D004 D008

BATTERY LEAD ACID BATTERY LEAD BATTERY LEAD ACID D008

BATTERY LEAD ACID BATTERY LEAD BATTERY LEAD ACID EMPTY D009

BATTERY LEAD ACID BATTERY LEAD LEAD, SULFURIC ACID D002 D008

BATTERY LEAD ACID BATTERY LEAD LEAD, SULFURIC ACID HAS BEEN DRAINED D008

BATTERY LEAD GEL BATTERY LEAD LEAD, ARSENIC, SULPHURIC ACID, ANTIMONY D002 D004 D008

BATTERY LITHIUM BATTERY LI 4286.1 D001 D003

BATTERY LITHIUM BATTERY LI BATTERY D003

BATTERY LITHIUM BATTERY LI BATTERY CHANGEOUT D003

BATTERY LITHIUM BATTERY LI BATTERY REPLACEMENT ADDED TO 678 D001 D003

BATTERY LITHIUM BATTERY LI BLXLF CKFWF BRSVY BMWYS D001 D003

BATTERY LITHIUM BATTERY LI CHHRX BWKXT BVZQB D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERIES D001

BATTERY LITHIUM BATTERY LI LITHIUM BATTERIES D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERIES D003




Page 12



BATTERY LITHIUM BATTERY LI LITHIUM BATTERIES FROM COMM D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY ACCUMULATION D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY LITHIUM ACETONITRILE D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY LITHIUM ACETONITRILE 4060 5057 D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY LITHIUM ACETONITRILE 4090 SP54 D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY VP92-2 D003

BATTERY LITHIUM BATTERY LI LITHIUM BATTERY WITHOUT ACETONITRILE D003

BATTERY LITHIUM BATTERY LI LITHIUM METAL, SULPHUR DIOXIDE, ACETONITRILE D001 D003

BATTERY LITHIUM BATTERY LI LITHIUM METAL, SULPHUR DIOXIDE, ACETONITRILE D001 D003 U003

BATTERY LITHIUM BATTERY LI SONOBUOY BATTERY & VP10,VPU1 RADIO BATTERIES D003

BATTERY LITHIUM BATTERY LI SONOBUOY BATTERY CHANGEOUT D001 D003

BATTERY LITHIUM BATTERY LI SPENT BATTERIES D001 D003

BATTERY LITHIUM BATTERY LI SPENT LITHIUM BATTERY D003

BATTERY MAGNESIUM BATTERY MAGNESIUM BATTERIES D005 D007

BATTERY MAGNESIUM BATTERY MAGNESIUM BATTERY CHANGEOUT D005 D007

BATTERY MAGNESIUM BATTERY MAGNESIUM BATTERY MAGNESIUM D002

BATTERY MAGNESIUM BATTERY MAGNESIUM BATTERY MAGNESIUM D005 D007

BATTERY MAGNESIUM BATTERY MAGNESIUM MAGNESIUM BATTERIES D005 D007

BATTERY MAGNESIUM BATTERY MAGNESIUM MAGNESIUM BATTERY D005 D007

BATTERY MAGNESIUM BATTERY MAGNESIUM NONRCHARGE BATTERY D007

BATTERY MERC/LITHI BATTERY MAGNESIUM LITHIUM AND MERCURY BATTERIES D001 D003 D009

BATTERY MERCURY BATTERY MERCURY AIMD D009

BATTERY MERCURY BATTERY MERCURY AIMD BATTERIES D009

BATTERY MERCURY BATTERY MERCURY ALKALINE BATTERY, MERCURY, D009

BATTERY MERCURY BATTERY MERCURY ALKALINE BATTERY, MERCURY, LEAD, CADMIUM, KOH D006 D008 D009

BATTERY MERCURY BATTERY MERCURY BA1574 DRY BATTERY D009

BATTERY MERCURY BATTERY MERCURY BATTERY MERCURY D009

BATTERY MERCURY BATTERY MERCURY BATTERY MERCURY,DRY CELL D009

BATTERY MERCURY BATTERY MERCURY BATTERY NONRECHARGEABLE DRY D009

BATTERY MERCURY BATTERY MERCURY BATTERY,DRY D009

BATTERY MERCURY BATTERY MERCURY BNZRP BNBCL D009

BATTERY MERCURY BATTERY MERCURY CARBON ZINC D009

BATTERY MERCURY BATTERY MERCURY CARBON ZINC BATTERY D009

BATTERY MERCURY BATTERY MERCURY EQUIPMENT CHANGEOUT D009

BATTERY MERCURY BATTERY MERCURY FROM SQUADRONS D009

BATTERY MERCURY BATTERY MERCURY MERCURIC BATTERIES D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES VP92-3 D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES FROM AIMD/VP92 D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES FROM STROBE LITES D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERIES HAZMAT-5 D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERY D009

BATTERY MERCURY BATTERY MERCURY MERCURY BATTERY D009

BATTERY MERCURY BATTERY MERCURY RED OXIDE MERCURY BATTERIES D009

BATTERY MERCURY BATTERY MERCURY STORAGE BATTERY, KOH D009

BATTERY MERCURY BATTERY MERCURY UNICOR ADDED TO DO 26-0016 D009

BATTERY MERCURY BATTERY MERCURY USED MERCURY BATTERY D009

Page 13



BATTERY MERCURY BATTERY MERCURY WASTE MERCURY BATTERIES D009

BATTERY MERCURY BATTERY MERCURY WASTE MERCURY BATTERY D009

BATTERY NI CAD BATTERY NI-CAD HELICOPTER BATTERY FROM OMD D002 D006

BATTERY NI/CAD BATTERY NI-CAD BATTERY NI/CAD DOI8

BATTERY NICAD BATTERY NI-CAD AIMD D002 D006

BATTERY NICAD BATTERY NI-CAD AIMD D006UW

BATTERY NICAD BATTERY NI-CAD BATTERY CHANGEOUT D006

BATTERY NICAD BATTERY NI-CAD BATTERY CHANGEOUT D002 D006

BATTERY NICAD BATTERY NI-CAD BATTERY NICAD D002 D006

BATTERY NICAD BATTERY NI-CAD BATTERY TURN IN FROM AIMD D006

BATTERY NICAD BATTERY NI-CAD CADIMIUM OXIDE, NICKEL HYDROXIDE, POTASSIUM D002 D006

BATTERY NICAD BATTERY NI-CAD CCMHV D002 D006

BATTERY NICAD BATTERY NI-CAD EMERGENCY LIGHT BATTERIES D002 D006

BATTERY NICAD BATTERY NI-CAD GENERATOR KNOWLEDGE D006

BATTERY NICAD BATTERY NI-CAD MEDICAL D006

BATTERY NICAD BATTERY NI-CAD NICAD BATERIES D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES FROM BOB D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES VP8-3 AIMD-50 D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERIES WITH KOH D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERY D002 D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERY D002 DOO6

BATTERY NICAD BATTERY NI-CAD NICAD BATTERY D006

BATTERY NICAD BATTERY NI-CAD NICAD BATTERYS D006

BATTERY NICAD BATTERY NI-CAD NICADS FROM MEDICA D006

BATTERY NICAD BATTERY NI-CAD NICAF BATTERY D002 D006

BATTERY NICAD BATTERY NI-CAD NICKEL CADMIUM BATTERIES D002 D006

BATTERY NICAD BATTERY NI-CAD NICKEL-CADMIUM BATTERY D006

BATTERY NICAD BATTERY NI-CAD NIFE NICAD BATTERYS D002 D006

BATTERY NICAD BATTERY NI-CAD SCA BATTERIES D006

BATTERY NICAD BATTERY NI-CAD USED BATTERIES FROM PW D002 D006

BATTERY NICAD BATTERY NI-CAD VARIOUS TYPES D006

BATTERY NI-CAD BATTERY NI-CAD NICKEL, POTASSIUM HYDROXIDE, CADMIUM D002 D006

BATTERY PACK BATTERY NI-CAD CADMIUM D002 D006

BATTERY WASTE BATTERY ALKALINE POTASSIUM HYDROXIDE, MERCURIC OXIDE, MERCURY D002 D009

BATTERY, ALDALINE BATTERY ALKALINE BATTERY, ALKALINE; MERCURY, POTASSIUM HYDROXIDE, D002 D009

BATTERY, ALKALINE BATTERY ALKALINE D002

BATTERY, ALKALINE BATTERY ALKALINE MERCURY, LEAD, CADMIUM, KOH D006 D008 D009

BATTERY, DRY BATTERY ALKALINE MERCURY, MECURIC OXIDE, ZINC, POTASSIUM HYDROXIDE D002 D009

BATTERY, LEAD ACID BATTERY LEAD BATTERY, LEAD ACID D008

BATTERY, LEAD ACID BATTERY LEAD BATTERY, LEAD ACID STORAGE D002 D008

BATTERY, LEAD ACID BATTERY LEAD BATTERY, LEAD ACID, SEALED D002

BATTERY, LIGHTALARM BATTERY LEAD SULFURIC ACID, WATER D002

BATTERY, LITHIUM BATTERY LI BATTERY, LITHIUM D003

BATTERY, LITHIUM BATTERY LI LITHIUM METAL, 5 ADDED WITH 1348 3344/5017, D003

BATTERY, LITHIUM BATTERY LI LITHIUM METAL, SULPHUR DIOXIDE, ACETONITRILE D003 U003

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BATTERY, MAG/MN DIO BATTERY MAGNESIUM BATTERY, MAGNESIUM/ MANGANESE DIOXIDE D005

BATTERY, MAGNESIUM BATTERY MAGNESIUM BATTERY, DRY, MAGNESIUM, SPENT D007

BATTERY, MAGNESIUM BATTERY MAGNESIUM MAGNESIUM-CARBON BATTERYS, SPENT D003 D005 D007

BATTERY, MERCURY BATTERY MERCURY D009

BATTERY, MERCURY BATTERY MERCURY BATTERY, MERCURY D009

BATTERY, MERCURY BATTERY MERCURY BATTERY, MERCURY SPENT D009

BATTERY, MERCURY BATTERY MERCURY BATTERY, MERCURY, SPENT D009

BATTERY, MERCURY BATTERY MERCURY MERCURY < 5% D009

BATTERY, MERCURY BATTERY MERCURY MERCURY BATTERYS D002 D009

BATTERY, MERCURY BATTERY MERCURY MERCURY BATTERYS, SPENT D002 D009

BATTERY, MERCURY BATTERY MERCURY MERCURY, KOH D002 D009

BATTERY, MERCURY BATTERY MERCURY MERCURY, KOH D009

BATTERY, MERCURY BATTERY MERCURY MERCURY, MERCURY OXIDE, POTASSIUM HYDROXIDE D002 D009

BATTERY, MG/CARBON BATTERY MAGNESIUM BATTERY, MAGNESIUM-CARBON D007

BATTERY, MG/MNO2 BATTERY MAGNESIUM BATTERY, MAGNESIUM/ MANGANESE DIOXIDE D005

BATTERY, NI/CAD BATTERY NI-CAD BATTERY, NICKEL/ CADMIUM D018

BATTERY, NI/CAD BATTERY NI-CAD BATTERY, NICKEL-CADMIUM D006

BATTERY, NICAD BATTERY NI-CAD BATTERY, NICAD W/POTASSIUM HYDROXIDE D006

BATTERY, NI-CAD BATTERY NI-CAD D002

BATTERY, NI-CAD BATTERY NI-CAD D002 D006

BATTERY, NI-CAD BATTERY NI-CAD D006

BATTERY, NI-CAD BATTERY NI-CAD BATTERY, NI-CAD D002

BATTERY, NI-CAD BATTERY NI-CAD BATTERY, NI-CAD, SPENT D002

BATTERY, NI-CAD BATTERY NI-CAD BATTERY, NI-CAD, SPENT D006

BATTERY, NI-CAD BATTERY NI-CAD BATTERY, NICKEL-CADMIUM D002

BATTERY, NI-CAD BATTERY NI-CAD NICKEL D002 D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL, CADMIUM, POTASSIUM HYDROXIDE D002 D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERIES, SPENT D002 D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERY W/ POTASSIUM HYDROXIDE D002 D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERYS D002 D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERYS D006

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERYS, SPENT D006 D002

BATTERY, NI-CAD BATTERY NI-CAD NICKEL-CADMIUM BATTERYS, SPENT, CONTAINING LIQUID D002 D006

BATTERY, NONRECH BATTERY MERCURY MERCURY, KOH D009

BATTERY, SILVER BATTERY SILVER SILVER BATTERY, SPENT D002 D011

BATTERY, STORAGE BATTERY MERCURY BATTERY, STORAGE D002

BATTERY, STORAGE BATTERY MERCURY POTASSIUM HYDROXIDE D002

BATTERY, WASTE BATTERY MERCURY POTASSIUM HYDROXIDE, MERCURY, MANGANESE DIOXIDE, D002 D009

BATTERY, WASTE BATTERY MERCURY POTASSIUM HYDROXIDE, MERCURY, MANGANESE DIOXIDE, D009

BATTERY, WET W/ALKA BATTERY NI-CAD WET BATTERY, WET FILLED W/ ALKALI, NI-CAD D002

BATTERY, WET, NI-CA BATTERY NI-CAD WET BATTERY, NI-CAD, WET W/ ALKALI D002

BATTERY,LEAD ACID BATTERY LEAD BATTERY, LEAD ACID D008

BATTERY,MERCURY BATTERY MERCURY BATTERY, MERCURY D009

BATTERY/LITHUIM BATTERY LI BATTERY /LITHUIM D002

BATTERY/SILICA GEL BATTERY LEAD BATTERY /SILICA GEL D002

BB WASH B&B WASH BB WASH WITH CADMIUM D006

BENZOIN IN ALCOHOL BENZOIN TINCTURE IN ALCOHOL D001

BIOGENIC SOLVENT D-LIMONENE, ALKALINE BUILDERS, EMULSIFIERS D001

BLACK UNKNOWN LEAD 78.88; CHROMIUM 68.0; XYLENE 170.0; TOLUENE D001 D007 D008 F003 F005

Page 15



BLANKET WASH LITHOGRAPHIC BLANKET WASH D001

BLANKET WASH TETRACHLOROETHYLENE 25%, MINERAL SPIRITS, UNK D001 D039 F002

BLAST BOOTH FILTERS BLAST BOOTH FILTERS BLAST BOOTH FILTERS FROM 900 DIV D006 D007

BLAST BOOTH FILTERS BLAST BOOTH FILTERS W/C 52A D006 D007

BLAST BOOTH FILTERS BLAST BOOTH FILTERS WC 520 & WC510 D006 D007

BLAST MEDIA BLAST MEDIA 710 BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA 900 BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA ALUMINUM OXIDE D006 D007

BLAST MEDIA BLAST MEDIA ALUMINUM OXIDE BLAST MEDIA D006

BLAST MEDIA BLAST MEDIA ALUMINUM OXIDE FROM WC 900 D006

BLAST MEDIA BLAST MEDIA ALUMINUM OXIDE WC 900 D006

BLAST MEDIA BLAST MEDIA BLAST MEDIA D006

BLAST MEDIA BLAST MEDIA BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA D006 D007 D008

BLAST MEDIA BLAST MEDIA BLAST MEDIA D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA AIMD-250 PW ELEC-37 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 250 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 D006

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 900 DIV D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 900 DIVISION D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 INSIDE D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 OUTSIDE D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 OUTSIDE HOPPER D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA BLDG 86 WC 900 D006

BLAST MEDIA BLAST MEDIA BLAST MEDIA FILTERS BLDG 86 900 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM 520 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM 900 DIV D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM 900DIV D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM AIMD D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM GSE CLEANOUT D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM W/C 520 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM W/C 520 BOOTH 14 D007



BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM WC 250 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA FROM WC900 D006 D007 D008

BLAST MEDIA BLAST MEDIA BLAST MEDIA W/C 520 BLDG 250 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA W/C 520 BOOTH #14 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA WC 900 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA WC520 D006 D007

BLAST MEDIA BLAST MEDIA BLAST MEDIA WC900 D006 D007

BLAST MEDIA BLAST MEDIA BLASTMEDIA W/C520 BLAST BOOTH D006 D007

BLAST MEDIA BLAST MEDIA CADMIUM D006

BLAST MEDIA BLAST MEDIA CHROMIUM D007

BLAST MEDIA BLAST MEDIA CHROMIUM 7.75 PPM D007

BLAST MEDIA BLAST MEDIA GLASS SPERES D005

BLAST MEDIA BLAST MEDIA HOBBY SHOP D006 D007

BLAST MEDIA BLAST MEDIA PAINT WASTE BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA PLASTIC BEADS/BLACK BEAUTY/GLASS BEADS BLAST MEDIA D006 D007

Page 16



BLAST MEDIA BLAST MEDIA PLASTIC BEADS/BLACK BEAUTY/GLASS BEADS BLAST MEDIA D007

BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA 900DIV BLDG 86 D006

BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA FROM WC 520 D006 D007

BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA WC 520 D006 D007

BLAST MEDIA BLAST MEDIA PLASTIC MEDIA WC 60A 520 710 D006 D007

BLAST MEDIA BLAST MEDIA SHOP05H D006 D007

BLAST MEDIA BLAST MEDIA USED ALUMINUM OXIDE MEDIA D006

BLAST MEDIA BLAST MEDIA USED BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA USED PLASTIC MEDIA D006 D007

BLAST MEDIA BLAST MEDIA W/C 800 D006 D007

BLAST MEDIA BLAST MEDIA WALNUT SHELL BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA WASTE BLAST MEDIA D006

BLAST MEDIA BLAST MEDIA WASTE BLAST MEDIA D006 D007

BLAST MEDIA BLAST MEDIA WASTE BLAST MEDIA D007

BLAST MEDIA BLAST MEDIA WASTE BLAST MEDIA BLDG 86 GSE INSIDE D006 D007

BLAST MEDIA BLAST MEDIA WASTE BLAST MEDIA FROM GSE D006 D007

BLAST MEDIA BLAST MEDIA WC 92D D006 D007

BLAST MEDIA, DIRT BLAST MEDIA DIRT & BLAST MEDIA D007 D008

BLEACH D002

BLEACH STB BLEACH D001

BLEACH STP DECONTAMINATING AGENT D001

BLEACH FIXATIVE D011

BLEACH FIXATIVE BLEACH FIXATIVE D003

BLEACH FIXER BLEACH FIXER D011

BLEACH FIXER STAB. BLEACH FIXER STAB. D011

BLEACH NEUTRALIZER BLEACH NEUTRALIZER D011

BLEACH STB D002

BLIND NAIL CEMENT NAPTHA, ASBESTOS D001

BOILER ASH ANALYSIS D010

BOILER ASH ANALYSIS AEO8368 D010

BOILER TREATMENT BOILER TREATMENT CMPD - CORROSIVE BASE D002

BRAZING ALLOY BRAZING ALLOY, CONTAINING SILVER D011

CADMIUM SOLUTION CADMIUM SOLUTION D002 D006

CADMIUM STANDARD CADMIUM STANDARD D002 D006

CALCIUM HYPO CALCIUM HYPOCHLORITE TECHINAL D001

CALCIUM HYPO DRY CALCIUM HYPOCHLORITE POWDER D001

CALCIUM HYPOCHLORIT CALCIUM HYPOCHLORITE D001

CARBON REMOVAL COMP METHYLENE CHLORIDE, CRESOL, POTASSIUM HYDROXIDE D002 F002 F004

CARPET CLEANER 2-BUTOXY-ETHANOL, DIPROPYLENE GLYCOL METHYL ETHER D002

CAUSTIC CALCLEAN D002

CAUSTIC CORROSION REMOVING COMPOUND D002 D005

CAUSTIC DETERGENT D002

CAUSTIC FLOOR STRIPPER D002

CAUSTIC FLOOR STRIPPER D002

CAUSTIC FLOOR WAX REMOVER Ph 13 D002

CAUSTIC INDUSTRIAL WATER TREATMENT W142 D002

CAUSTIC Ph 14 D002

Page 17



CAUSTIC AEROSOL AEROSOL OVEN CLEANER D002

CEMENT ADHESIVE CEMENT ADHESIVE D001

CEMENT, CONTACT SEE ANALYSIS KAL-153 D001

CEMENT, ROOF ASPHALT D001

CEMENT, ROOF, UNK SEE ANALYSIS DCM-157 D001 D007

CEMENT, RUBBER MEK, TOLUENE D001 D035

CHARCOAL CANISTER CHARCOAL CANISTER D007

CHECK SOLUTION WOOD FIBER CHECK SOLUTION D001 D002

CHLORHEXIDINE CHLORHEXIDINE GLUCONATE SOLUTION D001

CHLOROFORM TREATMENT PLANT D022 U044

CHLOROFORM ACS CHLOROFORM ACS D022

CHROMATE INDICATOR CHROMATE INDICATOR DOO7

CHROMIC ACID D002

CHROMIC ACID CHROMIC ACID D001 D007

CHROMIC ACID CHROMIC ACID, SOLID D001

CHROMIUM STANDARD CHROMIUM STANDARD D002 D007

CLEAN UP DEBRIS RAGS, CLEAN UP, SATURATED W/JP-5 D001

CLEANER ANTI STATIC CLEANER COMPOUND D001

CLEANER CLEANER, LUBRICANT & PRESERVATIVE F001 F002 D005

CLEANER CLEANING COMPOUND D001

CLEANER CLOROBEN PT-4 D001

CLEANER DEMKOTE STEAM SOLV D002

CLEANER DRAINO D002

CLEANER EXPIRED CLEANER D002

CLEANER FILM CLEANER D001

CLEANER FLOOR WAX D002

CLEANER PORCELAIN CLEANING COMPOUND D002

CLEANER SOARBEN SOAP D002

CLEANER TC-100 WASH CONTAMINATED WITH CADMIUM D006

CLEANER ZOLV DRAIN CLEANER D039

CLEANER AEROSOL AEROSOL CRT SCREEN CLEANER D001

CLEANER GAS PATH CLEANER GAS PATH D001

CLEANER GEN PURPOSE CLEANER GEN PURPOSE D001

CLEANER LENS ETHYL ALCOHOL, METHYL ALCOHOL D001

CLEANER WASTE SODIUM DICHROMATE, SULFURIC ACID D002 D007

CLEANER, OVEN D001 D002

CLEANER, SUPER BRIT D001

CLEANING CMPD CLEANING COMPOUND - CONTACT X D001

CLEANING CMPD A/C CLEANING COMPOUND A/C SURFACE, OVERAGED D001

CLEANING CMPD, SOLV CLEANING COMPOUND, SOLVENT D001

CLEANING CMPD, SOLV CLEANING COMPOUND, SOLVENT F002

CLEANING COMP. CLEANING COMP. D001

CLEANING COMPOUND F002

CLEANING COMPOUND 1,1,2 TRICHLORO-1,2,2 TRIFLUOROETHANE F002

CLEANING COMPOUND CLEANING COMPOUND D001

CLEANING COMPOUND CLEANING COMPOUND (CONTACT X) D001

CLEANING COMPOUND CLEANING COMPOUND A/C SURFACE D001

CLEANING COMPOUND CLEANING COMPOUND, LENS D001

CLEANING COMPOUND CLEANING COMPOUND-CORROSIVE LIQUID D002

Page 18



CLEANING SOLVENT D001

CLEANING SOLVENT METHYLENE CHLORIDE, NAPTHA F001

CLEANING SOLVENTS CLEANING SOLVENTS (DE-75) W/ CUTTING OILS D001

CLEAR FINISH NAPTHA, SILICA EARTH VOL ORGANIC COMPOUNDS D001

CLICK PATCH INORGANIC DICHROMATE D007

CLICK PATCH MEK D001 D035 F005

COATING COMPOUND COATING COMPOUND FOR AMMUNITION D001

COATING CORROSION D001

COATING ROOF D001

COATING, EPOXY COATING, EPOXY D001

COD REAGENT CHEMICAL OXYGEN DEMAND REAGENT D002 D007 D009 D011

COLOR DEVELOPER DEVLOPER COLOR DEVELOPER D002

COLOR DEVELOPER DEVLOPER COLOR DEVELOPER D011

COLOR FIX USED SILVER + FIXER D011

COMPOUND CLEANING 1,1,2-TRICHLORO-TRIFLOUROETHANE, DICHLORODIFLUORO- F002

COMPOUND CORROSION PETROLEUM BASED CORROSION PREVENTATIVE D001

COMPOUND CORROSION TECTYL 846 CORROSION COMPOUND D001

COMPOUND SEALING TOLUENE, LEAD D001 D008

COMPOUND WALKWAY NAPTHA, MINERAL SPRITS D001

CONCRETE SEALER XYLENE D001 F003

CONDUCTIVE COATING CONDUCTIVE COATING - VOID D001

CONDUCTIVE COATING PAINT RELATED MATERIAL D001

CONDUCTIVE COATING TOLUENE, MEK D001 D035 F005

CONDUCTIVE COATING TOLUENE, MEK, D001 D035

CONDUCTIVE COATING TOLUENE, XYLENE, TOLUENE-2,4-DIISOCYANATE, D001 F003 F005

CONFORMAL COATING CONFORMAL COATING D001

CONTAMINATED SOIL BENZENE 5%; SOIL 95% 27 DRUMS (2-D018/25-SOIL) D018

CORR. PREV. CMPD. CORROSION PREVENTIVE COMPOUND D002

CORRECTION FLUID CORRECTION FLUID D001 F003

CORRECTION FLUID CORRECTION FLUID D001 F003 U359

CORROSION COATING ALODINE D002 D007

CORROSION COATING CHROMIC ACID D002 D007

CORROSION COATING CHROMIUM OXIDE D002 D007

CORROSION COMPOUND D001

CORROSION PREV CMPD D001

CORROSION PREV CMPD 112 TRICHLORO 122-TRIFLUOROETHANE; NAPTHA; CO2 F002

CORROSION PREV CMPD 112-TRICHLORO 122-TRIFLUOROETHANE; CO2; F002

CORROSION PREV CMPD BARIUM SOAP OF AN OSYGENATED HYDROCARBON D005

CORROSION PREV CMPD CORROSION PREVENTATIVE COMPOUND; FREON 113 & F12 F002

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND D001

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND D001 D005 F002

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND D001 F003 F005 U075

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND D005 F002

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND, SPENT D001

CORROSION PREV CMPD CORROSION PREVENTIVE COMPOUND, SPENT F002

CORROSION PREV CMPD CORROSION PREVENTIVE XCOMPOUND, SPENT D001

CORROSION PREV COM F002

CORROSION PREV COM ORMD

CORROSION PREV. CMP CORROSION PREVENTIVE COMPOUND D001

Page 19



CORROSION PREV. CPD D001

CORROSION PREV. CPD BARIUM COMPOUNDS, FREON 113 D005

CORROSION PREVENT BARIUM COMPOUNDS 20%; FREON 113 45% D005

CORROSION PREVENT STODDARD SOLVENT 40-55% D001

CORROSION PREVENTAT CORROSION PREVENTATIVE COMPOUND F002

CORROSION PREVENTIV D001

CORROSION PREVENTIV STODDARD SOLVENT 40-55% D001

CORROSION RESIST CD CORROSION RESISTENT COMPOUND D002 D007

CORROSION RESISTENT CORROSION RESISTENT COMPOUND-ALODINE D002

CORROSION RMVG CMPD CORROSION REMOVING COMPOUND D002

CORROSIVE D002

CORROSIVE D002 D004 D008 D018

CORROSIVE AMMONIUM HYDROXIDE D002

CORROSIVE AQUA TREET FROM HEAT PLANT D002

CORROSIVE CORROSIVE LIQUID D002

CORROSIVE DETERGENT D002

CORROSIVE EXCESS EXTENDER FROM MACHINE D002

CORROSIVE EXTEND RUST TREATMENT D002 D005

CORROSIVE FLOOR POLISH REMOVER D002 D006 D008 D010

CORROSIVE FLOOR POLISH REMOVER D002

CORROSIVE FLOOR POLISH REMOVER D002

CORROSIVE FLOOR STRIPPER D002

CORROSIVE FLOOR WAX REMOVER D002

CORROSIVE MACRO MAG D-19 D002 D007

CORROSIVE ND-66 CLEANER D001

CORROSIVE OLD WAX SYSTEM D002

CORROSIVE OVERAGE DUE POOR MANAGEMENT D001 D002

CORROSIVE PAINT REMOVER D002 D006

CORROSIVE SULFURIC ACID D002

CORROSIVE VP-10/AIMD D007

CORROSIVE ACID DEVELOPER CLEANER, SULFURIC ACID, SODIUM CHROMATE D002 D007

CORROSIVE ACID DILUTE ACID D002

CORROSIVE ACID MURIATIC ACID D002

CORROSIVE ACID SOLUTION "E" D002

CORROSIVE ALK OVEN CLEANER, SODIUM HYDROXIDE D002

CORROSIVE PREVENTIV CORROSIVE PREVENTIVE D001

CORROSIVE PREVENTIV CORROSIVE PREVENTIVE D002

CORRSION COMPOUND D001

CREOSOTE CREOSOTE, SPENT U051

CRT 10EA VARIOUS D008UW

CRT 12EA D008

CRT 12EA GENERATOR KNOWLEDGE D008

CRT 12EA GENERATOR KNOWLEDGE DOO8

CRT 12EA GENERATOR KNOWLEDGE D008UW

CRT 12EA NCTAMS LANT DET D008UW

CRT 12EA VP-92 D008UW

CRT 13EA IT & 62 D008UW



Page 20



CRT 18EA GENERATOR KNOWLEDGE DOO8


CRT 1EA MWR D008

CRT 20EA CRTS FROM DRMO PORTMOUTH D008

CRT 21EA SEE ATTACHED D008UW

CRT 24EA D008UW

CRT 27EA NAVAL SECURITY D008UW


CRT 40EA WING FIVE D008UW


CRT 5EA BEQ/IT D008UW





CRT SCREEN CARE 2-BUTOXYETHANOL, HYDROCARBON PROPELLANT D001

CUPRIC SULFATE ORME

CUT-THRU, 1740 CLEANER COIL HEAVY DUTY DOO1

CUTTING FLUID CUTTING FLUID D001

CUTTING FLUID CUTTING FLUID ORME

CUTTING FLUID CUTTING FLUID, DIRTY D001

CYCLOHEXANONE D001 F003

CYCLOHEXYLAMINE CYCLOHEXYLAMINE D001

CYLINDERS EMPTY FRO CYLINDERS EMPTY FROEN DICHLORODIFLOROMETHANE D009

DAMPING FLUID DAMPING FLUID D001

DAMPING FLUID DAMPING FLUID ORMC

DE-75 SOLVENT DE-75 CLEANING SOLVENT D001

DE-75 SOLVENT DE-75 PETROLEUM SOLVENT, SPENT D001

DEBRIS HANGAR ONE LEAD AND ASBESTOS DEBRIS D008

DEBRIS LEAD PAINT DEBRIS BEQ REHAB N62472-91-0494 D008

DEBRIS LEAD PAINT DEBRIS BLDG 13/295 N62472-95-M-7205/720 D008

DEBRIS LEAD PAINT DEBRIS HGR 250 N62472-94-B-0421 D008

DEBRIS SPILL FUEL/OIL/WATER FROM SPILL AND BLDG 77 D001

DEBRIS SPILL TRANSFORMER OIL PADS SPEEDY DRY AND DEBRIS MA01

DEBRIS, CLEAN-UP CLEAN UP DEBRIS, RAGS W/ SOLVENTS D035

DECON KIT DECON 1 DECON 2 D001

DECON KITS EXPIRED DECON KITS D001 D002

DECONTAM AGENT CHLORINATED LIME D001

DEICER FLUID DEICER FLUID D001

DENATURED ALCOHOL ALCOHOL, DENATURED, EXCESS D001 F003

DENTAL RESIN ETHYL METHACRYLATE, ETHYLENE GLYCOL DIMETHACRYLATE D001

DENTAL RESIN ETHYL METHACRYLATE, TOLUIDINE D001

DEODORANT DEODORANT U072

DEODORANT, GEN PURP GENERAL PURPOSE DEODORANT D001

DERA 1,1,1 TRICHLOROETHANE U226

DERA BLDG 95 DEBRIS U061

DERA BLDG 95 SOILS U120 D012 D014 D031 D041 U022 U031 U036 U050 U060 U061

DERA BLDG 95 SOILS U120 D012 D014 D031 D041 P123 U022 U031 U036 U050 U060 U061

DERA FIRE TRAINING PIT D001

Page 21



DERA LEAD SITE 11 D008

DERA RQ WASTE PESTICIDES LIQUID TOXIC NOS D012 D014 D031 D041 U022 U031

DERA SITE 1 & 3 U036 D002 D020 D016 U240

DESEALANT D001

DETERGENT SODIUM HYDROXIDE D002

DEVELOPED BLEACH D011

DEVELOPER DEVLOPER D011

DEVELOPER DEVLOPER DEVELOPER D001

DEVELOPER DEVLOPER DEVELOPER D002

DEVELOPER DEVLOPER DEVELOPER STARTER D002

DEVELOPER DEVLOPER OVERAGE DEVELOPER D002

DEVELOPER PART A DEVLOPER POTASSIUM CARBONATE, POTASSIUM SULFITE D002

DEVELOPER REPLENISH DEVLOPER ACID D002

DEVELOPER REPLENISH DEVLOPER BASIC - K HYDROXIDE D002

DEVOLPER USED DEVOLPER USED D002

DEVOLPER USED DEVOLPER USED D011

DEVOLPER,ZEROX DEVOLPER,ZEROX D002

DIAZINON DIAZINON SOLUTION ORM-A

DICHLORODIFLUOROMET DICHLORODIFLUOROMETHANE U075

DICHLOROMETHANE DICHLOROMETHANE F001

DICHLOROMETHANE DICHLOROMETHANE U080

DICHLOROMETHANE DICHLOROMETHANE (METHYLENE CHLORIDE), CONTAMINATED U080

DICHLOROMETHANE DICHLOROMETHANE 100% U080

DICHLOROMETHANE METHYLENE CHLORIDE F002

DIE SPACE BLUE DIE SPACE BLUE FROM DENTAL D001

DIESEL START FLUID DIESEL STARTING FLUID - VOID D001 F003

DIETHALAMINEPROPAL BPFKJ D001 D02

DIETHANOL AMINE DIETHANOL AMINE SALT OF 2- METHYL, 4-CHLORO- U240

DIETHYERETRIAMINE DIETHYERETRIAMINE D002

DIETHYLENE TRIAMINE DIETHYLENTRIAMINE, CORROSIVE D002

DIETHYLENETRIAMINE AIMD D002

DIETHYLENETRIAMINE DIETHYLENETRIAMINE D001



DIETHYLENETRIAMINE DIETHYLENETRIAMINE TECHNICAL D001 D002

DIETHYLENETRIAMINE DIETHYLENETRIAMINE, DIRTY D002

DISPERSANT DISPERSANT D001

DISPERSANT SAVIN COPIER DISPERSANT D001

DISPERSION COATING DISPERSION COATING-FLAMMABLE LIQUID D001

D-PHENOTHRIN TRICHLOROMETHANE, DICHLORODIFLUOROMETHANE F002

DRY BATTERIES MERCURY, POTASSIUM HYDROXIDE D002 D009

DRY-CLEANING SOLV DRY CLEANING SOLVENT D001

DRY-CLEANING SOLVEN DRY-CLEANING SOLVENT D001

DS-2 DECONTAM AGENT DS-2 DECONTAMINATING AGENT D002

DUOFILM ETHYL ETHER D001 F003

DUPLICATING FLUID DUPLICATING FLUID D001

DUPLICATING FLUID DUPLICATING FLUID D001 F003

DUPLICATING FLUID DUPLICATING FLUID DOO1 F003 U359

DUPLICATING FLUID DUPLICATING FLUID- FLAMMABLE LIQUID D001

Page 22



DUPLICATING FLUID METHANOL, ETHANOL D001

DUPLICATING FLUID METHANOL, ETHANOL, ETHYLENE GLYCOL D001

DYE, RED LIQUID DYE, RED LIQUID - FLAMMABLE LIQUIDS D001 F003

EEBD EMERGENCY BREATHING DEVICE D005

EEBD EXPENDED O2 CANISTERS D001 D003 D005

EEBD OXYGEN BREATHING EXPENDED D005

ELECT INSULATING CP TOLUENE 20%, POLYMER 76% D001 F005

ENAMEL ALKYD YELLOW LEAD CHROMATE D001 D007 D008

ENAMEL BLACK GLOSS SOLVENT, NAPTHA D001

ENAMEL GLOSS GRAY MEK D001 D035

ENCAPSULANT, NONRCR PAINT LATEX ENCAPSULANT, NON-RCRA UNK

ENCAPSULANT-NONRCRA PAINT LATEX ENCAPSULANT UNK

ENVIROSOLVE ULTRASONIC CLEANER WASTE W/C 400 D006 D007

EPO-LUX 100E XYLENE, N-BUTYL ALCOHOL D001 F003

EPO-LUX 100ME XYLENE, EHTYL BENZENE, N-BUTYL ALCOHOL D001 F003

EPOXY CATALYST METHYL ETHYL KETONE D001 D035

EPOXY CHROMATE PRIM TOLUENE, CHROMIUM D001 D007 F005

EPOXY COAT PART A METHYL ETHYL KETONE, TOLUENE D001 D035

EPOXY COAT PART A METHYL ETHYL KETONE, TOLUENE D001 FOO5 D035

EPOXY COAT PART A TOLUENE D001 D007

EPOXY COAT PART A TOLUENE, MEK D001 D035

EPOXY COAT PART B D001

EPOXY COAT PART B MEK, ISOPROPYL ALCOHOL D001 D035

EPOXY COAT PART B METHYL ETHYL KETONE, N-BUTYL ALCOHOL D001 FOO3

EPOXY COATING D001 D035 F003 F005

EPOXY COATING ISOPROPYL ALCOHOL 15%, TOLUENE 10%, MEK 15% D001 F003 F005

EPOXY COATING MEK, TOLUENE D001 D035 F005

EPOXY COATING N-BUTYL ALCOHOL D001 F003

EPOXY COATING COMPA METHYL ETHYL KETONE, XYLENE, ISOUTANOL, TOLUENE D001 F003 F005 D035

EPOXY COATING COMPB METHYL ETHYL KETONE D001 F005 D035

EPOXY COATING KIT D001 D035 F005

EPOXY COATING PT A D001 D035

EPOXY COATING PT A MEK, BARIUM, CADMIUM D001 D005 D006 D035

EPOXY COATING PT A MEK, XYLENE D001 D035

EPOXY COATING PT B D001 D035

EPOXY COATING PT B MEK D001 D035

EPOXY COMPONENT "B" NITROETHANE D001

EPOXY CURING AGENT BENZENE, MIK D001 D018

EPOXY CURING AGENT XYLENE D001 F003

EPOXY PATCH KIT EPOXY PATCH KIT TRIETHYLENE DIETHYLENE TRIAMINE D001

EPOXY PATCH PART A EPOXY PATCH PART A D001

EPOXY POLY PAINT TOLUENE, MEK D001 D035

EPOXY PRIMER PART A TOLUENE, XYLENE, BUTYL ALCOHOL D001 F003 F005

EPOXY PRIMER PART B BUTYL ALCOHOL D001 FOO3

EPOXY REPAIR KIT EPOXY REPAIR KIT D001

EPOXY RESIN PART A CHROMIUM, TOLUENE D001 D007 F005

EPOXY RESIN PART A EPOXY RESIN - PART "A" D001

EPOXY RESIN-PART B EPOXY RESIN - PART "B" D001

EPOXY RESIST FINISH BENZENE D001 D018

Page 23



EPOXY THINNER D001

ETHER, PETROLEUM NAPTHA D001

ETHYL ACETATE TECH ETHYL ACETATE, ETHYL ALCOHOL D001

ETHYL ALCOHOL TECH ETHYL ALCOHOL D001

ETHYLMETHYL ALCOHOL ETHYL ALCOHOL, METHYL ALCOHOL D001

FIBERGLASS RESIN FIBERGLASS RESIN D001 D035

FILLER, WOOD MEK D001 D035

FILM CLEANER, COND. FILM CLEANER - 1,1,1 TRICHLOROETHANE F002

FILTER LEAD LEAD D008

FILTER PAINT FILTER 60A PAINT FILTERS D007

FILTER PAINT FILTER PAINT FILTERS D007

FILTERS BLAST BOOTH FILTERS D007

FILTERS FUEL JP-8 FILTERS D001

FILTERS, CARBON CHROMIC ACID D007

FILTERS, LEAD LEAD DEBRIS - FILTERS D008

FIXATIVE D011

FIXATIVE X-RAY FIXATIVE X-RAY D011

FIXER ANALYSIS AEO2497 D009 D010 D011

FIXER BDQKX D009

FIXER DENTAL/MEDICAL D009 D010 D011

FIXER DUPONT DEVELOPER D002

FIXER FIXER D011

FIXER FIXER FROM DENTAL D011

FIXER FIXER FROM MEDICAL D011

FIXER FIXER FROM MEDICAL DO11



FIXER HAZMAT AND MEDICAL D009 D010 D011

FIXER KODAK BLEACH II STARTER D002

FIXER MEDICAL D009 D010 D011

FIXER PHOTO FIXER D011

FIXER PHOTOGRAPHIC FIXER D011

FIXER SILVER FIXER D011

FIXER SILVER LADEN BLACK & WHITE CHEMISTRY D011

FIXER SILVER WASTE D011

FIXER USED BLACK & WHITE FIXER D011

FIXER USED BLACK AND WHITE FIXER D011

FIXER USED COLOR FIXER D011

FIXER USED DEVELOPER D011

FIXER USED FIXER D011

FIXER USED FIXER FROM MEDICAL D011

FIXER USED X RAY FIXER D011

FIXER USED X-RAY FIXER D011

FIXER USED XRAY FIXER ACCUMULATION D011

FIXER X-RAY FIXER D011

FIXER XRAY FIXER CONSOLIDATION D011

FIXER XRAY FIXER FROM MEDICAL/DENTAL D011

FIXER STABILIZER D011

FIXER STABILIZER FIXER STABILIZER D011

Page 24



FIXER WASTE SILVER, ACETIC ACID, ALUMNIUM CHLORIDE, AMMONIUM D011

FIXER WORK STRENGTH SILVER + FIXER D011

FIXER, X-RAY, USED AMMONIUM THIOSULFATE, ACETIC ACID, SODIUM SULFITE, D011

FLOOR COAT XYLENE D001 F003

FLOOR POLISH REMOVE FLOOR POLISH REMOVER; SODIUM HYDROXIDE D002

FLUID, SPIRIT METHANOL D001

FLUORCARBON LUBE 1,1,2-TRICHLORO-1,2,2-TRIFLUOROETHANE, ISOBUTANE D001

FLUORESCENT BULBS BROKEN LIGHT BULBS D009

FLUORESCENT BULBS FLUORESCENT BULBS D009

FLUX FLUX D002

FLUX ROSIN FLUX D001

FLUX SOLDERING SOLDERING FLUX D001

FORMALDEHYDE FORMALDEHYDE D001

FORMULA 724 CLEANER FORMULA 724 CLEANER, SPENT D001

FREEZING COMPOUND D001

FREON CONTAMINATED FREON F002

FREON 113 FREON 113 F003

FREON SPRAY KIT TRICHLOROTRIFLUOROETHANE, ISOBUTANE, F002

FROSTING SPRAY NAPTHA, TOLUENE, METHYLENE CHLORIDE D001

FUMITOXIN #5857-2 ALUMINUM PHOSPHIDE, AMMONIUM CARBONATE P006

GALVANIZING POWDER GAVALNIZING POWDER D005

GAS PATH CLEANER GAS PATH CLEANER D001

GASOLINE GASOLINE D001 D018

GASOLINE GASOLINE AND OIL D001 D008 D018

GASOLINE GASOLINE/DIESEL WASTE D001

GASOLINE GASOLINE/SPEEDY DRY D001 D018

GASOLINE /WATER BENEZENE, TOLUENE, ETHYL BENEZENE, XYLENE D001 D018 F003 F005

GASOLINE CONTAM. CONTAMINATED GASOLINE D001 D018

GASOLINE FILTER GAS FILTER GASOLINE FILTERS D001 D018

GASOLINE WASTE FUEL FARM TANK CLEANING - CONTRACT CLEANING FOR D001 D018

GASOLINE, CONTAM. GASOLINE, CONTAMINATED W/ WATER & DIRT D001

GLASS CLEANER ETHANOL, 2- BUTOXY ETHANOL, DETERGENT, BUTANE, D001

GLASS, GARNET STRONTIUM CHROMATE D007

GREASE ANTISEIZE COMPOUND D008

GREASE ASSORTED GREASE D005 D007

GREASE BARIUM, SODIUM CHROMATE D005 D007

GREASE EXPIRED GREASE D008

GREASE GREASE D001

GREASE GREASE F003

GREASE GREASE MA01

GREASE GREASE WIRE ROPE D008

GREASE GREASE, AIRCRAFT, EXCESS D007

GREASE GREASE, AIRCRAFT, EXCESS U012

GREASE GREASE, GENERAL PURPOSE, EXCESS D005

GREASE GREASE, SPENT D001

GREASE HEAT GREASE MA01

GREASE LEAD PLATE D008

GREASE LEAD-COTE D008

GREASE LUBRICANT MA01

Page 25



GREASE LUBRICANT SOLID FLUX D001 D008 D035

GREASE LUBRICATING COMPOUND D001

GREASE MOLYBDENUM DISULFIDE MA01

GREASE A/C GREASE AIRCRAFT AND INSTRUMENT D025

GREASE, AIRCRAFT GREASE, AIRCRAFT D001

GREASE, AUTOMOTIVE LEAD ALKYL DITHIOCARBANATE D008

GREASE, FLAMMABLE GREASE, FLAMMABLE SOLID D001

GREASE, MOLY GREASE, MOLYBDENUM DISULFIDE D025

GREASE, WIRE ROPE GREASE, WIRE ROPE, DIRTY D008

HALGENATED SOLVENTS HALOGENATED SOLVENTS F003

HALGENATED SOLVENTS SOLVENT HALOGENATED HALOGENATED SOLVENTS F002

HALGENATED SOLVENTS SOLVENT HALOGENATED HALOGENATED SOLVENTS F003

HALO RAGS W/ SOLV HALOGENATED RAGS WASTE RAGS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

HALO SOLVENT F002

HALO SOLVENT 1,1,2 TRICHLORO, F002

HALO SOLVENT HAL SOLV; FREON 113 F002

HALO SOLVENT HAL SOLV; TRICHLOROTRIFLUOROETHANE (FREON 113) F002

HALO SOLVENT HALO SOLVENT F002

HALO SOLVENT HYDRAULIC FLUID, 1,1,2 TRICHLORO, F002

HALO SOLVENT HYDRAULIC FLUID, ENGINE OIL, JP5, 1,1,2 TRICHLORO, F002

HALO SOLVENT RAG TRICHLOROETHANE, 1,1,1- F002

HALO SOLVENTS F001

HALO SOLVENTS F002

HALO SOLVENTS HALOGENATED SOLVENTS F001

HALO SOLVENTS HALOGENATED SOLVENTS F002

HALO SOLVENTS HALOGENATED SOLVENTS; PRM; JP5; HYD FLUID D007 D008 D035 F002 F003 F005

HALO SOVLENT HAL SOLV; FREON 113, ISOPROPYL ALCOHOL D001 F002

HALO WASTE RAGS W/S HALOGENATED RAGS WASTE RAGS SATURATED W/ SOLVENTS D001 F002

HALOGENATE SOLVENTS F001

HALOGENATED HALOGENATED SOLVENT HYD OIL FREON 113 ISOPROPYL D001 F002

HALOGENATED HALOGENATED SOLVENT HYD OIL FREON 113 TURBINE OIL D001 F002

HALOGENATED HALOGENATED SOLVENT HYD OIL FREON 113 TURBINE OIL F002

HALOGENATED HALOGENATED SOLVENT HYD OIL ISOPROPYL D001

HALOGENATED HALOGENATED SOLVENT, HYD OIL, FREON 113, BARIUM D005 F002

HALOGENATED HALOGENATED SOLVENT, HYDRAULIC OIL, 1,1,1 TRICH F002

HALOGENATED HALOGENATED SOLVENT, HYDRAULIC OIL, 1,1,2 TRICH F002

HALOGENATED METHYL CHLOROFORM CFC U226

HALOGENATED NDI DEVELOPER F002

HALOGENATED AEROSOL AEROSOL HALOGENATED CORROSION PREVENTATIVE COMPOUND D005

HALOGENATED RAGS HALOGENATED RAGS D001

HALOGENATED RAGS HALOGENATED RAGS 1,1,2 TRICHLORO-1,2,2 TRIFLUOROETHANE F002

HALOGENATED SOLV F002

HALOGENATED SOLV HALOGENATED SOLVENTS D001

HALOGENATED SOLV HALOGENATED SOLVENTS F002

HALOGENATED SOLV HALOGENATED SOLVENTS F005

HALOGENATED SOLV HAOGENATED SOLVENTS F003

HALOGENATED SOLV HYDRAULIC FLUID; TRICHLOROTRIFLUOROETHANE F002

HALOGENATED SOLV. HALOGENATED SOLVENT F002

HALOGENATED SOLV. HALOGENATED SOLVENTS D001

Page 26



HALOGENATED SOLV. HALOGENATED SOLVENTS F001

HALOGENATED SOLV. HALOGENATED SOLVENTS F002

HALOGENATED SOLV. HALOGENATED SOLVENTS, CLEANERS, SPENT F002

HALOGENATED SOLV. HALOGENATED SOLVENTS, CONTAMINATED F002

HALOGENATED SOLV. HALOGENATED SOLVENTS, CONTAMINATED W/ OILS, FUELS D001

HALOGENATED SOLVENT F001

HALOGENATED SOLVENT 1,1,2 TRICHLORO-1,2,2 TRIFLUORETHANE, F002

HALOGENATED SOLVENT 1,1,2 TRICHLORO-1,2,2 TRIFLUOROETHANE F002

HALOGENATED SOLVENT 1,1,2TRICHLORO-1,2,2-TRIFLUORETHANE, CADMIUM D006 F002

HALOGENATED SOLVENT FREON 113, HYDRAULIC FLUID F002

HALOGENATED SOLVENT FREON 113, ISOPROPYL ALCOHOL, HYDRAULIC FLUID D001 F002

HALOGENATED SOLVENT FREON 16.7, 1,1,1 TRICH 66.6, HYD FLUID 16.7 F002

HALOGENATED SOLVENT HALOGENATED SOLVENT D001

HALOGENATED SOLVENT HALOGENATED SOLVENT F001



HALOGENATED SOLVENT HALOGENATED SOLVENTS F002

HALOGENATED SOLVENT HALOGENATED SOLVENTS F003

HALOGENATED SOLVENT HALOGENATED SOLVENTS, AEROSOL CANS F002

HALOGENATED SOLVENT HALOGENATED SOLVENTS, CONTAMINATED D001

HALOGENATED SOLVENT HALOGENATED SOLVENTS, CONTAMINATED W/ OILS, FUELS F002

HALOGENATED SOLVENT HYDRAULIC FLUID, F002

HALOGENATED SOLVENT HYDRAULIC FLUID, 1,1,2 TRICHLORO-1,2,2- F002

HALOGENATED SOLVENT HYDRAULIC FLUID, BARIUM, 1,1,2 TRICHLORO-1,2,2- D005 F002

HALOGENATED SOLVENT HYDRAULIC FLUID, FREON 113, METHYL CHLOROFORM F002

HALOGENATED SOLVENT HYDRAULIC FLUID, ISOPROPYL ALCOHOL, 1,1,2 TRICH- D001 D005 F002

HALOGENATED SOLVENT HYDRAULIC FLUID, ISOPROPYL ALCOHOL, 1,1,2 TRICH- D001 F002

HALOGENATED SOLVENT HYDRAULIC FLUID, METHYL CHLOROFORM F002

HALOGENATED SOLVENT HYDRAULIC OIL, 1,1,2-TRICHLORO-1,2,2 TRIFLUOR- F002

HALOGENATED SOLVENT HYDRAULIC OIL, JP-5, 1,12-TRICHLORO-1,2,2 TRIFLUOR F002

HALOGENATED SOLVENT ISOPROPYL ALCOHOL, HYDRAULIC FLUID, JP-5 D001 F002

HALOGENATED SOLVENT ISOPROPYL ALCOHOL-<2%, 1,1,2 TRICHLORO-1,2,2-TRIF- F002

HALOGENATED SOLVENT SOLVENT HALOGENATED HYDRAULIC FLUID, PD 680, 1,1,2-TRICHLORO 1,2,2- F002

HALOGENATED WASTE HALOGENATED WASTE D001 D005 F002

HALOGENATED WASTE R 1,1,1-TRICHLOROETHANE, HYD FLUID F002

HALO-SOLVENT AEROSOL F002

HEATING OIL #2 KEROSENE, NAPHTHALENE D001

HELMET LINER MATERI TRICHLOROFLUOROMETHANE F002

HYD FLUID WITH TRIC HYD FLUID WITH TRIC F001

HYD FLUID/FREON HYD FLUID /FREON D001

HYDRAULIC FLUID HYDRAULIC FLUID WITH FROEN D001

HYDRAULIC FLUID HYDRAULIC FLUID, CONTAMINATED D001

HYDRAULIC FLUIDS HYDRAULIC FLUID /HALOGENS D001

HYDROCHLORIC ACID D002

HYDROCHLORIC ACID HYDROCHLORIC ACID D002



HYDROGEN PEROXIDE HYDORGEN PEROXIDE 50% SOLUTION D001 D002

INHIBITOR 46 PHOSPHORIC ACID D002

Page 27



INK INDELIBLE INK D001

INK INK CLEANER D001

INK, MARKING INK, MARKING D001 F003

INSECT FOGGER METHYL CHLOROFORM <89.5%, PYRETHRUM 0.5% F002

INSECTICIDE D-PHENOTHRIN, TRICHLOROFLUOROMETHANE F002

INSECTICIDE DURSBAN (R) 4 E D001

INSECTICIDE DURSBAN PRENTOX CARBAMATE F002

INSECTICIDE INSECTICIDE AEROSOL D022

INSECTICIDE, GOVT TRICHLOROFLUOROMETHANE, DICHLORODIFLUOROMETHANE, F002

INSP PENETRANT PT B METHYL CHLOROFORM F002

INSP PENETRANT PT C METHYL CHLOROFORM F002

INSULATING CMPD INSULATING CMPD, AEROSOL-FLAMMABLE GAS D001

INSULATING COMPOUND INSULATING COMPOUND PO-12-007M D001

INSULATING VARNISH INSULATING VARNISH; ACETONE, MEK, TOLUENE D001 D035 F003 F005

INSULATING VARNISH XYLENE, PROPYLENE GLYCOL, ETHYL BENZENE D001

IODIDE IODATE REAGE R-0699 BOILER PLANT D002

IODINE SOLUTION D00N

ISOAMYL ACETATE ISOAMYL ACETATE D001

ISOBUTANE GAS BOTTL ISOBUTANE GAS BOTTLES D001

ISOCYANATE D001 D035 F003 F005

ISOPAR D001

ISOPAR M-CUTTING ISOPAR M-CUTTING FLUID D001

ISOPROPYL ALCOHOL D001

ISOPROPYL ALCOHOL ISOPROPYL ALCOHOL D001

ISOPROPYL ALCOHOL ISOPROPYL ALCOHOL, CONTAMINATED W/ RUST & WATER D001

ISOPROPYL ALCOHOL ISOPROPYL ALCOHOL, DIRTY D001

ISOPROPYL ALCOHOL ISOPROPYL ALCOHOL,DIRTY D001

JP 8 AND WATER JP8 AND WATER FROM FUEL FARM D001 D018

JP-5, CONTAMINATED JP-5, CONTAMINATED W/ WATER D001

KAL-144 UNKNOWN D001 D028 D035

KAL-145 CHROMIUM 3510 PPM D001 D007

KAL-148 UNKNOWN D001

KAL-149 UNKNOWN D001

KIT, EPOXY PART A MEK, ISOPROPYL ALCOHOL D001 D035

LAB DEBRIS & SOILS SOILS & LAB GLASS, CONTAMINATED W/ VARIOUS D012 D013 D014 D032

LAB WASTE, LIQUIDS REANALYSIS & RESUBMITTED BY DOC#s 3R3E DERA 2 (DM3 F002

LAB WASTE, LIQUIDS REANAYLSIS & RESUBMITTED BY DOC# 3R3E DERA 1 D001 F002 F003

LABORATORY LIQUIDS D039 D040 D043 SEE CWM PROFILE AB6345 D002 D018 D019 D022 D029 D035

LABORATORY LIQUIDS DM #2 CHANGED TO 3R3E DERA 1 ID NO 93001 D002

LABORATORY LIQUIDS RESUBMITTED AS 3R3E DERA 2 (DM #3) 93002 D002

LABORATORY WASTES CWM PROFILE AB6346 D043

LAMP SODIUM LOW PRESSURE SODIUM LAMP D003

LAMP, MERCURY LAMP, MERCURY D009

LAMPS CRUSHED BULBS D009

LAMPS CRUSHED BULBS D009

LAMPS CRUSHED FLUORESCENT BULBS D009

LAMPS FLUORESCENT BULBS ACCUMULATION D009

LAMPS HIGH PRESSURE SODIUM D008 D009

LAMPS ROUND BULBS IN BOXES D009

Page 28



LAMPS 284 GENERATOR KNOWLEDGE D009

LAMPS 312 GENERATOR KNOWLEDGE D009UW

LAMPS 52 GENERATOR KNOWLEDGE D009

LAMPS 331 ANALYSIS 01241 D009UW

LATEX PAINT PAINT LATEX MERCURY, MEK, ACETONE D009 D035

LATEX, ACRYLIC VINYL CHLORIDE D043

LEAD DUST FILTERS D008

LEAD EXPLODED BATTERY D002 D008

LEAD LAMELLAS FROM SHOOTING RANGE D007 D008

LEAD LAMELLAS FROM SHOOTING RANGE D008

LEAD LEAD BLINDS D008

LEAD LEAD BLINDS FROM HOUSING D008

LEAD LEAD DEBRIS D008

LEAD LEAD DEBRIS FROM HGR THREE D008

LEAD LEAD DUST AND DEBRIS D008

LEAD LEAD LAMELLAS D008

LEAD LEAD LAMELLAS FROM SHOOTING RANGE D008

LEAD LEAD SOLDER D007 D008

LEAD LEAD SOLDER D008

LEAD NORTHEAST TEST CONSULTANTS D008

LEAD ROUNDS FROM FIRING RANGE D008



LEAD SEE ANALYSIS DOO8

LEAD SHOOTING RANGE LEAD LAMELLAS D008

LEAD ACID BATTERY BATTERY LEAD LEAD ACID BATTERY D002

LEAD ACID BATTERY BATTERY LEAD SULFURIC ACID, LEAD D002 D008

LEAD BLINDS LEAD BLINDS D008

LEAD BLINDS LEAD BLINDS FROM HOUSING D008

LEAD CONTAM DEBRIS LEAD, CADMIUM D006 D008 D035

LEAD DEBRIS D008

LEAD DEBRIS LEAD BLINDS D008

LEAD DEBRIS LEAD CONTAMINATED DEBRIS D008

LEAD DEBRIS LEAD DEBRIS D008

LEAD DEBRIS LEAD DEBRIS FROM HANGER THREE D008

LEAD DEBRIS LEAD LAMELAS D008

LEAD DEBRIS LEAD SOLDER D008

LEAD DEBRIS PAINT CHIPS, VACUUM BAGS, CARTRIDGES D008

LEAD DEBRIS(FILTERS LEAD DEBRIS (FILTERS) D005 D006 D007 D008

LEAD DROSS D008

LEAD DROSS LEAD DROSS, FILTERS D008

LEAD DUST & DEBRIS LEAD 2,630.0 PPM D008

LEAD FILTER LEAD HEPA VAC FILTERS & DEBRIS D008

LEAD FILTER LEAD LEAD COMTAMINATED LAMELLAS D008

LEAD FILTER LEAD SMALL ARM RANGE FILTERS D008

LEAD FILTERS LEAD CONTAMINATED FILTERS D008

LEAD FILTERS LEAD FILTERS D008

LEAD FILTERS, SOLID LEAD FILTERS, SOLID D008

LEAD REMOVAL BODG 905 LEAD REMOVAL D008

Page 29



LEAD RINSATE LEAD RINSATE FROM INDOOR FIRING RANGE D006 D008

LEAD RINSATE RINSE WATER FROM PISTOL RANGE D006 D008

LEAD SCRAP LEAD D008

LEAD STANDARD LEAD STANDARD D002 D008

LEAD WASTE DEMOLITION OF BLDG 293+614 D008

LEAD WASTE HANGAR 5 REPAIRS D008

LEAD WASTE HEPA FILTERS D008

LEAD WASTE LEAD DEBRIS FROM CONTRACTORS D008

LEAD WASTE LEAD PAINT CHIPS D008

LEAD WASTE LEAD WASTE D008

LEAD WASTE RANGE AIR FILTERS D008

LEAD WASTE REPAIR OF BLDG 25 D008

LEAD WASTE TOPSHAM SHOOTING RANGE D008

LINE CLEANING SOLV. LINE CLEANING SOLVENTS F002

LITHIUM BATTERY BATTERY LI LITHIUM BATTERYS, SPENT D003

LUBE OIL F002

LUBE OIL LUBE OIL D001

LUBE OIL, GEAR LUBRICATING OIL, GEAR D001

LUBRICANT BRAKE FREE LUBRICANT D005

LUBRICANT DRY FILM LUBRICANT D001

LUBRICANT GENERAL PURPOSE LUBE OIL D005

LUBRICANT INORGANIC LEAD COMPOUND, MEK, XYLENE = UNK % D001 D008 D035 F003 F005

LUBRICANT LEAD, MEK D001 D008 D035

LUBRICANT LUBRICANT D001

LUBRICANT SOLID LUBRICANT D001 D008

LUBRICANT AEROSOL AEROSOL LUBRICATING COMPOUND D001

LUBRICATING COMP METHYL CHLORFORM FOO2

LUBRICATING COMPOUN LUBRICATING COMPOUND D001

LUBRICATING OIL D001

LUBRICATING OIL LUBRICATING OIL, AEROSOL F002

MD-1931 XYLENE, MEK, N-BUTYNOL D001 D035 F003 F005

MEK MEK D001 D035 U159

MEK METHYL ETHYL KETONE F005

MERCURY BROCKED FLUORESCENT BULBS D009

MERCURY BROKEN LAMPS D009

MERCURY BROKEN LAMPS D009

MERCURY BROKEN MERCURY THERMOMETER D009

MERCURY BROKEN THERMOMETER D009

MERCURY CHANGE OUT OF SWITCHES D009

MERCURY FROM CONTRACTOR GYM FLOOR D009

MERCURY GENERATOR KNOWLEDGE D009

MERCURY LIGHT BULBS D009

MERCURY MERCURY D009

MERCURY MERCURY ANALYZED D002 D009

MERCURY MERCURY SWITCH D009

MERCURY MERCURY SWITCHES D009

MERCURY MERCURY SWITCHES FROM HANGAR 2 D009

MERCURY MERCURY SWITCHS D009

MERCURY MERCURY SWITCHS FROM DELUGE SYSTEM HGR 250 D009

Page 30



MERCURY MERCURY THERMOMETER D009

MERCURY MERCURY THERMOMETER D009

MERCURY MERCURY THERMOMETERS D009

MERCURY MERCURY THERMOMETERS CLIN 6630MM=8.00 D009

MERCURY MERCURY THERMOSTAT D009UW

MERCURY MERTHIOLATE D001 D009

MERCURY STEAM PLANT BROKEN MANOMETER D009

MERCURY STEAM PLANT BROKEN MANOMETER D009

MERCURY WASTE MERCURY D009

MERCURY ANALYZED MERCURY ANALYZED D009

MERCURY BATTERIES BYDZQ D009

MERCURY BATTERY BATTERY MERCURY D009

MERCURY BATTERYS BATTERY MERCURY BATTERY, MERCURY, SPENT D002

MERCURY BATTERYS BATTERY MERCURY BATTERYS, MERCURY, SPENT D002

MERCURY BATTERYS BATTERY MERCURY MERCURY BATTERYS ,SPENT D009

MERCURY BATTERYS BATTERY MERCURY MERCURY BATTERYS, SPENT D002

MERCURY BATTERYS BATTERY MERCURY MERCURY BATTERYS, SPENT D009

MERCURY DEBRIS D009

MERCURY DEBRIS MERCURY D009

MERCURY DEBRIS MERCURY CONTAMINATED DEBRIS D009

MERCURY DEBRIS MERCURY DEBRIS D009

MERCURY DEBRIS MERCURY THERMOMETER D009

MERCURY DIRTY D009

MERCURY GAUGES MERCURY D009

MERCURY STANDARD MERCURY STANDARD D002 D009

MERCURY SURCHARGE MERCURY SURCHARGE SURCHARGE

MERCURY SWITCHS MERCURY D009

MERCURY THERMOMETER MERCURY DEBRIS D009

MERCURY VAPOR LAMP D005

MERCURY VAPOR LAMPS MERCURY VAPOR LAMPS, SPENT D009

MERCURY WASTE MERCURY D009

MERCURY WASTE WASATE MERCURY, DIRTY D009

MERCURY, DIRTY MERCURY, DIRTY D009

MERTHIOLATE ACETONE 10%; ETHYL ALCOHOL 50% D001 F003

MERTHIOLATE MERTHIOLATE - FLAMMABLE LIQUID D001 F003

METAL CONDITIONER PHOSPHORIC ACID D002

METAL PRE TREAT D002

METHANOL METHANOL F003

METHYL CHLOROFORM METHYL CHLOROFORM U226

METHYL ETHYL KETONE METHYL ETHYL KETONE D001 D035

METHYL ETHYL KETONE METHYL ETHYL KETONE D035

METHYLENE CHLORIDE METHYLENE CHLORIDE U080

METHYLENE CHLORIDE METHYLENE CHLORIDE SOLVENT F002

M-GARD D001

MINERAL SPIRITS MINERAL SPIRITS D001

MINWAX POLYSHADE STODDARD SOLVENT, VEHICLE, ADDITIVES, PIGMENTS D001

MODEL SPRAY TOLUENE, HALOGENATED HYDROCARBON F002, F005

MOTH BALLS URINAL CAKES U072

MOTHBALLS MOTHBALLS U072

Page 31



MULTI-PURPOSE PATCH CHROMIUM D007

NAPHTHA CYCLOHEXANE, N-HEPTANE, TOLUENE, METHYLCYCLOHEXANE D001 F005

NAPTHA, ALIPHATIC TOLUENE D001

NI CAD BATTERY BATTERY NI-CAD NI CAD BATTERY D006

NICAD BATTERIES NICAD BATTERY D006

NI-CAD BATTERIES D006

NI-CAD BATTERIES NI-CAD BATTERIES D006

NICAD BATTERY BATTERY NI-CAD BFRPT BGNVG BPTVC D006

NI-CAD BATTERY BATTERY NI-CAD D006

NI-CAD BATTERY BATTERY NI-CAD NI-CAD BATTERY D006

NI-CAD BATTERY BATTERY NI-CAD NICKEL-CADMIUM BATTERYS, SPENT D002

NI-CAD BATTERYS BATTERY NI-CAD NICKEL-CADMIUM BATTERYS, SPENT D002

NITRATE SODIUM NITRATE CRYSTALS D001

NITRIC ACID D002

NON HALO SOLVENT D001

NON HALO SOLVENT NON HALOGENATED SOLVENT F005

NON HALO SOLVENTS D001

NON HALO SOLVENTS NON HALOGENATED SOLVENTS D001

NON HALOGENATED SOL NON HALOGENATED SOLVENTS D001

NON-HAL SOLVENT NON-HALOGENATED SOLVENTS D001

NON-HAL SOLVENTS ALCOHOL 58.6%; PD-680 36.45%; VVL-800 3.3%; D001

NON-HAL SOLVENTS ISOPROPYL ALCOHOL 43.3%; PD-680 56.6%; D001 F002

NON-HAL SOLVENTS JP5, LUBRICATING OIL, TYPE II DRY CLEANING SOLVENT D001

NON-HALO SOLVENT ISOPROPYL ALCOHOL, HYDRAULIC FLUID D001

NON-HALO SOLVENT MEK, NAPTHA D001 D035 F005

NON-HALO SOLVENTS NON-HALO SOLVENTS D001

NON-HALOGENATED NON-HALOGENATED WASTE D001

NON-HALOGENATED SOL D001

NON-HALOGENATED SOL N0N-HALOGENATED SOLVENTS D001

NON-HALOGENATED SOL NON-HALOGENATED SO0LVENTS, SPENT D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENT D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, CONTAMINATED D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, DIRTY D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, ISOPROPYL ALCOHOL D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, MIXED, SPENT D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, SPENT D001

NON-HALOGENATED SOL NON-HALOGENATED SOLVENTS, SPENT, DIRTY D001

NON-HALOGENATED SOL PETROLEUM SOLVENTS D001

O2 CLEANER BYRXJ D002

O2 CLEANER SHOP 81C D002

OBA BYBYB D001 D003 D005

OBA CJHDJ D001 D003 D005

OBA EEBD D001 D003 D005

OBA CANDLES OBA CANDLES FROM MARINES D001 D005

OBA CANNISTER EXPENDED OBA CANINSTER D001 D003 D005

OBA CANNISTER EXPENDED OBA CANNISTER D001

OBA CANNISTER EXPENDED OBA CANNISTER D001 D003 D005

OBA CANNISTER OVERAGE BREATHING DEVICES D001 D003 D005

Page 32



OBA GENERATORS EXPENDED OBA GENERATORS D001 D003 D005

OIL FLUID CHANGE OUT OIL D035

OIL VV-L-800 CFC F002

OIL /HALOGENS OIL CANTAINING /HALOGENS D001

OIL ABSORBENT PADS # 2 FUEL OIL DOO1

OIL AEROSOL AEROSOL SPRAY LUBE CFC F002

OIL GAS JET FUEL CONTAMINATED WITH WATER D001

OIL SWITCH OIL SWITCH W/ PCBS M002

OIL SWITCH OIL SWITCH W/PCBS M002

OIL, CONTAM W/SOLV. WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS D001

OIL, CONTAM. W/SOLV OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

OIL, CONTAMINATED OILS, CONTAMINATED W/ SOLVENTS D001

OIL, CONTAMINATED OILS, CONTAMINATED W/ SOLVENTS F002

OIL, CONTAMINATED WASTE OILS, CONTAMINATED W/ SOLVENTS D001

OIL, CONTAMINATEED OILS, CONTAMINATED W/ SOLVENTS D001

OIL, LUBE F002

OIL, LUBRICATING BARIUM SULFONATE D005

OIL, LUBRICATING LUBRICATING OIL, WASTE D025

OIL, LUBRICATING WASTE OILS D001

OIL, WASTE WASTE OIL, WATER, SLUDGE D001

OIL,LUBRICATING OIL,LUBRICATING D001

OIL/FUEL REMOVAL OF FUEL FROM BLDG 42 UST D001 D008 D018

OIL/GAS ACETONE AND JP8 D001 D018

OIL/GAS CONTAMINATED DIESEL D001 D018

OIL/GAS CONTAMINATED DIESEL FUEL D001 D018

OIL/GAS CONTAMINATED GAS FROM AUTO D001 D018

OIL/GAS CONTAMINATED GAS FROM TRANSPORTATION D001 D018

OIL/GAS FUEL AND OIL FROM TRANSFORMER D001 D018

OIL/GAS GASOLINE D001 D008

OIL/GAS GASOLINE D001 D008 D018

OIL/GAS GASOLINE AND OIL MIXTURE D001

OIL/GAS GASOLINE AND WATER D001 D018

OIL/GAS GENERATOR KNOWLEDGE D001

OIL/GAS JP8 & WATER SPILL CLEANUP D001

OIL/GAS JP8 AND MO GAS MIXTURE D001 D018

OIL/GAS JP8 AND WATER D001 D018

OIL/GAS JP8 FROM PRODUCT RECOVERY TANK MA01

OIL/GAS JP-8 SPILL CLEAN UP D001 D018

OIL/GAS LUBRICATING OIL GENERAL PURPOSE D005

OIL/GAS MOGAS AND OIL D001 D018

OIL/GAS MO-GAS OIL MIXTURE D001 D008

OIL/GAS MOTOR OIL AND GASOLINE D001 D018

OIL/GAS OIL AND GAS MIXTURE D001 D018

OIL/GAS PENETRATING OIL D001

OIL/GAS POL TANK HGR 3 DO18 D035

OIL/GAS SPILL DEBRIS D001

OIL/GAS TANK FROM STEAM PLANT D018 D035

OIL/GAS USED OIL WITH GAS D001 D018

OILS, CONTAM W/ SOL WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

Page 33



OILS, CONTAM W/SOLV OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

OILS, CONTAM W/SOLV OILS, CONTAMINATED W/ SOLVENTS F002

OILS, CONTAM. OILS/HYDRAULIC FLUIDS, CONTAMINATED W/ SOLVENTS F002

OILS, CONTAM. WASTE OILS, CONTAMINATED W/ SOLVENTS D001

OILS, CONTAM. WASTE OILS, CONTAMINATED W/ SOLVENTS F001

OILS, CONTAMINATED OILS CONTAMINATED W/ SOLVENTS D001

OILS, CONTAMINATED OILS, CONTAMINATED W HALOGENATED SOLVENTS F002

OILS, CONTAMINATED OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

OILS, CONTAMINATED OILS, CONTAMINATED W/ SOLVENTS D001

OILS, CONTAMINATED OILS, CONTAMINATED W/ SOLVENTS F002

OILS, CONTAMINATED WASTE HYDRAULIC OILS, CONTAMINATED W/HALOGENATED F001 F002

OILS, CONTAMINATED WASTE OILS CONTAMINATED W/ HALOGENATED SOLVENTS F002

OILS, CONTAMINATED WASTE OILS CONTAMINATED W/ SOLVENTS D001 F001 F002

OILS, CONTAMINATED WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS D001

OILS, CONTAMINATED WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS D001 F002

OILS, CONTAMINATED WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

ORGANIC PEROXIDE HARDNER FIBERGLASS RESIN D003

ORTHOPHOSPHORIC ACI ORTHO-PHOSPHORIC ACID 85 D002

OVEN CLEANER OVEN CLEANER D001

OVEN CLEANER SODIUM HYDROXIDE D002

OVEN CLEANER SODIUM HYDROXIDE, ETHANOLAMINE, BUTANE, H20 D002

PAINT D001 D006 D007 D008 D035

PAINT 05 RED PPAINT D001

PAINT 1544 ROSIN FLUX D001

PAINT 60A PAINT FILTERS & WASTE PAINT RAGS D001 D007 D035

PAINT 7268 ELECTRICAL COATING D001

PAINT 728013 METAL PRETREATMENT PART A D001 D007

PAINT 728013 METAL PRETREATMENT PART B D001 D002

PAINT 8B6A LAMINAR X500 CONDUCTIVE BLACK D001 D035

PAINT ABANDONED PAINT FROM NCTD D001 D035

PAINT ACCELERATORS D001 D035

PAINT ACCUMULATION DRUM D001 D006 D007 D008 D035

PAINT ACCUMULATION DRUM D001 D006 D007 D035

PAINT ACCUMULATION OF OVERAGE PAINTS D001 D005 D035

PAINT ACLYRLIC LACQUER, MEK, LEAD, TOLUENE, CHROMIUM D001 D007 D008 D035

PAINT ACRYLIC MASONRY FINISH D001 D009

PAINT AEROSOL D001 D008 D035

PAINT AEROSOL PAINT D001

PAINT AIMD D001 D006 D007 D035

PAINT AIRCRAFT WAX D001

PAINT AIROPS/AIMD D005

PAINT ALIPHATIC NAPTHA D001

PAINT ALKYD ENAMEL PAINT D001

PAINT ALKYD ENAMEL PAINT D001 D008

PAINT ALODINE WASTE D007

PAINT ALUMICUT D001

PAINT ANALYSIS D001 D006 D007 D008 D035

PAINT ASSORTED OVERAGE PAINTS D001 D006 D007 D008 D035

PAINT ASSORTED PAINT WASTE D001 D007 D008

Page 34



PAINT ASSORTED PAINT XYLENE MEK D001 D035

PAINT ASSORTED PAINT XYLENE MEK LEAD CHROMATE LEAD D001 D007 D008 D035

PAINT ASSORTED PAINTS D001 D008

PAINT ASSORTED PAINTS D001 D007 D008 D035 F002 F003 F005

PAINT BLACK CONDUCTIVE COATING D001 D035

PAINT BLACK ENAMEL PAINT D001 D005

PAINT BOOTH COAT D001 D035

PAINT BQGWX/Y BJQGB CCZXL BZFXY D001 D006 D007 D035 F002 F003

PAINT BTJQR CGFDN BJZSL CBVKP CGYBR D001 D006 D007 D035

PAINT CAMI GREY LACQUER D001

PAINT CARON CANORAMA TONER D001

PAINT CGNCV D002

PAINT CGNCV D002

PAINT CGNDT BZTBN 40501 D001 D006 D007 D008 D035

PAINT CGXTF BQGTP CDRVX G26684 K45331 D001 D006 D007 D008 D035

PAINT CGYBR BZTBQ CDHLT CCGMX CCMTM BJRNH CFCDW BVZNR D001 D006 D007 D008 D035

PAINT CHO-BOND PRIMER 1085 D011

PAINT CHROMATE PAINT D001 D007 D008

PAINT CLEAR URETHANE FINNISH D001

PAINT COATING COMPOUND D001

PAINT COATING COMPOUND PART A D001 D007

PAINT COATING COMPOUND PART B D001

PAINT COATING EPOXY POLYAMIDE D001

PAINT COND X AEROSOL D001

PAINT CONDUCTIVE COATINEG D001 D035

PAINT CONDUCTIVE COATING D001 D005 D018 D035

PAINT CONDUCTIVE COATING D001 D005 D035

PAINT CONDUCTIVE COATING D001 D018

PAINT CONDUCTIVE COATING D001 D035

PAINT CONDUCTIVE COATING BLACK PAINT D035

PAINT CONFORMAL COATING D001

PAINT CONSOLIDATION BRQMW

PAINT CONSOLIDATION DRUM D001 D006 D007 D008 D035

PAINT CONSOLIDATION DRUM D001 D006 D007 D035 F002 F003

PAINT CONTRACTOR D008

PAINT COPIER DEGLAZE D001

PAINT CORROSION COMPOUND D001

PAINT CORROSION PREVENTATIVE D001

PAINT CORROSION PREVENTATIVE D001 D007 D035

PAINT CORROSION PREVENTATIVE BARIUM D005

PAINT CORROSION PREVENTATIVE BARIUM FREON 113 D005

PAINT CORROSION PREVENTATIVE COMPOUND D001

PAINT CORROSION PREVENTATIVE COMPOUND D005

PAINT CORROSION PREVENTAVE D001

PAINT CORROSION PREVENTION COMP D001

PAINT CORROSION PREVENTIVE D001

PAINT CORROSION PREVENTIVE D005

PAINT CORROSION PREVENTIVE COMPOUND D001

PAINT CORROSION PREVENTIVE COMPOUND D005

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PAINT CORROSIVE PREVENTION COMPOUND D001

PAINT CPC TYPE II D005

PAINT DYE LIQUID D001

PAINT ELECTROSTATIC PRIMER EPOXY D001 D007

PAINT ENAMEL D001 D005 D035

PAINT ENAMEL ALKYD GLOSS BLUE D001 D035

PAINT ENAMEL GLOSS D001 D007 D008 D035

PAINT ENAMEL GLOSS ALKYD D001

PAINT ENAMEL GLOSS ALKYD D001 D035

PAINT ENAMEL PAINT D001

PAINT ENAMEL PAINT, LEAD CHROMATE D001 D007 D008

PAINT ENAMEL SILICONE ALKYD COPOLYMER D001

PAINT EPO-LUX THINNER D001

PAINT EPOXY COAT PART A D001 D035

PAINT EPOXY COAT PART B D001 D035

PAINT EPOXY COATING D001 D035

PAINT EPOXY COATING KIT D001 D035

PAINT EPOXY COATING KIT PART A D001 D006 D035

PAINT EPOXY COATING KIT PART A D001 D018 D035

PAINT EPOXY COATING KIT PART B D001 D035

PAINT EPOXY COATING PART A D001 D035

PAINT EPOXY COATING PART A D007

PAINT EPOXY POLYMIDE PART A D001

PAINT EPOXY POLYMIDE PART B D001

PAINT EPOXY PRIMER BASE ONLY D001 D007

PAINT EPOXY PRIMER BASE ONLY D001 D007 D035

PAINT EPOXY PRIMER COATING PART A D001 D007 D035

PAINT EPOXY PRIMER COATING PART B D001 D018

PAINT EPOXY PRIMER PART B D001

PAINT EPOXY THINNER D001 D035

PAINT ETHYL ACETATE, TOULENE, MEK D001 D035 F003 F005

PAINT EUCLID FLOOR PAINT D001

PAINT EXCESS PAINTS FROM SUPPLY PART A D001 D035

PAINT EXCESS PAINTS FROM SUPPLY PART B D001 D035

PAINT EXPIRED AEROSOL PAINT D001

PAINT EXPIRED PAINT D001

PAINT EXPIRED PAINT REMOVER D007

PAINT EXPIRED PAINTS D001 D008

PAINT EXPIRED PAINTS D001 D006 D007 D008 D035

PAINT EXPIRED PAINTS FROM HAZMAT D001 D035

PAINT EXPIRED PAINTS FROM HAZMAT + ITEM 304 FROM 1997 D001 D035

PAINT EXPIRED SHELF LIFE PAINTS D001 D007 D035

PAINT FAST DRYING POLYURETHANE CLEAR SEMIGLOSS II D001

PAINT FINISH COATING D001 D035

PAINT FIRESTONE ACRYLITOP D001

PAINT FLAT BLACK NO 412 D001

PAINT FLAT BLACK PAINT D001 D035

PAINT FLOOR POLISH REMOVER D002

PAINT FUEL FARM D001 D006 D007 D007 D035

Page 36



PAINT GOLD PAINT D001

PAINT GRAY ACTUATOR B D001 D035

PAINT GRAY COMP A D001 D018 D035

PAINT GRAY PRIMER PART A D001

PAINT GRAY PRIMER PART B D001

PAINT GREEN PAINT D001 D019

PAINT GREY SPRAY PAINT D001

PAINT HAZMAT AEROSOL D001

PAINT HAZMAT OVERAGE PAINT D001 D006 D007 D035 F002 F003 F005

PAINT HEAT RESISTANT PAINT D001

PAINT HOUSING DROP OFFS D001 D006 D007 D008 D035

PAINT INSULATING COMPOUND D001

PAINT INSULATING COMPOUND XYLENE TOLUENE-2-4DIISOCYANATE D001

PAINT INSULATING PAINT D001 D035

PAINT INSULATING VARNISH D001

PAINT INTERIOR PAINT D001

PAINT KRYLON 16022 ULTRA FLAT BLACK D001 D035

PAINT LACQUER D001 D007 D008 D035

PAINT LACQUER PAINT D001

PAINT LACQUER SPRAY PAINT D001 D007 D008 D035

PAINT LAMINAR HARDENER D001

PAINT LAMINAR HARDNER D001

PAINT LAMINAR X500 D001 D005 D035

PAINT LAMINAR X-500 D001 D005 D008 D018

PAINT LATEX PAINT D001

PAINT LATEX PAINT F002

PAINT LAYOUT DYE D001

PAINT LEAD CONTAMINATED PAINT CHIPS D008

PAINT LEAD PAINT CHIPS D008

PAINT LEAD, FP 58 DEG F D001 D008

PAINT LEFT BY CONTRACTOR D001 D006 D007 D035

PAINT LEFT BY VP-10 D001 D007 D008 D035

PAINT LEFT OVER PAINTS D001 D007 D035

PAINT LENMAR PAINT D001 D008 D035

PAINT LIQUID PAINT AND PENETRANTS D001 D005

PAINT MARINE POLYESTER RESIN D001

PAINT MARKING PAINT D001

PAINT MEK, TOLUENE, XYLENE D001 D035

PAINT METAL POLISH D001

PAINT METHYL N AMYL KETONE, XYLENE, TITANIUM DIOXIDE D001

PAINT MIL-P-23377E PART B D001

PAINT MIL-P-23377E PART B D001 D007 D035

PAINT MISC PAINT CANS D001 D007 D035

PAINT MISCELANEOUS PAINT D001 D007 D035

PAINT MIXED ASSORTMENT OF PAINT CANS D001 D007 D035

PAINT NAPTHA D001

PAINT NAPTHA, MINERAL SPIRITS D001

PAINT NOKORODE CORROSION PREVENTATIVE D001

PAINT NORSIC PRIMER ACCELERATOR D001

Page 37



PAINT OATEY PURPLE PRIMER D001 D035

PAINT OIL BASED PAINT D001

PAINT OLD ENAMEL PAINT D001 D007 D008

PAINT OLD PAINT FROM FUEL FARM D001 D006 D007 D035 F002 F003

PAINT OMD PAINT BARREL D001 D035

PAINT OVERAGE PAINT D001 D006 D007 D008

PAINT OVERAGE PAINT D001 D007 D035 D005

PAINT OVERAGE PAINT D001 D006 D007 D007 D035

PAINT OVERAGE PAINT FROM BOB D001 D007 D035

PAINT OVERAGE PAINTS D001 D007 D035

PAINT OVERAGE PAINTS D001 D035

PAINT OVERAGE PAINTS VP8 AND HAZMAT D001 D007 D035

PAINT PAINT D001

PAINT PAINT D001 D005 D035

PAINT PAINT D001 D006 D007 D008 D035

PAINT PAINT D001 D006 D008 D009 D018

PAINT PAINT D001 D007

PAINT PAINT D001 D007 D035



PAINT PAINT D001 F003


PAINT PAINT VPU1-6 D001 D004 D006

PAINT PAINT WASTE D001 D007 D035 F003 F005

PAINT PAINT & ADHESIVE WASTE D001 D007 D008 D035

PAINT PAINT AND THINNER AWAITING ANALYSIS 5201 A&B D001 D035 F003 F005

PAINT PAINT AND THINNER WASTE D001 D005 D007 F001 F003 F005

PAINT PAINT AND THINNER WASTE D001 D007 D018 D035

PAINT PAINT CHIPS D008

PAINT PAINT CHIPS CONTAMINATED WITH LEAD D007 D008

PAINT PAINT CHIPS FROM CHAPEL D008

PAINT PAINT CHIPS FROM CONTRACTOR D008

PAINT PAINT CHIPS FROM DECK D008

PAINT PAINT CHIPS FROM GUARDRAIL D007 D008

PAINT PAINT CHIPS FROM SEABEES D008

PAINT PAINT CONSOLIDATION DRUM D001 D035 F002 F005

PAINT PAINT DRUM D001 D006 D007 D035 F002 F003 F005

PAINT PAINT DRUM FROM SCA D001 D006 D007 D035 F002 F003 F005

PAINT PAINT FILTERS D007

PAINT PAINT FROM AEROSOL PUNCHER D001 D005 D019 D028 D029 D039 D035 D040

PAINT PAINT FROM OMD D001 D007 D035

PAINT PAINT FROM SEABEES D001 D035

PAINT PAINT FROM SUPPLY D001 D007 D035

PAINT PAINT FROM TREATMENT PLANT D001 D035

PAINT PAINT HARDNER D007 D008 D018

PAINT PAINT HEAT RESISTANT D001

PAINT PAINT LACQUER D001

PAINT PAINT LIQUID D001 D006 D007 D035

PAINT PAINT MISC D001 D007 D008 D035

Page 38



PAINT PAINT POLY GREY D001

PAINT PAINT REMOVER D007

PAINT PAINT REMOVER D007 D035

PAINT PAINT RUBBER D001

PAINT PAINT SHOP D001 D006 D007 D035

PAINT PAINT SHOP D001

PAINT PAINT SHOP D001 D006 D007 D008 D035

PAINT PAINT SHOP MISC GENERATORS D001 D006 D007 D035

PAINT PAINT SHOP MISC GENERATORS D001

PAINT PAINT STRIPPER D002 D007

PAINT PAINT STRIPPER D007

PAINT PAINT STRIPPER & WATER D007 F002

PAINT PAINT STRIPPER RINSE WATER D007 F001

PAINT PAINT THINNER D001

PAINT PAINT THINNER D001 D035

PAINT PAINT THINNER WASTE D001 D005 D007 D035 F001 F002

PAINT PAINT WASTE D001

PAINT PAINT WASTE D001 D005 D007 D035 F002 F003

PAINT PAINT WASTE D001 D005 D035

PAINT PAINT WASTE D001 D006 D007 D008 D035

PAINT PAINT WASTE D001 D006 D007 D035 F002 F003 F005


PAINT PAINT WASTE D001 D007 D008 D035

PAINT PAINT WASTE D001 D007 D008 D035 F003


PAINT PAINT WASTE D001 D007 D035 F002 F003 F005

PAINT PAINT WASTE D001 D007 D035 F003 F005

PAINT PAINT WASTE D001 D018 D035 F005

PAINT PAINT WASTE D001 D035

PAINT PAINT WASTE D001 D035 F003 F005

PAINT PAINT WASTE F003 F005 D001 D008 D019 D035 F001 F002

PAINT PAINT WASTE AND THINNER D001 D007 D035 F003 F005

PAINT PAINT WASTE BARREL D001 D035 F005

PAINT PAINT WASTE F005 D001 D005 D007 D035 F002 F003

PAINT PAINT WASTE FROM HANGAR 250 F002

PAINT PAINT WASTE FROM SCA D001 D035

PAINT PAINT WASTE FROM SCA D001

PAINT PAINT WASTE MEK D001 D035

PAINT PAINT WASTE MEK F005 D001 D019 D035 F001 F002 F003

PAINT PAINT WASTE MIK XYLENE TOLUENE MEK CHROMATE CADMIU D001 D006 D007 D035

PAINT PAINT WASTE XYLENE LEAD MEK CHROMIUM D001 D007 D008 D035 D039

PAINT PAINT WASTE, CHROMIUM, BARIUM, LEAD CHROMATE, MEK D001 D005 D007 D008 D035

PAINT PAINT WASTE, LEAD MEK D001 D008 D035

PAINT PAINT WASTE, MEK, ACETONE, XYLENE, TOLUENE D001 D035

PAINT PAINT, ALUMINUM D001

PAINT PART A and B PAINT D001 D035

PAINT PETROLEUM HYDROCARBONS D001

PAINT PETROLIUM BASED RUST PREVENTATIVE D001

PAINT PLASTIC POLISH D001

Page 39



PAINT POLISH REMOVER D002

PAINT POLY COAT PART A D001

PAINT POLY COAT PART A D001 D007

PAINT POLY COAT PART A D001 D035

PAINT POLY COAT PART A D001 DO35

PAINT POLY COAT PART B D001

PAINT POLY COAT PART B D001 D035

PAINT POLY COAT PART B D001 DO35

PAINT POLY COATING D001 D035

PAINT POLYURETHANE D001

PAINT POLYURETHANE D001 D007 D035

PAINT POLYURETHANE COATING D001

PAINT POLYURETHANE COATING KIT D001 D035

PAINT POLYURETHANE GREY D001 D035

PAINT POLYURETHANE KIT D001

PAINT POLYURETHANE PAINT PART A D001

PAINT POLYURETHANE PAINT PART A D001 D035

PAINT POLYURETHANE PAINT PART B D001 D035

PAINT POLYURETHANEE CURING AGENT D001

PAINT PPAINT D001 D005 D035

PAINT PPG GLOSS WHITE D001

PAINT PRIMER D001 D035

PAINT PRIMER ADHESIVE D001

PAINT PRIMER COATING D001 D005

PAINT PRIMER COATING D001 D005 D007

PAINT PRIMER COATING PART A D001 D007

PAINT PRIMER COATING PART B D001

PAINT PRIMER COATING PART B D001 D035

PAINT PRIMER COATING ZINC CHROMATE D001 D007 D008

PAINT PRIMER ENAMEL-UNDERCOAT ODORLESS INT WH D001

PAINT PRIMER PAINT D001

PAINT PRIMER T U226

PAINT PRIMER WASH PAINT D001 D007

PAINT PRIMER WASH PART A D001

PAINT PW TOM WRIGHT D001 D006 D007 D035

PAINT QASTE PAINT D001 D035

PAINT RAIN EROSION D001 D005 D035

PAINT RAIN EROSION COATING D005 D035

PAINT RAIN EROSION CONDUCTIVE BLACK D001 D005 D035

PAINT RAIN EROSION PAINT D001 D005 D035

PAINT RAIN EROSION PAINT D001 D035

PAINT RAIN ERROSION COATING D001 D035

PAINT RESIN D001

PAINT RID RUST D001

PAINT RUBBER PAINT D001 D035

PAINT RUST TREATMENT D002 D005

PAINT SCA PAINT DRUM D001 D006 D007 D035 F002 F003 F005

PAINT SCOTCHKOTE ELECTRICAL COATING D001 D035

PAINT SEALER-PRIMER D001

Page 40



PAINT SEE ANALYSIS D001 D006 D007 D035

PAINT SEE DUMP LOG D001 D006 D007 D008 D035 F002 F003

PAINT SELF PRIMING TOPCOAT D001

PAINT SEMI-GLOSS PAINT D001

PAINT SILICONE PRIMER D001 D018

PAINT SILICONE PRIMER D001 D035

PAINT SOLVENTS D001

PAINT SO-SURE SPRAY LACQUER D001

PAINT STAIN DARK REDWOOD D001

PAINT STAIN SOLUTION D001

PAINT STATICIDE D001

PAINT STODDARD SOLVENT D001

PAINT STRIPING PAINT D001 D005 D035

PAINT SUPER X FORM RELEASE D001

PAINT TECTIVE COATING V114L D001 D035

PAINT THINNER EPOXY D001 D035

PAINT TILECLAD ENAMEL D001 D007 D008

PAINT TOLUENE, ISOBUTYL ALCOHOL, PROPYLENE GLYCOL, D001 D007

PAINT TOLUENE, XYLENE, ACETONE, MEK D001 D005 D007 D008 D035

PAINT TONER CARTRIDGE D007

PAINT TRAFFIC PAINT D001

PAINT TTE489G WHITE ENAMEL D001 D008

PAINT TTE489H ENAMEL GLOSS D001 D005

PAINT TURPENTINE D001

PAINT TURPINTINE D001

PAINT TYPE M WHITE D001

PAINT UNKNOWN D001 D006 F003 F005

PAINT UNKNOWN D001 D008

PAINT USED PAINTS D001 D007 D035

PAINT VARIOUS PAINTS D001 D035

PAINT VARNISH D001

PAINT VP-10 D001 D006 D007 D035

PAINT VP-10 PAINT BARREL D001 D006 D007 D035

PAINT VP-8 D001 D006 D00 D035 F002 F003 F005

PAINT VP-92 D001 D006 D007 D008 D035

PAINT VR-62 D001 D006 D007 D035

PAINT WALKWAY COMPOUND D001

PAINT WALKWAY COMPOUND D001 D008

PAINT WALKWAY COMPOUND NON-SLIP D001

PAINT WASTE FROM J A JONES D008

PAINT WASTE LATEX PAINT D001

PAINT WASTE OIL BASE PAINT D001 D035

PAINT WASTE PAINT D001

PAINT WASTE PAINT D001 D005 D035 F003 F005

PAINT WASTE PAINT D001 D007 D035

PAINT WASTE PAINT D001 D007 D035 F001 F003 F005



PAINT WASTE PAINT D001 D008

Page 41





PAINT WASTE PAINT D001 D035

PAINT WASTE PAINT D001 D035 F003 F005


PAINT WASTE PAINT AND THINNER D001 D007 D035 F003 F005

PAINT WASTE PAINT AND THINNER D001 D035 F003 F005

PAINT WASTE PAINT F005 D001 D007 D008 D018 D035 F003

PAINT WASTE PAINT FROM AEROSOL D001 D005 D019 D028 D029 D039

PAINT WASTE PAINT FROM HAZMAT AEROSOL DRUM D001 D005 D007 D008 D035

PAINT WASTE PAINT FROM HOBBY SHOP D001

PAINT WASTE PAINT RAGS D001 D035 F003 F005

PAINT WASTE PAINT THINNER AND REMOVER D001 D007 D0035 F002 F005

PAINT WASTE RAGS, TOLUENE, XYLENE, ACETONE, MEK D001 D007 D035 F003 F005

PAINT WASTE RAGS, TOLUENE, XYLENE, ACETONE, MEK D001 D035 F002 F003

PAINT WASTE RAGS, TOLUENE, XYLENE, ACETONE, MEK D007 D035 F001 F003 F005

PAINT WASTE RAGS, TOLUENE, XYLENE, CHROMATE, MEK, MIK D001 D007 D035

PAINT WHITE ENAMEL PAINT D001

PAINT WHITE LACQUER D001

PAINT WHITE PAINT D001

PAINT WHITE UNICOAT D001 F003 F005

PAINT X O RUST D001

PAINT XYLENE, TOLUENE D001

PAINT XYLENE, TOLUENE, MIK, ISOBUTYL ALCOHOL, ACETATE D001

PAINT YELLOW A/D ENAMEL 13538 D001

PAINT YELLOW ENAMEL D001

PAINT YELLOW LACQUER D001

PAINT YELLOW PAINT D001

PAINT ZAR SATIN EXTERIOR POLYURETHANE D001

PAINT ZINC CHROMATE D001 D007

PAINT AEROSOL AEROSOL PAINT D001 D035

PAINT AEROSOL AEROSOL PAINT D001

PAINT AEROSOL AEROSOL WATER DISPLACING COMPOUND D001

PAINT AEROSOL EXCESS AEROSOLS FROM VPU-1 D001

PAINT AEROSOL STEEL INK BLUE AEROSOL D001

PAINT LAED LEAD CONTAMINATED DEBRIS D008

PAINT LEAD LEAD CONTAMINATED DEBRIS D008

PAINT PAINT RAGS WASTE RAGS, TOLUENE, XYLENE, ACETONE, MEK D001 D007 D035 F002 F003 F005

PAINT PAITN LATEX PW PAINT SHOP D001 D006 D007 D035

PAINT PAITN LATEX PW PAINT SHOP D001 D006 D007 D035

PAINT PAITN LATEX WASTE PAINT FROM PW D001 D035

PAINT AEROSOL AEROSOL D001

PAINT AEROSOL AEROSOL AEROSOL D001

PAINT AEROSOL AEROSOL AEROSOL PAINT D001 D007

PAINT AEROSOL AEROSOL AEROSOL PAINT WASTE CHROMIUM MEK XYLENE D001 D007 D035

PAINT AEROSOL AEROSOL AEROSOL PAINTS D001

PAINT AEROSOL AEROSOL ASSORTED SPRAY PAINT D001 D005

PAINT AEROSOL AEROSOL ASSORTED SPRAY PAINT D001 D035

PAINT AEROSOL AEROSOL CORROSION PREVENTATIVE FREON 113 D005

Page 42



PAINT AEROSOL AEROSOL CORROSION PREVENTIVE COMPOUND D005

PAINT AEROSOL AEROSOL CORROSION PREVENTIVE COMPOUND FREON 113 F002

PAINT AEROSOL AEROSOL ENAMEL FLAT GREY PAINT D001

PAINT AEROSOL AEROSOL ENAMEL PAINT LEAD TOLUENE XYLENE ACETONE D001 D008

PAINT AEROSOL AEROSOL LACQUER AEROSOL CLEAR D001

PAINT AEROSOL AEROSOL SO SURE SPRAY PAINT CHROMATE LEAD TOLUENE XYLENE D001 D007 D008

PAINT AEROSOL AEROSOL SPRAY PAINT TOLUENE XYLENE ETHYL BENZENE ACETONE D001 D007 D008

PAINT AEROSOL AEROSOL TRAFFIC PAINT ETC D001

PAINT AEROSOL AEROSOL UNKNOWN D001 D035

PAINT AEROSOL AEROSOL WASTE AEROSOL PAINT D001

PAINT AEROSOL CAN AEROSOL PAINT AEROSOL CAN D001

PAINT ALUMINUM D001

PAINT BLACK LAC D001

PAINT BLUE LAC D001

PAINT CHIPS LEAD PAINT CHIPS AND DEBRIS D008

PAINT CHIPS PAINT CHIPS FROM BUILDING D008

PAINT CONDUCTING D001

PAINT DEBRIS PAINT DEBRIS D008

PAINT DEBRIS PAINT SCRAPPINGS D008

PAINT DECK MINERAL SPIRITS, TALC, IRON OXIDE, TITANIUM OXIDE D001

PAINT DROSS D001

PAINT DROSS PAINT DROSS D001

PAINT DROSS PAINT DROSS (SOAK RAGS) D001

PAINT DROSS PAINT DROSS FILTERS D001

PAINT DROSS PAINT FILTERS D001

PAINT DROSS PAINT FILTERS D008

PAINT ENAMEL STODDARD SOLVENT D001

PAINT ENAMEL TOLUENE, ACETONE, CALCIUM-BARIUM PHOSPHOSILICATE D001 D005

PAINT ENAMEL LATEX PAINT LATEX MEDIUM ALIPHATIC NAPTHA D001

PAINT EPOXY D001

PAINT FILTER PAINT FILTER ANALAYSIS AEO2499 D006 D007

PAINT FILTER PAINT FILTER ANALYSIS 53041 D006 D007 D008

PAINT FILTER PAINT FILTER ANALYSIS 53041 D006 D007 D008 D009

PAINT FILTER PAINT FILTER FROM W/520 D007

PAINT FILTER PAINT FILTER PAINT FILTERS FROM WC 500 D007

PAINT FILTER PAINT FILTER PAINT FILTERS FROM WC60A D007

PAINT FILTER PAINT FILTER W/C 51B D007

PAINT FILTER PAINT FILTER W/C 920/60A D007

PAINT FILTER PAINT FILTER WC/92D D007

PAINT FILTERS AIR FILTERS D007

PAINT FILTERS AIR FILTERS EXHAUST D007

PAINT FILTERS BLAST BOOTH FILTERS 900 DIV D006

PAINT FILTERS CONTAMINATED LEAD FILTERS D008

PAINT FILTERS EXHAUST FILTERS FROM 500 DIVISION BLDG 250 D007

PAINT FILTERS EXHAUST PAINT FILTERS 900 DIV D006 D007

PAINT FILTERS FIBERGLASS/POLY PAINT DUST FILTERS D006 DOO7

PAINT FILTERS FILTER ELEMENTS D007

PAINT FILTERS PAINT BOOTH FILTERS OMD D007

PAINT FILTERS PAINT FILTER D007

Page 43



PAINT FILTERS PAINT FILTERS D007

PAINT FILTERS PAINT FILTERS 51 A/B D007

PAINT FILTERS PAINT FILTERS AIMD BLDG86 EXHAUST D007

PAINT FILTERS PAINT FILTERS BLDG 86 GSE D007

PAINT FILTERS PAINT FILTERS EXHAUST 51 A/B BLDG 250 D007

PAINT FILTERS PAINT FILTERS EXHAUST PAINT BOOTH #16 D007

PAINT FILTERS PAINT FILTERS EXHAUST PAINTBOOTH #18 D007

PAINT FILTERS PAINT FILTERS FROM 51B D007

PAINT FILTERS PAINT FILTERS FROM 51B LARGE BOOTH D007

PAINT FILTERS PAINT FILTERS FROM 51B SMALL AND LARGE BOOTH D007

PAINT FILTERS PAINT FILTERS FROM 900 BLAST BOOTH D007

PAINT FILTERS PAINT FILTERS FROM GSE BLDG 86 D007

PAINT FILTERS PAINT FILTERS FROM W/C 500 BLDG 250 D007

PAINT FILTERS PAINT FILTERS FROM W/C 51A D007 D008

PAINT FILTERS PAINT FILTERS FROM W/C 51B LARGE PAINT BOOTH D007

PAINT FILTERS PAINT FILTERS FROM W/C 900 D007

PAINT FILTERS PAINT FILTERS FROM WC 510 D007

PAINT FILTERS PAINT FILTERS FROM WC51B D007

PAINT FILTERS PAINT FILTERS W/C 900 BLDG 86 D007

PAINT FILTERS PAINT FILTERS WC 51B D007

PAINT FILTERS PAINT FILTERS WC 51B/900 D007

PAINT FILTERS PAINT RELATED MATERIAL-SOLID PAINT WASTE D007

PAINT FILTERS USED PAINT FILTERS D007 D035

PAINT FILTERS WASTE FIBERGLASS/POLY PAINT FILTER DUST FROM 51A D006

PAINT FILTERS WASTE PAINT FILTERS D007

PAINT FILTERS WC 51B AND 900 PAINT FILTERS D007

PAINT FILTERS WC 900 AND 520 PAINT FILTERS D007

PAINT FILTERS WC 900 PAINT BOOTH FILTERS D007

PAINT FILTERS WC 900 PAINT FILTERS D007

PAINT FILTERS PAINT FILTERS CHROMIUM D007

PAINT FILTERS PAINT FILTERS CHROMIUM, PAINT FILTERS D007

PAINT FILTERS PAINT FILTERS PAINT FILTERS D007

PAINT FILTERS PAINT FILTERS PAINT FILTERS FROM WC51B D007 D008

PAINT FILTERS PAINT FILTERS PAINT FILTERS, CHROMIUM D007

PAINT FILTERS PAINT FILTERS PAINT RELATED MATERIAL D007

PAINT FILTERS PAINT FILTERS PAINT RELATED MATERIAL D008

PAINT FILTERS PAINT FILTERS WC 900 D007

PAINT FILTERS PAINT FILTERS WC51B PAINT BOOTH D007 D008

PAINT FILTERS, WAST PAINT FILTERS CHROMIUM D007

PAINT GRAY LAC D001

PAINT ORANGE LAC D001

PAINT PRIMER D001

PAINT RAGS PAINT RAGS D001 D006 D007 D008 D035 F003 F005

PAINT RAGS PAINT RAGS ACCUMULATION DRUM D006 D007 D035

PAINT RAGS PAINT RAGS ACCUMULATION OF RAGS AIMD-39 D001 D018 D035 F003

PAINT RAGS PAINT RAGS ACCUMULATION OF RAGS VP10-68 VPU1-60 AIMD-54 VP92- D035 F003 F004

PAINT RAGS PAINT RAGS ACCUMULATION OF RAGS VP26-82 VR62-37 D035 F003 F005

PAINT RAGS PAINT RAGS AIMD D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS AIMD D001 D006 D007 D035

Page 44



PAINT RAGS PAINT RAGS AIMD D035

PAINT RAGS PAINT RAGS AIMD PAINT RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS BWGXZ BMWXJ BHDBV CFCSM CFCZF BWSDNBJSPR CBTRW D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS BXMCP CDMCQ BHBVF BTJQH D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS BZTBQ CKZHS D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS CDALR CFCSM BYRTW BQXZN D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS CONSOLIDATION D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS OIL AND PAINT RAGS D007 D035 F002 F003 F005

PAINT RAGS PAINT RAGS OIL SOAKED RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT AND THINNER RAGS D005 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT AND THINNER RAGS D005 D007 D035 F001 F003 F005

PAINT RAGS PAINT RAGS PAINT RAG CONSOLIDATION D001 D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D005 D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D005 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D006 D008 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D007 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D007 DO35 F003 F005

PAINT RAGS PAINT RAGS PAINT RAGS D035 F003 F005



PAINT RAGS PAINT RAGS PAINT RAGS FROM OMD DO35 F005

PAINT RAGS PAINT RAGS PAINT RAGS FROM OMD-90,VR62-40, VPU1-45,AIMD-93 D035 F003 F004

PAINT RAGS PAINT RAGS PAINT RAGS FROM VP10-86 D007 D018 D035 F003 F005

PAINT RAGS PAINT RAGS PAINT REMOVER RAGS D007 D035 F002 F003

PAINT RAGS PAINT RAGS PAINT WASTE RAGS D001 D035

PAINT RAGS PAINT RAGS RAG ACCUMLATION D001 D006 D007 D035

PAINT RAGS PAINT RAGS RAG ACCUMULATION D001 D006 D007 D008 D035

PAINT RAGS PAINT RAGS RAGS D007 D035 F002 F003 F005

PAINT RAGS PAINT RAGS RAGS D035 F003 F004

PAINT RAGS PAINT RAGS SEE ATTACHED D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS SEE ATTACHED D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS SEE DUMP LOG D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS SOLVENT AND PAINT RAGS D035 F003 F005

PAINT RAGS PAINT RAGS STRIPPER WASTE RAGS D007 D035 F002

PAINT RAGS PAINT RAGS USED PAINT RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS USED PAINT RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS VP-8 D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS VP-8 VP-10 D001 D006 D007 D035

PAINT RAGS PAINT RAGS VPU-1, VP-92 D006 D007 D035

PAINT RAGS PAINT RAGS VR-62 SPILL CLEAN-UP D001

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D005 D007 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D005 D007 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D007 D008 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D007 D035 F001 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D007 D035 F002 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D007 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D035 F003 F005

PAINT RAGS PAINT RAGS WASTE PAINT RAGS D001 D006 D007 D035 F003 F005

Page 45




PAINT RAGS PAINT RAGS WASTE PAINT RAGS D006 D007 D035


PAINT RAGS PAINT RAGS WASTE RAGS D007

PAINT RAGS PAINT RAGS WASTE RAGS D007 F002 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D007 D008 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D007 D035 F002 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D007 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D007 F002 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D035 F003 F004

PAINT RAGS PAINT RAGS WASTE RAGS D035 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D035 F005

PAINT RAGS PAINT RAGS WASTE RAGS D001 D006 D007 D035 F003 F005

PAINT RAGS PAINT RAGS WASTE RAGS D006 D007 D035

PAINT RAGS PAINT RAGS WASTE RAGS D001 D006 D007 D035 F003 F005

PAINT RED LAC D001

PAINT REMOVER METHYLENE CHLORIDE 55%, PHENOL (CARBOLIC ACID) 16% D002 D007 F002

PAINT REMOVER PAINT REMOVER D007

PAINT STRIPPER AIRCRAFT PAINT REMOVER D007 F001

PAINT STRIPPER PAINT REMOVER D007

PAINT STRIPPER PAINT STRIPPER DILUTED W/WATER D007

PAINT THINNER PAINT RELATED MATERIAL D001

PAINT THINNER RETOUCHING FLUID, PETROLEUM DISTILLATE, TURPENTINE D001

PAINT THINNER XYLENE, PARAFFINS, AROMATIC COMPOUNDS D001

PAINT THINNER EPOXY MEK, XYLENE, TOLUENE D001 D035

PAINT TRAFFIC METHANOL D001

PAINT WASTE D001

PAINT WASTE D001 D035 F003 F005

PAINT WASTE F005

PAINT WASTE ACETONE, MEK, D001 D035

PAINT WASTE ACETONE, N-BUTYL ALCOHOL, METHYLENE CHLORIDE, MEK, D001 D007 D008 D035 F002 F003

PAINT WASTE BARIUM CHROMATE 25% D001 D007

PAINT WASTE BARIUM, CHROMIUM, LEAD, BENZENE, MEK D001 D003 D005 D007 D008 D018

PAINT WASTE BARIUM, CHROMIUM, METHYLENE CHLORIDE, MEK, D001 D005 D007 D035 F002 F003

PAINT WASTE BENZENE, STRONTIUM CHROMATE, LEAD, MEK, D001 D007 D008 D018 D035

PAINT WASTE CHROMIUM D001 D007

PAINT WASTE CHROMIUM, LEAD, ACETONE, TOLUENE, 1,1,1 TRICHLORO- D001 D007 D008 D018

PAINT WASTE CHROMIUM, METHYLEEN CHLORIDE, ISOCYANATE, PRM D001 D003 D007 D035 F002 F003

PAINT WASTE EPOXY COATING D001 D035 F003 F005

PAINT WASTE INSULATING CMPD, ELECTRICAL D001

PAINT WASTE MEK D001 D035

PAINT WASTE MEK, ACETATE, 1-METHOXY-2-PROPANOL, BUTYL ACETATE D001 D005 D035

PAINT WASTE MEK, BARIUM D001 D005 D035

PAINT WASTE MEK, BENZENE, CADMIUM, LEAD OXIDES, D001 D005 D006 D007 D008 D018

PAINT WASTE MEK, BENZENE, METHYLENE CHLORIDE, CADMIUM D001 D005 D006 D007 D018 D035

PAINT WASTE MEK, BUTYL ACETATE, TOLUENE, XYLENE, N-BUTYL ACET D001 D005 D008 D018 D035

PAINT WASTE MEK, BUTYL ACETATE, TOLUENE, XYLENE, N-BUTYL ACET D001 D005 D008 D035

PAINT WASTE MEK, LEAD, CHROMIUM, XYLENE D001 D007 D008

PAINT WASTE MEK, METHYLENE CHLORIDE, BARIUM, LEAD, BENZENE, D001 D003 D005 D007 D008 D018

Page 46



PAINT WASTE MEK, MIK, TOLUENE, BARIUM, XYLENE, LEAD CHROMATE D001 D005 D007 D008 D035

PAINT WASTE MEK, STRONTIUM CHROMATE, DIISOCYANATOHEXANE D001 D003 D007 D035

PAINT WASTE MEK, STRONTIUM CHROMATE, METHYL BENZENE, D001 D007 D035

PAINT WASTE MEK, TOLUENE, XYLENE D001 D035

PAINT WASTE MEK, XYLENE, TOLUENE, CHROMIUM, ALODINE, D018 D035 D001 D002 D005 D006 D007 D008

PAINT WASTE MEK,MIK, TOLUENE, ETHYL ACETATE, XYLENE, ACETONE, D001 D007 D035 F003 F005

PAINT WASTE METHYL ETHYL KETONE, XYLENE, TOLUENE, CHROMIUM D001 D002 D007 D035

PAINT WASTE METHYL ETHYL KETONE, XYLENE, TOLUENE, CHROMIUM D001 D007 F003 F005 D035

PAINT WASTE MINERAL SPIRITS D001

PAINT WASTE N-BUTYL ALCOHOL, MEK, MIK, TOLUENE, CADIMUM, D001 D006 D007 D035 F003 F005

PAINT WASTE N-BUTYL ALCOHOL, MEK, TOLUENE D001 D035 F003 F005

PAINT WASTE PAINT D001

PAINT WASTE PAINT RELATED MATERIAL D001

PAINT WASTE PAINT PRIMER WASTE (ZINC CHROMATE) D001


PAINT WASTE PAINT RELATED MATERIAL D001 D005 D006 D035

PAINT WASTE PAINT RELATED MATERIAL D001 D005 D007 D008 D035 F001

PAINT WASTE PAINT RELATED MATERIAL D001 D005 D007 D008 D035 F002

PAINT WASTE PAINT RELATED MATERIAL D001 D005 D007 D035 F002 F003

PAINT WASTE PAINT RELATED MATERIAL D001 D007 D008




PAINT WASTE PAINT RELATED MATERIAL D001 D007 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL D001 D007 D035 F003 F005 U080

PAINT WASTE PAINT RELATED MATERIAL D001 D007 D035 F005

PAINT WASTE PAINT RELATED MATERIAL D001 D035 F002 F003 F005

PAINT WASTE PAINT RELATED MATERIAL D001 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL D001 D035 F005

PAINT WASTE PAINT RELATED MATERIAL D001 F003

PAINT WASTE PAINT RELATED MATERIAL D001 F003 F005

PAINT WASTE PAINT RELATED MATERIAL D001 F005


PAINT WASTE PAINT RELATED MATERIAL D006 D007 D008


PAINT WASTE PAINT RELATED MATERIAL D007 D008 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL D007 U080 U188

PAINT WASTE PAINT RELATED MATERIAL D008 F002 D005


PAINT WASTE PAINT RELATED MATERIAL D01 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL F003

PAINT WASTE PAINT RELATED MATERIAL F005

PAINT WASTE PAINT RELATED MATERIAL - FLAMMABLE LIQUID D001 D007 D008 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL - INSULATING VARNISH, ELECT D001

PAINT WASTE PAINT RELATED MATERIAL - PAINT FILTERS D007 D008

PAINT WASTE PAINT RELATED MATERIAL- AEROSOL CANS D001

PAINT WASTE PAINT RELATED MATERIAL -F004;F005 D001

PAINT WASTE PAINT RELATED MATERIAL -F005 D001

PAINT WASTE PAINT RELATED MATERIAL W/ THINNERS D001

Page 47



PAINT WASTE PAINT RELATED MATERIAL, CONTAINING LEAD, CHROMIUM, D001 D007 D008 D035 F003 F005

PAINT WASTE PAINT RELATED MATERIAL, ELCTRICAL VARNISH F005

PAINT WASTE PAINT RELATED MATERIAL, THINNER D001 D003 D007 D035 F002 F003

PAINT WASTE PAINT RELATED MATERIAL-FLAMMABLE LIQUID D001

PAINT WASTE PAINT RELATED MATERIALS D008

PAINT WASTE PAINT REMOVER - METHYLENE CHLORIDE D007 F002 U188

PAINT WASTE PAINT WASET - FILTERS D007

PAINT WASTE PAINT WASTE D001

PAINT WASTE PAINT WASTE D001 D003 D007 D008 D035 F003*

PAINT WASTE PAINT WASTE D001 D003 D007 D035 F003 F005

PAINT WASTE PAINT WASTE D001 D008 D035 F003 F005

PAINT WASTE PAINT WASTE D001 D035 F003 F005

PAINT WASTE PAINT WASTE D001 F003 F005

PAINT WASTE PAINT WASTE F003

PAINT WASTE PAINT WASTE F005

PAINT WASTE PAINT WASTE #3 D001 D035 F003 F005

PAINT WASTE PAINT WASTE, D001

PAINT WASTE PAINT WASTE, MIXED D001

PAINT WASTE PAINT WASTE, SOLID, FILTERS D001

PAINT WASTE PAINT WASTE,TRAFFIC D001

PAINT WASTE PAINT, ENAMEL D001

PAINT WASTE PAINT, EPOXY (PART A) D001

PAINT WASTE PAINT, EPOXY (PART B) D001

PAINT WASTE POLYURETHANE D001

PAINT WASTE PRM & THINNER D001 D007 D035 F003 F005

PAINT WASTE THINNER 23% MEK 8.2% MAPTHA 0.7% ACETONE 5.5% D001 D007 D018 D035 F002 F003

PAINT WASTE THINNER 46.7% PAINT WASTE 53.3% D001 D007 D035 F003 F005

PAINT WASTE THINNER, PRM, WATER D001 D003 D007 D008 D035 F002

PAINT WASTE THINNER, VARNISH, OIL BASE PAINT, LATEX PAINT D001

PAINT WASTE TOLUENE, MEK, STRONTIUM CHROMATE D001 D007 D035

PAINT WASTE TOLUENE, XYLENE, MEK, N-BUTYL ALCOHOL, LEAD, D001 D003 D007 D008 D035 F003

PAINT WASTE XYLENE, TOLUENE, LEAD CHROMATE D001 D007 D008

PAINT WASTE XYLENE, TOLUENE, MEK, ETHYL BENZENE, LEAD CHROMATE D001 D007 D008 D018 D035

PAINT WASTE ZINC CHROMATE, STRONTIUM CHROMATE, CADIMIUM, D001 D005 D006 D007 D008

PAINT WASTE (RAGS) PAINT RAGS PAINT RELATED MATERIAL - RAGS D001

PAINT WASTE - SOLID PAINT RELATED MATERIAL D007 D008

PAINT WASTE - VOID PAINT RELATED MATERIAL - VOID ADDED TO ANOTHER WAS D001

PAINT WASTE (RAGS) PAINT RAGS PAINT RELATED MATERIAL (WASTE RAGS) D007 D008 D035 F003 F005

PAINT WASTE DRIED LEAD CHROMATE D001 D007 D008

PAINT WASTE FILTERS PAINT FILTERS D007

PAINT WASTE RAGS PAINT RAGS CHROMIUM, ACETONE, LEAD D001 D005 D007 D008 D035

PAINT WASTE RAGS PAINT RAGS FOO5, ISOCYANATE, CHROMIUM, ACETONE, ETHYL ACETATE D001 D003 D007 D035 F002 F003

PAINT WASTE RAGS PAINT RAGS ISOCYANATE, CHROMIUM, ACETONE, ETHYL ACETATE D001 D003 D007 D018 D035

PAINT WASTE RAGS PAINT RAGS ISOCYANATE, CHROMIUM, ACETONE, ETHYL ACETATE D001 D003 D007 D035

PAINT WASTE W/LEAD PAINT CHIPS CONTAMINATED WITH LEAD, WASTE CHEESE D008

PAINT WASTE, AEROSO PAINT RELATED MATERIAL D001 D007 F005

PAINT WASTE-AEROSOL AEROSOL PAINT RELATED MATERIAL, AEROSOL CANS, SPENT D001

PAINT WASTE-AEROSOL AEROSOL PAINT RELATED MATERIAL-AEROSOL CANS, SPENT D001

PAINT WASTE-FILTERS PAINT FILTERS PAINT RELATED MATERIAL, FILTERS, SOLID D006 D007 D008

Page 48



PAINT WASTE-FILTERS PAINT FILTERS PAINT RELATED MATERIALS - FILTERS D006 D007 D008

PAINT WASTE-VOID PAINT RELATED MATERIAL D001

PAINT WHITE TOLUENE, XYLENE, D001

PAINT WHITE GLOSS D001

PAINT YELLOW LAC D001

PAINT YELLOW PRIMER D001

PAINT, AEROSOL AEROSOL TOLUENE, ACETONE, XYLENE, METHYLENE CHLORIDE, D001 D035

PAINT, AEROSOL AEROSOL TOLUENE, METHYLENE CHLORIDE, LEAD, PROPANE D001 D008 F002 F005

PAINT, AEROSOLS AEROSOL TOLUENE, XYLENE, MEK, METHYLENE CHLORIDE D001 D035 F002 F003 F005

PAINT, CONCRETE MINERAL SPIRITS 13%; LINSEED OIL 12% D001

PAINT, CONDUCT. COA CONDUCTIVE COATING - FLAT BLACK D001

PAINT, DARK RED SEE ANALYSIS KAL-151&152 D001

PAINT, DRIED LEAD; DRIED PIGMENT D001 D008

PAINT, ENAMEL D001

PAINT, ENAMEL XYLENE, CHROMATE, LEAD CHROMATE, MINERAL SPIRITS D001 D007 D008

PAINT, EPOXY COAT 2 PART KIT D001

PAINT, INSULATING D001

PAINT, OIL BASE BARIUM, LEAD, MEK, FP 70 DEG F D001 D005 D008 D035

PAINT, PART A ISOPROPYL ALCOHOL D001

PAINT, PART A ISOPROPYL ALCOHOL, ZINC CHROMATE D001 D007

PAINT, PART B ISOPROPYL ALCOHOL D001

PAINT, PRIMER ZINC CHROMATE D007

PAINT, PRIMER COAT PART B D001

PAINT, PRIMER COATI MEK <10%; STRONTIUM CHROMATE <15%; TOLUENT <15% D001 D007 D035

PAINT, RED ACRYLIC LEAD CHROMATE <1%; MEK 5% D001 D007 D008 D035

PAINT, RED ENAMEL LEAD DRIER, ALKYD RESIN, MINERAL SPIRITS, ZINC DOO1 DOO8

PAINT, TREE LEAD CHROMATE, MINERAL SPIRITS D001 D007 D008

PAINT, UNK ALUMINUM SEE ANALYSIS DCM-159 D001

PAINT, UNK WHITE SEE ANALYSIS DCM-158 D001

PAINT, UNK YELLOW SEE ANALYSIS DCM-160 D001 D008

PAINT, VARNISH XYLENE 24%, TOLUENE DIISOCYANATE 5%, D001 F003

PAINT, WASTE D001

PAINT, WASTE BARIUM, MEK, TOLUENE, XYLENE, LEAD, CADIMIUM, D001 D005 D006 D007 D008 D035

PAINT, WASTE BARIUM, TOLUENE, XYLENE, LEAD, METHANOL, ETHANOL, D001 D005 D007 D008

PAINT, WASTE LEAD CHROMATE, MEK D001 D007 D008 D035

PAINT, WASTE ZINC CHROMATE, LEAD, MIK D001 D007 D008 D035

PAINT,ENAMEL MID CHROME YELLOW 25%; LEAD NAPTHENATE <5% D001 D008

PAINT,ENAMEL PART A LEAD CHROMATE D001 D007 D008

PAINTS AEROSOL AEROSOL AEROSOL PAINTS D001 D007 D008 D035

PAPER DRY SILVER PHOTO PAPER D009 D011

PAPER MICORFICHE COPY PAPER D009

PCB 12 GAL 10 KVA #2643-1-7 303 LBS 92PPM 321-0002 M002

PCB BALLAST 5EA M002

PCB BALLAST FROM OLD HEATING PLANT M002

PCB COMMISARY RENOVATION M002

PCB LIGHTING CHANGEOUT MA99

PCB LIGHTING CHANGEOUT AT MARINE RESERVES MA99

PCB PCB BALLAST M002

PCB PCB BALLAST MOO2

Page 49



PCB PCB BALLASTS M002

PCB PCB LIGHT BALLASTS M002

PCB PCB OIL FROM PW SHOPS M002

PCB PCB SAMPLES M002

PCB PCB SWITCH M002

PCB PCB TRANSFORMER M002

PCB PCB TRANSFORMER 66 PPM M002

PCB PCB TRANSFORMER 66PPM M002

PCB PCB TRANSFORMER S/N C666213, S/N 2643-5-6 M002

PCB SUSPECT PCB BALLASTS M002

PCB BALLASTS PCB BALLASTS M002

PCB BALLASTS PCB BALLASTS (603/202/160/133/151#) M002

PCB CAPACITOR PCB CAPACITOR S19247 M002

PCB CAPACITORS PCB CAPACITORS & LIGHT BALLAST M002

PCB CONTAM. DEBRIS PCB CONTAMINATED DEBRIS M002

PCB DEBRIS LIGHT BALLASTS, CONTAMINATED W/ PCBS M002

PCB DEBRIS PCB DEBRIS, CONTAMINATED W/ PCBS M002

PCB OIL OIL FROM TRANSFORMER >39PPM NOW 100 PPM M002 MA02

PCB OIL PCB OIL FROM O CLUB PARKING LOT TX M002

PCB SOIL PCB CONTAMINATED SOIL FROM O CLUB MOO2 BOO7

PCB SOIL PCB SOIL FROM TRANSFORMER OIL SPILL M002

PCB TRANSFORMER PCB TRANSFORMER M002

PCB TRANSFORMER POLYCHLORINATED BIPHENYLS (PCBS) M002

PCB TRANSFORMER SER #2643-10 M002

PCB TRANSFORMER SER #2643-2-15 M002

PCB TRANSFORMER SER #2643-2-17 M002



PCB TRANSFORMER SER #B539647 M002

PCB TRANSFORMER SER #B539648 M002

PCBS-TRANSFORMER TRANSFORMER CONTAINING PCBS M002

PD 680 PD 680 D001

PD 680 CONTAMINATED D001

PD 680,CONTAM. PD 680, CONTAMINATED D001

PD 680,CONTAM. PD 680,CONTAMINATED W/OILS, GREASES (2%) D001

PD-680 D001

PD-680 PD-680 D001

PD-680 PD-680 D011

PD-680 PD-680, CONTAMINATED D001

PD-680 PD-680, DRY-CLEANING SOLVENT D001

PD-680 CONTAMINATED D001

PD-680 CONTAMINATED PETROLEUM DISTILLATE, NOS D001

PD-680 FROM WC430 PD-680 FROM WC430 D006 D010

PD-680, CONTAM. PD-680, CONTAMINATED D001

PD-680, CONTAM. PD-680, CONTAMINATED W/ GREASES & OILS D001

PD-680, CONTAM. PD-680, CONTAMINATED W/ OILS & GREASE D001

PD-680, CONTAM. PD-680, CONTAMINATED W/ SOLVENTS D001

PENETRATING OIL PENETRATING OIL D001

PESTICIDE INSECTICIDE D001

Page 50



PESTICIDE ORTHO INSECTICIDE D001

PESTICIDE ORTHO ISOTOX INSECT SPRAY D001

PESTICIDE PESTICIDE D002

PESTICIDE PESTICIDE F002

PESTICIDE PESTICIDE AND WATER D001

PESTICIDE 2,4,5-T 2,4,5-T/SILVEX DIOXIN PESTICIDES F027

PETROLEUM NAPHTHA PETROLEUM NAPHTHA D001

PETROLEUM NAPTHA PETROLEUM NAPTHA D001

PETTCOTE 30 FINISH PETROLEUM DISTILLATES D001

PHENOL PHENOL D001

PHOTO PHOTO WASTE D011

PHOTO SILVER D011

PHOTO SILVER NITRATE D011

PHOTO BLEACH D011

PHOTO CHEM. SPILL SILVER RECOVERY SOLUTION & SPEEDYDRY D011

PHOTO CHEMISTRY PHOTO CHEMISTRY (XP1) 1 OF 5 PARTS D002

PHOTO CLEANER PHOTOGRAPHIC CLEANER, SPENT D007 D007

PHOTO DEVELOPER DEVLOPER D011

PHOTO FIXATIVE PHOTO FIXATIVE D011

PHOTO FIXATIVE PHOTO FIXATIVE W/ HIGH LEVEL OF SILVER D011

PHOTO FIXATIVE PHOTO FIXATIVE W/ SILVER D011

PHOTO FIXATIVE PHOTO FIXATIVE, BLACK /WHITE, SPENT D011

PHOTO FIXATIVE PHOTO FIXATIVE, COLOR, SPENT D011

PHOTO FIXATIVE PHOTO FIXATIVE, SPENT D011

PHOTO FIXATIVE PHOTO FIXATIVE, SPENT W/ SILVER D011

PHOTO FIXATIVE PHOTO FIXATIVE,CONTAMINATED WITH SILVER D011

PHOTO FIXATIVE PHOTOGRAPHIC WASTE D011

PHOTO FIXATIVE PHOTOGRAPHIC WASTES D011

PHOTO FIXATIVE PHOTOGRAPHIC WASTES, SPENT D011

PHOTO FIXER D011

PHOTO FIXER PHOTO FIXER D011

PHOTO FIXER PHOTO FIXER /STABLIZER D011

PHOTO FIXER PHOTO FIXER BLEACH D011

PHOTO FIXER B/W PHOTO FIXER BLACK/WHITE D011

PHOTO FIXER WASTE SILVER + FIXER D011

PHOTO FIXER, X-RAY SILVER, ACETIC ACID, SODIUM ACETATE D011

PHOTO PAPER PHOTOGRAPHIC PAPER D011

PHOTO SYSTEM CLEANR CHROMIUM; SULFERIC ACID; SULFAMIC ACID; WATER D002 D007

PHOTO SYSTEM CLEANR POTASSIUM DICHROMATE, SULFAMIC ACID D007

PHOTO WASTE 2-55 GAL/1-15 GAL D011

PHOTO WASTE PHOTO FIXATIVE D011

PHOTO WASTE PHOTO OR X-RAY FIXATIVE W/ SILVER D011

PHOTO WASTE PHOTO OR X-RAY FIXATIVE W/SILVER D011

PHOTO WASTE PHOTO WASTE D011

PHOTO WASTE PHOTOGRAPHIC WASTE D002

PHOTO WASTE PHOTOGRAPHIC WASTE D011

PHOTO WASTE X-RAY FIXATIVE, CONTAINING EXCESS SILVER D011

PHOTO WASTE XR-DEVELOPER-REPL (PART B) - PHOTO WASTE D002

PHOTO WASTE, SILVER SILVER D011

Page 51



PHOTOGRAPHIC FILM SILVER 1-5% D011

PLASTI DIP PLASTI DIP D001

PLASTIC BLAST MEDIA BLAST MEDIA PLASTIC BLAST BEAD MEDIA, CONTAMINATED D007

PLASTIC BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA, SPENT D006 D007

PLASTIC BLAST MEDIA BLAST MEDIA PLASTIC BLAST MEDIA, SPENT D006 D007 D008

PLASTIC MOLDING ISOCYANATE D003 F002

PLASTIC POLISH PETROLEUM HYDROCARBONS D001

POLISH GYM FINISH D001

POLISH METAL POLISH D001

POLISH PLASTIC POLISH D001

POLISH PLASTIC POLISH DOO1

POLISH AUTO POLISH, AUTO D001

POLISH LIQUID POLISH LIQUID D001

POLISH REMOVER FLOOR POLISH REMOVER D002

POLISH REMOVER SODIUM HYDROXIDE D002

POLISH, AUTOMOTIVE D001

POLISH, PLASTIC MINERAL SPIRITS D001

POLISH, PLASTIC PLASTIC POLISH D001

POLISH, REMOVER PH>13 D002

POLY COAT PART A METHYL ETHYL KETONE, ETHYL ACETATE, ETHYL BENZENE, D001 FOO3 F005 D035

POLY COAT PART B METHYL ETHYL KETONE, XYLENE, TOLUENE, DIISOCYNATE, D001 D003 F003 F005 D035

POLYAMIDE PAINT "A" BARIUM CHROMATE, 2-BUTOXYETHANOL, CS&10 AROMATIC D001 D007

POLYAMIDE RESIN B TOLUENE, ISOBUTANOL, MEK D001 D035 F005

POLYESTER RESIN RESIN, STYRENE D001

POLYURETHANE D001 D035 F003 F005

POLYURETHANE D001 F005

POLYURETHANE 2-BUTANOL, 2-ETHOXYETHYL ACETATE D001

POLYURETHANE STODDARD SOLVENT D001

POLYURETHANE XYLENE, ETHYLENE GLYCOL, MINERAL SPIRITS D001

POLYURETHANE COATIN D001 D035 F003 F005

POLYURETHANE COATIN MEK 10%, ETHYL ACETATE 11%, CELLOSOLVE ACETATE 20% D001 D035 F005

POLYURETHANE COATIN MEK 10%, MIK 11.5%, XYLENE 5%, CELLUOSOLVE 11% D001 D035 F003 F005

POLYURETHANE COATIN MEK 5-10%, XYLENE 35-40%, POLYURETHANE 40-45% D001 F003

POTASSIUM POTASSIUM DICHROMATE TECH D007

POTASSIUM CHLORATE 4000 GM POTASSIUM CHLORATE D001

POTASSIUM CHLORATE DOG TRAINING D001

POTASSIUM CHLORATE EXPIRED POTASSIUM CHLORATE D001

POTASSIUM CHLORATE EXPIRED SODIUM CHLORATE D001



POTASSIUM CHLORATE POTASSIUM CHLORATE FROM KENNEL D001

POTASSIUM CHLORATE TEST KIT FROM DOG HANDLERS D001

POTASSIUM CHLORATE TESTING BOMB DOG D001

POTASSIUM CHLORIDE POTASSIUM CHLORIDE D001

POTASSIUM CYANIDE WASTE POTASSIUM CYANIDE D003 P068

POTASSIUM DICHROMAT POTASSIUM DICHROMATE D001 D007

POTASSIUM DICHROMAT POTASSIUM DICHROMATE D003 D007

POTASSIUM DICHROMAT POTASSIUM DICHROMATE, OVER-AGED D003

POTASSIUM HYDROXIDE MEDICAL D002

Page 52



POTASSIUM HYDROXIDE POTASSIUM HYDROXIDE D002

POTASSIUM HYDROXIDE POTASSIUM HYDROXIDE ELECTROLYTE D002

POTASSIUM PERMAGANT POTASSIUM PERMAGANATE D001

POWER PAK AEROSOL AEROSOL POWER PAK AEROSOL CONTAINING CFCS F002

PRIME COAT NAPTHA, TOLUENE, N-BUTYL ALCOHOL D001

PRIMER MEK, ACDTONE, METHANOL, CHROMATE, D001 D007 D035 F003 F005

PRIMER COATING SOLVENTS D001

PRIMER COATING -A TOLUENE MEK CHROMIUM ETHANOL METHYL ETHER D001 D007 D035 F005

PRIMER COATING -B TOLUENE D001 F005

PRIMER COATING YEL CHROMIUM, LEAD, BENZENE, METHYLENE CHLORIDE, D001 D007 D008 D018

PRIMER PRE TREAT D002

PRO SEAL ADHESIVE PART A D001

PRO SEAL ADHESIVE PART A F005

PRO SEAL ADHESIVE PART A & B D001

PRO SEAL ADHESIVE PART B D001

PROSEAL 870 PART A MAGNESIUM DICHROMATE, MANGANESE DIOXIDE, D007

PROSEAL 870 PART A TOLUENE, PHENOL POLYMER WITH FORMALDEHYDE D001

PROSEAL 870 PART B MEK, TOLUENE, RESIN D035

PRO-SEAL PART A METHYL BENZENE D001

PRO-SEAL PART B MAGNESIUM CHROMATE D007

PUTTY ZINC CHROMATE PUTTY D007

PUTTY, ZINC CHR ZINC CHROMATE D007

RAGS PAINT RAGS JP-8 CONTAMINATED MATS AND RAGS AND SPEEDY DRY D018

RAGS PAINT RAGS OIL AND FUEL SOAKED FUEL SPILL DEBRIS D001

RAGS PAINT RAGS OILY RAGS FROM MRCR TOPSHAM D005

RAGS PAINT RAGS PAINT RAGS D035 F003 F005

RAGS PAINT RAGS PAINT RAGS DO35

RAGS PAINT RAGS PAINT THINNER SOILED RAGS D005 D035 F003 F005

RAGS PAINT RAGS PAINT WASTE RAGS D005 D007 D035 F003 F005

RAGS PAINT RAGS PAINT WASTE RAGS D007 D035 F002 F003 F005

RAGS PAINT RAGS PAINT WASTE RAGS D035

RAGS PAINT RAGS RAGS AND SPEEDY DRY D007 D035 F003 F005

RAGS PAINT RAGS SAFETY KLEEN BLDG 339 D005

RAGS PAINT RAGS USED RAGS FROM MARINE RESERVE TOPSHAM D005

RAGS PAINT RAGS WASTE PAINT RAGS D005 D007 D035

RAGS PAINT RAGS WASTE PAINT RAGS D007 D018 D035

RAGS PAINT RAGS WASTE PAINT RAGS D007 D035 F003 F005

RAGS PAINT RAGS WASTE PAINT RAGS D035

RAGS PAINT RAGS WASTE RAGS D005 D007 D008 D035

RAGS PAINT RAGS WASTE RAGS D005 D007 D018 D035

RAGS PAINT RAGS WASTE RAGS D005 D007 D035

RAGS PAINT RAGS WASTE RAGS D005 D008 D035 F003 F005

RAGS PAINT RAGS WASTE RAGS D005 D035

RAGS PAINT RAGS WASTE RAGS D007

RAGS PAINT RAGS WASTE RAGS D007 D008 D035


RAGS PAINT RAGS WASTE RAGS D007 D035 F003 F005

RAGS PAINT RAGS WASTE RAGS D018


Page 53



RAGS PAINT RAGS WASTE RAGS D035 F002 F003

RAGS PAINT RAGS WASTE RAGS D035 F003 F005

RAGS PAINT RAGS WASTE RAGS D035 FOO3

RAGS SOLVENT PAINT RAGS GUN CLEANING RAGS FROM MARINES D005

RAGS W/ PAINTS & TH PAINT RAGS RAGS, SATURATED W/ PAINTS AND THINNERS D007 D008 D035 F003 F005

RAGS, CONTAM W/SOLV PAINT RAGS RAGS, CONTAMINATED W/ SOLVENTS F001 F003

RAIN COATING KIT PAINT ETHYL BENZENE <10%, XYLENE 10-20%, TOLUENE D001 D003 F003

RAIN COATING KIT PAINT MEK <10%, TOLUENE <10%, BUTYL ACETATE <10% D001 D035 F005

RAIN EROSION RESIS RESIN RAIN EROSION RESISTENT KIT D001

RAIN EROSION RESIS RESIN RAIN EROSION RESISTENT KIT D001 F003

RAIN EROSION RESIST RESIN RAIN EROSION RESISTENT KIT D001

RAIN EROSION RESIST RESIN RAIN EROSION RESISTENT KIT D001 F003

RCRA CLOSURE RCRA CLOSURE - FINAL RINSATE (SILVER RECOVERY, F003 F005

RCRA CLOSURE RCRA CLOSURE - QUONSET HUT ASPHALT FLOOR D008

REDUCER REDUCER REDUCER D001 D035

RESIN RESIN ISOPROPYL ALCOHOL, POLYAMIDE RESIN D001

RESIN POLYESTER RESIN RESIN POLYESTER D001

RESIN, POLYESTER RESIN FLAMMABLE D001

RESMETHRIN RESIN D TRANS ALLETHRIN RESMETHRIN D001

ROOF COATING CMPD PAINT ROOF COATING COMPOUND - COMBUSTIBLE LIQUID D001

RUBBER COMPOUND PAINT CHROMIUM D007

RUBBER COMPOUND PAINT TOLUENE, MEK, CHROMIUM D001 D007 D035 F005

RUG SHAMPOO SOAP 2-BUTOXYETHANOL, ISOPROPYL ALCOHOL, PETROLEUM D001

RUST ELIMINATOR ACID CONSOLIDATED INTO #823 D002

RUST PREVENT COMP ACID CHROMIC ACID, SODIUM FLUASILCATE D002 D007

RUST PREVENTATIVE SOLVENT STODDARD SOLVENT, PETROLEUM DISTILATES D001

SALICYLIC ACID ACID SALICYLIC ACID AND LACTIC ACID D001 D002

SAND BLAST MEDIA BLAST MEDIA SAND BLAST MEDIA, CONTAMINATED W/ METALS D006

SCALE REMOVER ACID PHOSPHORIC ACID D002

SCRAP AMALGAM D009

SEALANT D001

SEALANT MEK, CHROMIUM D001 D007 D035

SEALANT SEALANT D001

SEALANT SEALING COMPOUND U226

SEALANT- "A" SEALANT- PART A D006

SEALANT -"A" SEALANT - PART A D001

SEALANT (PART A) D006

SEALANT PART A LEAD OXIDE D008

SEALANT PART A TOLUENE D001

SEALANT PART B MAGNESIUM CHROMATE D007

SEALANT TOPCOAT SEALANT TOP COAT F005

SEALER, ADHESIVE SEALER, ADHESIVE D001

SEALING CMPD D001

SEALING CMPD TOLUENE D001

SEALING CMPD PART B SEALING COMPOUND ADHESIVE PART B F005

SEALING CMPD PT B CHROMIUM D007

SEALING CMPD, PAINT MEK 50%, 2-PROPANOL 15%, MIK (HEXONE) 10% D001 D035 F003 F005

SEALING COM PART B CALCIUM DICHROMATE, TOLUENE, MIXED RESINS D007

SEALING COMP PART A TOLUENE, PHENOL POLYMER WITH FORMALDEHYDE, D001

Page 54



SEALING COMP PART B MAGNESIUM CHROMATE, 1,3 DIPHENYL GUANADINE, D007

SEALING COMPOUND D001

SEALING COMPOUND D001 F003

SEALING COMPOUND D007

SEALING COMPOUND D035 F005

SEALING COMPOUND CHROMIUM D007

SEALING COMPOUND CHROMIUM 25%; MEK <5% D007 D035

SEALING COMPOUND CHROMIUM, MEK D001 D007 D035

SEALING COMPOUND CHROMIUM, MEK D001 D007 D035 F005

SEALING COMPOUND LEAD D008

SEALING COMPOUND LEAD DIOXIDE D008

SEALING COMPOUND MAGNESIUM DICHROMATE, CALCIUM DICHROMATE MEK D001 D007 D035

SEALING COMPOUND MEK D001 D035

SEALING COMPOUND MEK, D001 D035

SEALING COMPOUND MEK, PHENOLIC D001 D035

SEALING COMPOUND MEK, PHENOLIC D001 D035 F005

SEALING COMPOUND SEALING COMPOPUND D001 D007 D035 F005

SEALING COMPOUND SEALING COMPOUND D001

SEALING COMPOUND SEALING COMPOUND D001 D007 D035 F005

SEALING COMPOUND SEALING COMPOUND D001 D007 F005

SEALING COMPOUND SEALING COMPOUND D001 F003

SEALING COMPOUND SEALING COMPOUND D001 F005

SEALING COMPOUND SEALING COMPOUND D008

SEALING COMPOUND SEALING COMPOUND F005

SEALING COMPOUND SEALING COMPOUND, SPENT D001 F003

SEALING COMPOUND SEALING COMPOUND, SPENT D001 F005

SEALING COMPOUND TOLUENE D001

SEALING COMPOUND TOLUENE D001 F005

SEALING COMPOUND TOLUENE F005

SEALING COMPOUND- TOLUENE, PART A D001 F005

SEALING COMPOUND A METHYL BENZENE D001 D018

SEALING COMPOUND A TOLUENE, MEK D035

SEALING COMPOUND -A CHROMIUM D001 D007 D035 F005

SEALING COMPOUND B CALCIUM DICHROMATE D007

SEALING COMPOUND B MAGNESIUM CHROMATE D007

SEALING COMPOUND-B CHROMIUM D007

SELENIUM STANDARD SELENIUM STANDARD D002 D010

SEWER CLEANER SEWER CLEANER - SODIUM HYDROXIDE D002

SILICONE ADHESIVE D001

SILVER AMALGAM D009

SILVER DRY SILVER PAPER D011

SILVER NITRATE SIVLER NITRATE 75%; POTASSIUM NITRATE 25% D001

SILVER RECOVERY SOL SILVER RECOVERY SOLUTION D011

SILVER STANDARD SILVER STANDARD D002 D011

SLUDGE BLDG 225 PARTS WASHER D006

SLUDGE JET WASHER SLUDGE FROM GSE D008

SLUDGE SLUDGE & WATER MA01

SLUDGE SLUDGE FROM JET WASH D006

SO SURE ENAMEL TOLUENE, ACETONE, D001

Page 55



SO SURE LACQUER TOLUENE, XYLENE, ACETONE D001

SODIUM CHLORATE 1000 GM SODIUM CHLORAT D001

SODIUM CHLORATE DOG TRAINING D001

SODIUM CHLORATE EXPIRED SODIUM CHLORATE D001

SODIUM CHLORATE EXPIRED SODIUM CHLORATE D001



SODIUM CHLORATE SODIUM CHLORATE FROM KENNEL D001

SODIUM CHLORATE TEST KIT FOR BOMB DOGS D001

SODIUM CHLORATE TESTING BOMB DOG D001

SODIUM DICHROMATE SODIUM DICHROMATE D001 D007

SODIUM HYDROXIDE SODIUM HYDROXIDE D002

SODIUM HYDROXIDE SODIUM HYDROXIDE D002

SODIUM HYDROXIDE SODIUM HYDROXIDE, IMPURITIES D002

SODIUM HYDROXIDE TREATMENT PLANT LEAK D002

SODIUM HYDROXIDE SO SODIUM HYDROXIDE SOLUTION D002

SODIUM HYPOCHLORITE SODIUM HYPOCHLORITE SOLUTION D002

SODIUM SULFIDE SODIUM SULFIDE MARKED 7% FROM MEDICAL D002

SOLDER USED SOLDER D008

SOLDER WASTE SOLDER D008

SOLDERING FLUX SOLDERING FLUX D001

SOLDERING FLUX SOLDERING FLUX D002

SOLDERING FLUX WHITE ROSIN FLUX D001

SOLVENT B&B WASH UNUSED B&B CLEANER D010

SOLVENT SOLVENT 111 TRICHLOROETHANE U226

SOLVENT SOLVENT 1-1-1-TRICLOROETHANE F002

SOLVENT SOLVENT ANALYSIS D001 D006 D007

SOLVENT SOLVENT ANALYSIS 73-008DD PARTS WASHER D006

SOLVENT SOLVENT BLDG 8 SAFETY KLEEN SOLVENT D006

SOLVENT SOLVENT BTKXZ ANALYSIS 6311N D001 D006 D007

SOLVENT SOLVENT CARBON REMOVING COMPOUND D007 F002

SOLVENT SOLVENT CLEANING COMPOUND D001 D035

SOLVENT SOLVENT CONTAMINATED ACETONE D001 F003

SOLVENT SOLVENT CONTAMINATED WASTE OIL F002 F003

SOLVENT SOLVENT CORROSION PREVENTATIVE COMPOUND D005

SOLVENT SOLVENT CORROSION PREVENTIVE D001

SOLVENT SOLVENT CRX ENVIROSOL D001 D006 D007

SOLVENT SOLVENT CRX ENVIROSOL D006 D007

SOLVENT SOLVENT DETERGENT FROM 51E TIRE SHOP D006

SOLVENT SOLVENT DRY CLEANING SOLVENT D001

SOLVENT SOLVENT ENVIROSOL CRX W/C 400 D006 D007

SOLVENT SOLVENT ENVIROSOLV D001 D006 D007

SOLVENT SOLVENT ENVIROSOLV D002

SOLVENT SOLVENT ENVIROSOLV CRX AND WATER FROM PARTS WASHER D006 D007

SOLVENT SOLVENT ENVIROSOLV FROM DIV 400 D001 D006 D007

SOLVENT SOLVENT ENVIROSOLV FROM W/C HOD #9 D006

SOLVENT SOLVENT ENVIROSOLV FROM WC 400 D001 D006 D007

SOLVENT SOLVENT ENVIROSOLVE FROM WC520 D001 D006 D007

SOLVENT SOLVENT ENVIROSOLVE FROM WC520 D001 D006 D007

Page 56



SOLVENT SOLVENT EXPIRED SOLVENT D001

SOLVENT SOLVENT EXPIRED SOLVENT D001 U002

SOLVENT SOLVENT FROM BETTER ENGINEERING MACHINE CONSOLIDATED INTO #798

SOLVENT SOLVENT HALOGENATED SOLVENT F002

SOLVENT SOLVENT HALOGENATED WASTE DRUM D001 F002

SOLVENT SOLVENT HAZMAT D039

SOLVENT SOLVENT HOBBY SHOP SOLVENT D001 D006 D008 D035 D040

SOLVENT SOLVENT HOBBY SHOP SOLVENT D008 D018 D039 D040

SOLVENT SOLVENT JET WASHER SLUDGE FROM PROP SHOP D006

SOLVENT SOLVENT LUBRICANT SOLID FILM AIR DRYING D001 D008 D035

SOLVENT SOLVENT MINERAL SPIRITS D001

SOLVENT SOLVENT NON HALOGENATED SOLVENT D001 D035 F003 F005

SOLVENT SOLVENT NON HALOGENATED SOLVENT MA01

SOLVENT SOLVENT NONHAL SOLVENT D001 D006 D007 D035 F002 F003 F005

SOLVENT SOLVENT NON-HAL SOLVENT D001 D005 D035 F003 F005

SOLVENT SOLVENT NON-HALOGENATED SOLVENT D001

SOLVENT SOLVENT NON-HALOGENATED SOLVENT D001 D035 F002 F003 F005

SOLVENT SOLVENT NON-HALOGENATED SOLVENT D001 D035 F003 F005

SOLVENT SOLVENT NON-HALOGENATED SOLVENT D001 F002

SOLVENT SOLVENT OIL & WATER FROM BLDG 337 TOPSHAM F003 F005

SOLVENT SOLVENT PAINT THINNER D001 D018 D035

SOLVENT SOLVENT PARTS WASH AT WC414 PROP SHOP D008

SOLVENT SOLVENT PARTS WASHER 51E TIRE SHOP D006

SOLVENT SOLVENT PD 680 FROM WC 430 D001 D006

SOLVENT SOLVENT PD 680 FROM WC 430 D006

SOLVENT SOLVENT PD-680 FROM BEARING CLEANER WC/411 D001

SOLVENT SOLVENT PD680 FROM PARTS WASHER D006

SOLVENT SOLVENT PD-680 FROM PARTS WASHER 730 D006 D007 D008 D011

SOLVENT SOLVENT PD-680 FROM W/C 411 D001

SOLVENT SOLVENT PD-680 FROM W/C 430 D006 D007

SOLVENT SOLVENT PD680 FROM W/C 730 D006 D007 D008 D011

SOLVENT SOLVENT PD680 MIXED WITH COSMOLINE D006

SOLVENT SOLVENT PD-680 WASTE FROM WASHER INW/C 411 D001

SOLVENT SOLVENT PF DEGREASER BLDG 86 #17 D006

SOLVENT SOLVENT PRECISION CLEANING AGENT F002

SOLVENT SOLVENT PUBLIC WORKS SOLVENT MA01

SOLVENT SOLVENT SAFETY KLEEN D001 D006 D008 D018 D035 D039

SOLVENT SOLVENT SAFETY KLEEN BLDG 635 D001 D018 D039

SOLVENT SOLVENT SAFETY KLEEN CHANGE OUT D007 D008

SOLVENT SOLVENT SAFETY KLEEN NEX SERVICE STATION D008 D018 D039

SOLVENT SOLVENT SAFETY KLEEN NEX SERVICE STATION D039 D040

SOLVENT SOLVENT SERVICE STATION SOLVENT D001 D006 D008 D035 D040

SOLVENT SOLVENT SERVICE STATION SOLVENT D001 D018 D039 D040

SOLVENT SOLVENT SERVICE STATION SOLVENT D006 D039

SOLVENT SOLVENT SOLVENT D039

SOLVENT SOLVENT SOLVENT CHANGEOUT D001 D018 D039

SOLVENT SOLVENT SOLVENT CHANGEOUT D001 D018 D039 D040

SOLVENT SOLVENT SOLVENT CHANGEOUT D039

SOLVENT SOLVENT SOLVENT CHANGEOUT/REMOVAL D039

Page 57



SOLVENT SOLVENT SOLVENT FROM CPW5 IN BOTTLE LABELED WASH UP D001

SOLVENT SOLVENT SOLVENT FROM WC 430 D001 D006 D007

SOLVENT SOLVENT SOLVENT PARTS WASHER 51E D006

SOLVENT SOLVENT SOLVENT TANK CHANGEOUT D001 D006 D008 D018 D039 D040

SOLVENT SOLVENT SOLVENT TANK REMOVAL FROM RMCB27 D001 D018 D039 D040

SOLVENT SOLVENT SPRAY WASHER WASTE 900 DIVISION D008

SOLVENT SOLVENT STEAM PLANT D002

SOLVENT SOLVENT TEKSOL AND PD 680 D001

SOLVENT SOLVENT TEKSOL SOLVENT D001

SOLVENT SOLVENT TURPENTINE D001

SOLVENT SOLVENT WASHER WASTE FROM W/C 51E D006

SOLVENT SOLVENT WASTE BRAKE CLEANER FROM HOBBY SHOP D001

SOLVENT SOLVENT WASTE ENVIROSOLV TANK 9 D006

SOLVENT SOLVENT WC51E BOLT WASHER D006

SOLVENT SOLVENT halogenated HALOGENATED SOLVENT D001 F001

SOLVENT SOLVENT HALOGENATED HALOGENATED SOLVENTS D001 D005 F002

SOLVENT SOLVENT halogenated HALOGENATED WASTE D001

SOLVENT SOLVENT HALOGENATED HALOGENATED WASTE F002

SOLVENT SOLVENT HALOGENATED TRICHCLOROETHANE 100% D040

SOLVENT SOLVENT HALOGENATED TRICHLOROETHANE F001 F002

SOLVENT SOLVENT HALOGENATED TRICHLOROTRIFLUOROETHANE CLEANER F002

SOLVENT DEGREASER SOLVENT DEGREASER F002

SOLVENT HALO 1 1 1 TRICH F001 F002

SOLVENT HALO 1 1 1 TRICH U226

SOLVENT HALO FREON HCFC-141 F001

SOLVENT NON-HAL 51E PARTS WASHER D006

SOLVENT NON-HAL BLDG 555 OIL WATER SEPARATOR D027 D035

SOLVENT NON-HAL DRY CLEANING SOLVENT D001

SOLVENT NON-HAL ENVIROSOLV CRX WASTE FROM 520/400 D006

SOLVENT NON-HAL ENVIROSOLVE CRX D006 D018 F003 F005

SOLVENT NON-HAL HOBBY SHOP OIL AND WATER SEPARATOR F003

SOLVENT NON-HAL MARINE RESERVE LIFT SUMP F001 F003

SOLVENT NON-HAL NON HALOGENATED SOLVENT PD 680 TYPE II D006

SOLVENT NON-HAL NON HALOGENATED SOLVENTS D001

SOLVENT NON-HAL NON-HALOGENATED SOLVENT WASTE D001

SOLVENT NON-HAL PD-680 WASTE FROM PARTS WASHER #11 BLDG 250/400DIV D006

SOLVENT NON-HAL PD-680 WITH FLASH POINT LESS THAN 140DEGREES D001

SOLVENT NON-HAL PF DEGREASER 900 DIV PARTS WASHER D006

SOLVENT NON-HAL SOLVENT D001 D006 D008 D035 D040

SOLVENT NON-HAL SOLVENT DOO1 D006 D008 D035 D040

SOLVENT NON-HAL SOLVENT F005

SOLVENT NON-HAL STEELE COTE SOLVENT D001

SOLVENT NON-HAL USED SOLVENT D001 D018 D035 F003

SOLVENT NON-HAL WASTE ACETONE D001

SOLVENT NON-HAL WASTE FROM 51E JET SPRAY WASHER #30 D006

SPILL DEBRIS RAGS, SOAKED W/ JP-5, COMBUSTIBLE D001

SPILL DEBRIS SPILL DEBRIS D011

SPILL DEBRIS SPILL DEBRIS D018

SPILL DEBRIS FUEL ABSORBANT BOOMS ETHYLENE GLYCOL, KEROSENE, #2 FUEL D001

Page 58



SPILL DROSS SPILL RESIDUE JP-5 SPEEDY DRY D001

SPILL RESIDUE D001

SPLICING CEMENT HEXANE, TOLUENE, XYLENE, N-BUTYL ACETATE, D001

SPRAY KIT AEROSOL SPRAY KIT D001

SPRAY KIT MEK, 1,1,1 TRICHLOROETHANE, ACETONE, XYLENE D001 D035

STAIN REMOVER STAIN REMOVER D002

STAIN, MAPLE MINERAL SPIRITS D001

STANDARD BOILER PLANT PRODUCT D002

STENCIL CORR. FLUID STENCIL CORRECTION FLUID D001 F003

STRIPPER PROTECTIVE COATING D002

STRIPPER SALVATION D002

SULFURIC ACID SULFURIC ACID D002

SULFURIC ACID, SPEN SULFURIC ACID, PH 0.5 (FIELD TEST); LEAD D002 D008

SUPER AGITENE CLEAN D001

SYSTEMS CLEANER PHOTO SYSTEMS CLEANER, SPENT D007

SYTEMS CLEANER, EXC PHOTO SYSTEMS CLEANER, EXCESS D007

TANK CARCASS DENTAL TANK CARCASS D009 D011

TECH PETROLATUM D001

TEST KIT ACID TEST KIT D001

THINNER XYLENE, N-BUTYL ALCOHOL, ISOPROPYL ALCOHOL D001 F003

THINNER XYLENE, TOLUENE, MEK, --BUTYL ACETATE, OXOHEXYL D001 D035 F003 F005

THINNER A/C COATING MEK, MIK D001 D035

THINNER PAINT WASTE THINNER PAINT WASTE D001

THINNER, A/C COATIN XYLENE, TOLUENE, MEK, N-BUTYL ACETATE, ACETATE D001 D035 F003 F005

THINNER, PAINT TOLUENE, MEK, PAINT RELATED MATERIAL D001 D035 F005

THINNERS C23 SOLVEN THINNERS C23 SOLVENTS F003

TOLUENE TOLUENE D001 U220

TOLUENE TOLUENE U220

TOLUENE TOLUENE, SPENT D001

TOLUENE MIBK MIX TOLUENE, METHYLISOBUTYLKETONE D001

TONER TONER MITA TONER D006

TONER TONER TONER D001

TONER TONER TONER D007

TONER TONER TONER AND DISPERSAN D001

TONER TONER TONER AND DISPERSANT D001

TONER TONER TONER CARTRIDGES D007

TONER TONER TONER INDIRECT ELEC D001

TONER, COPY TONER D001

TONER, RICOH TONER NAPTHA, RESIN, CARBON BLACK D001

TONER, USED, DIRTY TONER TONER, USED, DIRTY D001

TOULENE D001

TRANSFORMER TRANSFORMER W/ PCBS - 310 PPM M002

TRANSFORMER TRANSFORMER W/ PCBS 86 PPM M002

TRANSFORMER TRANSFORMER W/PCBS - 62PPM M002

TRANSFORMER TRANSFORMER W/PCBS 80 PPM M002

TRANSFORMER TRANSFORMER W/PCBS 86PPM M002

TRICHLOROETHANE 1 1 1 TRICHLOROETHENE U226

TRICHLOROETHANE 1,1,1, TRICHLOROETHANE, DIRTY F002

TRICHLOROETHANE 1,1,1, TRICHLOROETHANE, SPENT F002

Page 59



TRICHLOROETHANE 111 TRICHLOROETHANE U226

TRICHLOROETHANE TRICHLOROETHANE F002

TRICHLOROETHANE TRICHLOROETHANE 111 U226

TRICHLOROETHANE,CTM TRICHLOROETHANE, 1,1,1- ; CONTAMINATED F001

TRICHLOROETHYLENE TRICHLOROEHTYLENE D040

TRICHLOROTRIFLUOROE TRICHLOROTRIFLUOROETHANE F002

TRNSFRMR OIL<5O PPM TRANSFORMER OILS, LESS THAN 50 PPM PCBS M002

TURCO SOLVENT TURCO SOLVENT D007 F002 F003

TY-ION I20 NA NITRI TY-ION I20; SODIUM NITRITE D001

UNDERCOATING UNDERCOATING SUPERGUARD D001

UNIVERSAL CEMENT 1,1,1-TRICHLOROETHANE F002

UNKNOWN ANALYSIS 4116 D001

UNKNOWN PAINT D001 D035

UNKNOWN PAINT ETC D001

UNKNOWN SEE ANALYSIS KAL-155 D035

UNKNOWN UNKNOWN BLUE LIQUID D035

UNKNOWN UNKNOWN FOUND IN DRUM STORAGE D010

UNKNOWN UNKNOWN LIQUID FROM AIMD D006

UNKNOWN UNKNOWN TAR FROM WEAPONS AREA D018

UNKNOWN UNKNOWN YELLOW LIQUID F003

UNKNOWN KAL-147 CHROMIUM, TOLUENE, KEROSENE D001 D007 F005

UNKNOWN LIQUID 560 MG/KG MEK, FP 80 DEG F D001 D006 D008 D035

UNKNOWN LIQUID TANK FROM STEAM PLANT D001 D018 D035

URETHANE VARNISH XYLENE, ETHYL BENZENE, TOLUENE D001 F003 F005

USED FIXATIVE D011

VANADIUM STANDARD VANADIUM STANDARD D002

VARNISH VARNISH D001

VARNISH SPAR SOLVENT D001

VARNISH, ELECTRICAL VARNISH, ELECTRICAL- PAINT WASTE D001

WALKWAY COMPOUND NAPTHA, LEAD, COBALT D001 D008

WALKWAY COMPOUND WALKWAY COMPOUND D001

WARFARIN WARFARIN <.3 U248

WASH PRIMER COATING ZINC CHROMATE, 2-ETHOXYETHYL ACETATE, D001 D007

WASTE CARBONATE PESTICIDE SHOP F002

WASTE DIESEL FUEL WASTE DIESEL FUEL, CONTAMINATED W/WATER D001

WASTE FUEL WASTE FUEL D001

WASTE FUEL, CONTAM. WASTE DIESEL FUEL, CONTAMINATED W/OIL,WATER,ANTI-F D001

WASTE FUEL, CONTAM. WASTE FUEL, CONTAMINATED D001

WASTE FUEL,CONTAM. WASTE JP-5, CONTAMINATED W/WATER & DIRT D001

WASTE FUELS, CONTAM WASTE MOTOR FUELS, CONTAMINATED W/ WATER, DIRT D001

WASTE GASOLINE WASTE GASOLINE D001

WASTE GASOLINE WASTE GASOLINE D001 D018

WASTE OIL CONTAMINATED WASTE OIL D005 D008 F002

WASTE OIL OILS, LUBRICATING, INSTRUMENT D001

WASTE OIL WASTE LUBRICATING OIL D001

WASTE OIL CONTAM D001

WASTE OIL, CONTAM WASTE OIL, CONTAMINATED D001

WASTE OIL, CONTAM. WASTE HYDRAULIC OILS CONTAMINATED W/ SOLVENTS D001

WASTE OIL, CONTAM. WASTE HYDRAULIC OILS, CONTAMINATED W/ SOLVENTS D001

Page 60



WASTE OIL, CONTAM. WASTE OIL, CONTAMINATED W/THINNERS D001

WASTE OIL, CONTAM. WASTE OILS, CONTAMINATED W/ HALOGENS D001

WASTE OIL, CONTAM. WASTE OILS, CONTAMINATED W/SOLVENTS D001

WASTE OIL, CONTAM. WASTE OILS, CONTAMINATED, COMBUSTIBLE D001

WASTE OIL, CONTAM. WASTE OILS,CONTAMINATED W/HALOGENS D001

WASTE OIL, CONTAMIN CADMIUM (2.57 MG/L), LEAD (12.58 MG/L) D006 D008

WASTE OIL, CONTAMIN CHROMIUM (136.0MG/L) D007

WASTE OIL,CONTAM. WASTE OIL,CONTAMINATED W/HALOGENS D001

WASTE OIL,CONTAM. WASTE OILS, CONTAMINATED D001

WASTE OIL,CONTAM. WASTE OILS, CONTAMINATED W/HALOGENS D001

WASTE OIL,CONTAM. WASTE OILS,CONTAMINATED W./HALOGENS D001

WASTE OILS, CONTAM. WASTE ENGINE OILS, CONTAMINATED W/ SOLVENTS D001

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED D001

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED W/ HALOGENATED SOLVENTS F002

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED W/ SOLVENTS F002

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED W/HALOGENATED SOLVENTS D001

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED W/SOLVENTS D001

WASTE OILS, CONTAM. WASTE OILS, CONTAMINATED W/SOLVENTS F002

WASTE PAINT D001

WASTE PAINT PAINT RELATED MATERIAL D001

WASTE PAINT PAINT RELATED MATERIAL F003

WASTE PAINT PAINT RELATED MATERIAL F005

WASTE PAINT PAINT WASTE, CADIMUM, MEK, N-BUTYL ALCOHOL D001 D006 D035 F003 F005

WASTE PAINT TOLUENE 2.5%, MAPTHA 97.5% D001 F005

WASTE PAINT FILTERS PAINT FILTERS STRONTIUM CHROMATE D007

WASTE POL RAGS POL RAGS POL WASTE RAGS, THINNER, VVL-800 D001

WASTE RAGS HALOGENATED RAGS CHROMIUM, 1,1,1-TRICHLOROETHANE; RAGS; PRM; D001 D007 F002

WASTE RAGS PAINT RAGS BARIUM, XYLENE, TOLUENE,N-BUTYL ACETATE, MIK D001 D005 D035 F002

WASTE RAGS PAINT RAGS WASTE RAGS F002

WASTE RAGS POL RAGS WASTE RAGS, CONTAMINATED W/ JP-5, ENGINE OILS AND D001

WASTE RAGS W/ PRM PAINT RAGS MEK, MIK, N-BUTYL ALCOHOL, XYLENE, ETHYL BENZENE, D001 D007 D008 D018 D035 F002

WASTE RAGS W/ PRM PAINT RAGS MEK, MIK, N-BUTYL ALCOHOL, XYLENE, ETHYL BENZENE, D001 D007 D035 F002 F003 F005

WASTE RAGS W/ PRM PAINT RAGS MEK, XYLENE, JP-5 D001 D035 F003 F005

WASTE RAGS W/ PRM PAINT RAGS PAINT WASTE D001 D035 F003 F005

WASTE RAGS W/PAINTS PAINT RAGS WASTE RAGS, CONTAMINATED W/ PAINTS & THINNERS D007 D008 D035 F002 F003 F005

WASTE RAGS, PAINT PAINT RAGS PAINT RELATED MATERIAL - RAGS, PAINT & THINNER SAT D001

WASTE RAGS, PRM PAINT RAGS WASTE RAGS D001 D035 F002 F003 F005

WASTE RAGS, SOLVENT PAINT RAGS WASTE RAGS, SOLVENT SATURATED, HALO & NON-HALO F002

WASTE TONER/DISPER TONER NAPTHA (PETROLEUM) D001

WATER & STRIPPER LUBE OIL, PENAIR M5573, TURCO 6037 D002 D007

WATER LEAD CONTAM LEAD, WATER D008

WAX AIRCRAFT WAX (ADDED TO ITEM 361) D001 D007 D035

WAX STODDARD SOLVENT D001

WAX STRIPPER SODIUM HYDROXIDE D002

WAX, AUTOMOBILE STODDARD SOLVENT D001

WOOD STAIN VM&P NAPTHA, TALC, VOL ORGANIC COMPOUNDS D001

X-RAY FIXATIVE D011

X-RAY FIXATIVE PHOTOGRAPHY WASTES D011

X-RAY FIXATIVE X-RAY FIXATIVE D011

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X-RAY FIXER X-RAY FIXER D011

XYLENE XYLENE D001 U239

XYLENE XYLENE, SPENT, DIRTY F003

XYLENE REAGENT XYLENE, ETHYL BENZENE D001

ZINC CHROMATE BENZENE, ZINC CHROMATE, LEAD, METHYLENE CHLORIDE, D001 D007 D008 D018

ZINC CHROMATE PRIME D001

Page 62

EXHIBIT D

Notice of Petroleum Products and Derivatives

Notice of the use and storage of petroleum products and derivatives is provided herein for the Transfer Parcels, as described in Sections 3.3 and 3.4 of this FOST.

EXHIBIT E

Asbestos-Containing Materials Hazard Disclosure and Acknowledgment Form

ASBESTOS-CONTAINING MATERIALS HAZARD DISCLOSURE AND ACKNOWLEDGMENT FORM

ASBESTOS WARNING STATEMENT YOU ARE ADVISED THAT CERTAIN BUILDINGS AND UNDERGROUND UTILITIES AT THE FORMER NAVAL AIR STATION BRUNSWICK POTENTIALLY CONTAIN ASBESTOS-CONTAINING MATERIALS. INDIVIDUALS (WORKERS) MAY SUFFER ADVERSE HEALTH EFFECTS AS A RESULT OF INHALATION EXPOSURE TO ASBESTOS. THESE ADVERSE HEALTH EFFECTS INCLUDE ASBESTOSIS (PULMONARY FIBROSIS) AND MESOTHELIOMAS (BENIGN OR MALIGNANT TUMORS).

ACKNOWLEDGMENT I acknowledge that: (1) I have read and understand the above-stated Asbestos Warning Statement. (2) I have received from the Government the following document(s): Finding of Suitability to Transfer,

FOST 2013-5, PARCELS AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, AND EDC-46 (Approximately 59.58 Acres), Former Naval Air Station Brunswick, Brunswick, Maine (Department of Navy [DoN] Base Realignment and Closure [BRAC] Program Management Office [PMO] East, 2014); Final (Revision 2) Environmental Condition of Property Report for the Naval Air Station, Brunswick, Maine (DoN BRAC PMO, 2006); Lead and Asbestos Containing Building Materials Summaries (Sanders, 2011), and the Construction Completion Report, Asbestos Contaminated Soil Remediation Building 20 Crawl Space, Former Naval Air Station, Brunswick, Maine (AGVIQ, 2013) representing the best information available to the Government as to the presence of and condition of asbestos-containing-materials hazards in the buildings, crawl spaces, and underground utilities and pipelines covered by this transfer deed.

(3) I understand that my failure to inspect or to become fully informed of the condition of all or any portion

of the property offered will not constitute grounds for any claim or demand for adjustment or withdrawal of any bid or offer made after its opening or tender.

(4) I understand that, upon execution of this deed transfer, I shall assume full responsibility for preventing

future asbestos exposure by properly managing and maintaining or, as required by applicable federal, State, or local laws or regulations, for abating any asbestos hazard in buildings and structures, underground utilities, or fuel pipelines that may pose a risk to human health.

_____________________________ ____________________ GRANTEE (or duly authorized agent) Date

EXHIBIT F

Lead-Based Paint Hazard Disclosure and Acknowledgment Form

LEAD-BASED PAINT HAZARD DISCLOSURE AND ACKNOWLEDGMENT FORM

LEAD WARNING STATEMENT

YOU ARE ADVISED THAT STRUCTURES CONSTRUCTED PRIOR TO 1978 MAY PRESENT EXPOSURE TO LEAD FROM LEAD-BASED PAINT THAT MAY PLACE YOUNG CHILDREN AT RISK OF DEVELOPING LEAD POISONING. LEAD POISONING IN YOUNG CHILDREN MAY PRODUCE PERMANENT NEUROLOGICAL DAMAGE. YOU ARE FURTHER ADVISED THAT LEAD POISONING ALSO POSES A PARTICULAR RISK TO PREGNANT WOMEN. WORKERS MAY ALSO SUFFER ADVERSE HEALTH EFFECTS FROM LEAD DUST AND FUME EXPOSURE.

ACKNOWLEDGMENT I acknowledge that: (1) I have read and understand the above stated Lead Warning Statement; (2) I have received from the Federal Government the following document(s): Finding of Suitability to

Transfer, FOST 2013-5, PARCELS AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, AND EDC-46 (Approximately 59.58 Acres), Former Naval Air Station Brunswick, Brunswick, Maine (Department of Navy [DoN] Base Realignment and Closure [BRAC] Program Management Office [PMO] East, 2014), Final (Revision 2) Environmental Condition of Property Report for the Naval Air Station, Brunswick, Maine (DoN BRAC PMO, 2006), and Lead and Asbestos Containing Building Materials Summaries (Sanders, 2011), representing the best information available to the Government as to the presence of Lead-Based Paint and Lead-Based Paint hazards for the buildings covered by this transfer;

(3) I understand that my failure to inspect, or to become fully informed as to the condition of all or any

portion of the property offered will not constitute grounds for any claim or demand for adjustment or withdrawal of any bid or offer made after its opening or tender; and

(4) I understand that upon execution of this deed transfer, I shall assume full responsibility for preventing

future lead exposure by properly managing and maintaining or, as required by applicable Federal, state, or local laws or regulations, for abating any lead-based paint hazard in buildings and structures that may pose a risk to human health.

_____________________________ ________________ GRANTEE (or duly authorized agent) Date

EXHIBIT G

Environmental Notices, Restrictions, and Covenants

G-1

Exhibit G-1 Environmental Notices, Restrictions, and Covenants FOST 2013-5

Transfer Parcels AIR-18, EDC-15, EDC-28, EDC-34, and EDC-35 Former Naval Air Station Brunswick

Brunswick, Maine

1. Notice of Environmental Condition: Information concerning the environmental condition of

Parcels AIR-18, EDC-15, EDC-28, EDC-34, and EDC-35 (PROPERTY) is contained in the

document known as the Finding of Suitability to Transfer (FOST) 2013-5 dated _____ 2014,

which is attached hereto and made a part hereof as Exhibit “_”, the receipt of which is hereby

acknowledged by the GRANTEE. An Environmental Condition of Property (ECP) report and

other environmental documents are referenced in the FOST; the FOST, ECP and referenced

environmental documents describe environmental conditions on the PROPERTY. The FOST

sets forth the basis for the GOVERNMENT’s determination that the PROPERTY is suitable for

transfer. Together, the FOST, ECP, and referenced environmental documents contain all

pertinent information currently known by GOVERNMENT as to the environmental condition of the

PROPERTY. GRANTEE hereby acknowledges that it has been provided copies of the ECP and

FOST. The specific environmental conditions described in the FOST and ECP, which are

applicable to the PROPERTY, are contained in this Quitclaim Deed.

2. CERCLA Covenant: Pursuant to Section 120(h)(4)(D)(i) of the Comprehensive Environmental

Response, Compensation and Liability Act of 1980 (42 U.S.C. § 9620(h)(4)(D)(i)), the United

States warrants that any response action or corrective action found to be necessary after the date

of this deed for contamination existing on the PROPERTY prior to the date of this deed shall be

conducted by the United States.

3. Reservation of Access required by Title, 42 U.S.C., Section 9620(h)(4)(D)(ii): The United

States retains and reserves a perpetual and assignable easement and right of access on, over,

and through the PROPERTY, to enter upon the PROPERTY in any case in which an

environmental response or corrective action is found to be necessary on the part of the United

States, without regard to whether such environmental response or corrective action is on the

PROPERTY or on adjoining or nearby lands. Such easement and right of access includes,

without limitation, the right to perform any environmental investigation, survey, monitoring,

sampling, testing, drilling, boring, coring, test pitting, installing monitoring or pumping wells or

other treatment facilities, response action, corrective action, or any other action necessary for the

United States to meet its responsibilities under applicable laws and as provided for in this

instrument. Such easement and right of access shall be binding on the GRANTEE and its

successors and assigns and shall run with the land.

G-2

In exercising such easement and right of access, the United States shall provide the GRANTEE

or its successors or assigns, as the case may be, with reasonable notice of its intent to enter

upon the PROPERTY and exercise its rights under this clause, which notice may be severely

curtailed or even eliminated in emergency situations. The United States shall use reasonable

means to avoid and to minimize interference with the GRANTEE’s and the GRANTEE’s

successors’ and assigns’ quiet enjoyment of the PROPERTY. At the completion of work, the

work site shall be reasonably restored. Such easement and right of access includes the right to

obtain and use utility services, including water, gas, electricity, sewer, and communications

services available on the PROPERTY at a reasonable charge to the United States. Excluding the

reasonable charges for such utility services, no fee, charge, or compensation will be due the

GRANTEE, nor its successor and assigns, for the exercise of the easement and right of access

hereby retained and reserved by the United States.

In exercising such easement and right of access, neither the GRANTEE nor its successors and

assigns, as the case may be, shall have any claim at law or equity against the United States or

any officer, employee, agent, contractor of any tier, or servant of the United States based on

actions taken by the United States or its officers, employees, agents, contractors of any tier, or

servants pursuant to and in accordance with this clause; Provided, however, that nothing in this

paragraph shall be considered as a waiver by the GRANTEE and its successors and assigns of

any remedy available to them under the Federal Tort Claims Act.

4. Federal Facility Agreement: The former Naval Air Station Brunswick (Main Base) has been

identified as a National Priorities List (NPL) Site under the Comprehensive Environmental

Response Compensation and Liability Act (CERCLA) of 1980, as amended. The transfer deed,

as it currently exists or may be amended, shall not affect the rights and obligations of parties

under the Federal Facility Agreement ([FFA] DoN, USEPA, State of Maine, 1990). The FFA

Section VIII requires that the Navy ensure that any transactions involving interest or right in real

property do not impede or impair activities or response actions taken pursuant to the FFA.

Therefore, the Navy has provided and the GRANTEE will acknowledge it has received a copy of

the FFA through execution of the deed. The Navy will ensure that provisions in the transfer deed

address the rights of Navy and regulatory agencies to access the PROPERTY to conduct

environmental studies and investigations and to carry out environmental responses as necessary;

contain provisions relating to compliance with applicable health and safety plans; and for

operation of any response actions.

G-3

5. Access to PROPERTY by State of Maine: Pursuant to Maine law (Maine Revised Statutes Title

38 [38 M.R.S. Chapter 3, §548; 38 M.R.S. Chapter 13 §1318-B; and 38 M.R.S Chapter 13 §1361

et seq]), GRANTEE agrees on behalf of itself, its successors and assigns as a covenant running

with the land, that the State of Maine, or its officers, agents, employees, contractors and

subcontractors (the “State”), shall have the right to enter upon the PROPERTY to perform any

environmental investigation, survey, monitoring, sampling, testing, drilling, boring, coring, test

pitting, installing monitoring or pumping wells or other treatment or containment facilities if

corrective or remedial action is found by the State to be necessary or advisable after the date of

transfer and that GRANTEE shall allow the State to enter upon the PROPERTY for such

purposes following reasonable notice. The State agrees to use reasonable means to avoid or

minimize interference with GRANTEE’s or GRANTEE’s successors’ and assigns’ quiet enjoyment

of the PROPERTY so as not to unreasonably interfere with GRANTEE’s and the GRANTEE’s

successors’ and assigns’ operations on the PROPERTY. GRANTEE and all successive owners

of the PROPERTY or any portion thereof, and their assigns, are hereby bound by such covenants

for the benefit of the State as the covenantee.

6. Parcel AIR-18 Reuse Restriction: The GRANTEE, its successors, and assigns agree that

reuse of Parcel AIR-18 shall be restricted to airport/aviation-related activities and that this parcel

cannot be used for residential or office scenarios that include long-term elder care facilities, child

day care, pre-school, child playground or any other similar child-occupied facility or activity. This

parcel shall not be used for dwellings of any kind, lodgings, campgrounds, community centers,

recreational facilities, stables, farms, or vegetable gardens.

7. Parcels EDC-15 and EDC-35 Reuse Restriction: The GRANTEE, its successors, and assigns

agree that Parcels EDC-15 and EDC-35 shall be restricted to commercial/industrial reuse, and

that these parcels cannot be used for residential or office scenarios that include long-term elder

care facilities, child day care, pre-school, child playground or any other similar child occupied

facility or activity. These parcels shall not be used for dwellings of any kind, lodgings,

campgrounds, community centers, recreational facilities, stables, farms, or vegetable gardens.

8. Groundwater Use Restriction: The GRANTEE, its successors, and assigns agree that no

groundwater extraction/production supply wells shall be installed or permitted, and that no access

to groundwater for dewatering or other purposes shall be permitted on the PROPERTY without

the prior written approval of the Navy and the applicable federal and state regulatory agencies, as

appropriate.

G-4

9. Parcels EDC-15 and EDC-35 Soil Disturbance Restriction: The GRANTEE, its successors,

and assigns agree that no soil excavation, drilling, digging or other ground-disturbing activities,

including disturbance of building slabs, roads and other structures and paved areas, shall be

allowed within Parcels EDC-15 and EDC-35 without prior written approval of the Navy, and the

applicable federal and state regulatory agencies, as appropriate.

10. Presence of Polycyclic Aromatic Hydrocarbons (PAHs) in Soil: The GRANTEE

acknowledges that PAHs are likely to exist in soils on Parcel AIR-18 as a result of airport

operations including but not limited to emissions from aircraft engine exhaust; e.g., at the ends of

runway, edges of apron areas and locations where engine testing occurred on a regular basis.

Emissions from engine exhaust of a motor vehicle, rolling stock, aircraft, or vessel or pipeline

pumping station engine are specifically excluded from the definition of release under CERCLA

Section 101(22) (42 U.S.C. § 9601(22)). The GRANTEE will need to manage potential risk to

commercial/industrial/construction workers from exposure to soils containing PAHs at levels that

may exceed human health exposure guidelines in accordance with the Materials Management

Plan for MRRA Property, Brunswick Landing, Brunswick, Maine.

11. Discovery of Previously Unknown Contamination: The GRANTEE, its successors and

assigns, or their subcontractors, shall stop all work and notify the Navy immediately if previously

unknown contamination, such as, but without limitation, buried debris, stained soil, unusual odors,

is discovered during soil disturbing activity such as soil excavation, drilling, digging or other

ground-disturbing activities, including disturbance of building slabs, roads and other structures

and paved areas.

12. Presence of Asbestos: The GRANTEE, its successors, and assigns, covenant and agree that

they will comply with all federal, state and local laws relating to ACM in their use of any buildings

and structures included in this transfer (including demolition and disposal of underground utilities

and pipelines that may contain ACM wrapping). The GRANTOR assumes no new or further

liability as a result of this transfer than it would otherwise have for losses, judgments, claims,

demands or expenses, or damages of whatever nature or kind from or incident to the purchase,

transportation, removal, handling, use, disposition, or other activity causing or leading to contact

of any kind whatsoever with ACM from buildings, structures, and underground utilities and

pipelines included in this transfer. Due to the known or potential presence of undiscovered ACM

associated with underground utilities and pipelines, any subsurface work performed by the

GRANTEE must be conducted in accordance with applicable regulations and conducted by

trained, properly-equipped personnel. Buildings and structures included in this transfer will be

transferred “as is” and asbestos hazards in said buildings and underground utilities and pipelines

G-5

will become the responsibility of the GRANTEE. The GRANTEE will be required to sign the

Asbestos Hazard Disclosure and Acknowledgment Form included as Exhibit E of the FOST prior

to execution of the transfer deed.

13. Presence of Lead-Based Paint: The GRANTEE, its successors, and assigns agree that they

will comply with all federal, state, and local laws relating to LBP in their use of any buildings and

structures on the PROPERTY (including demolition and disposal of existing improvements). The

GRANTOR assumes no new or further liability as a result of this transfer than it would otherwise

have for losses, judgments, claims, demands, expenses, or damages of whatever nature or kind

from or incident to the purchase, transportation, removal, handling, use, disposition, or other

activity causing or leading to contact of any kind whatsoever with LBP from buildings or structures

on the PROPERTY. Buildings will be transferred “as is” and LBP hazards in said buildings will

become the responsibility of the GRANTEE. The GRANTEE will be required to sign the Lead-

based Paint Hazard Disclosure and Acknowledgment Form included as Exhibit F of the FOST

prior to execution of the transfer deed.

14. Presence of Polychlorinated Biphenyls in Building Materials: The GRANTEE acknowledges

that fluorescent light fixture ballasts in facilities on the PROPERTY may contain PCBs. Prior to

beginning any maintenance, alterations, demolition, restoration, or construction work affecting

fluorescent light fixtures, the GRANTEE must determine if PCB ballasts are present. If present,

PCB ballasts and/or fixtures must be disposed of properly in accordance with all applicable

Federal, State, and local laws and regulations. The GRANTEE also acknowledges that buildings

constructed or renovated between 1950 and 1978 have the potential to have PCBs contained

within caulking, and the PCBs can migrate from the caulk into air, dust and surrounding material,

such as wood, bricks and soil. Such materials must be handled, managed and disposed of

properly during maintenance and/or renovations by the GRANTEE.

15. Pesticide Notification. The GRANTEE is hereby notified that the Transfer Parcels may contain

pesticide residue from pesticides that have been applied in the management of the PROPERTY.

The GRANTOR knows of no use of any registered pesticide in a manner inconsistent with its

labeling and believes that all applications were made in accordance with the Federal Insecticide,

Fungicide and Rodenticide Act (FIFRA - 7 U.S.C. Sec. 136, et seq.), its implementing regulations,

and according to the labeling provided with such substances. It is the GRANTOR's position that,

other than as described in the Final Environmental Condition of Property Report dated May 30,

2006, it shall have no obligation under the covenants provided pursuant to Section 120(h)(3)(A)(ii)

of the Comprehensive Environmental Response, Compensation and Liability Act of 1980, 42

U.S.C. Sections 9620(h)(3)(A)(ii), for the remediation of legally applied pesticides.

G-6

16. Parcel EDC-28 Groundwater Monitoring Wells: The GRANTOR reserves for itself an

easement to certain areas, more fully described in the deed, and located within Parcel EDC-28,

as shown on FOST Figure B-9, and as listed on FOST Table B-10, for (a) the periodic sampling

of existing groundwater monitoring wells to satisfy the requirements of the Navy Installation

Restoration (IR) and Petroleum Programs and (b) the maintenance or abandonment of the

monitoring wells. The GRANTOR shall further have the right, in common with all others entitled

thereto, to pass and repass on streets, roadways, and passageways as may exist and as

reasonably necessary to install new wells and perform periodic sampling and required

maintenance of the existing and any future groundwater monitoring wells on the

PROPERTY. The GRANTEE, its successors, and assigns shall be able to use the PROPERTY

in any manner that does not relocate or otherwise interfere with the integrity, maintenance or

continued usefulness of the monitoring wells, or any part or portion thereof without the prior

written consent of the GRANTOR. This restriction will be required for as long as the wells are

needed to meet the requirements of the Navy IR and Petroleum Programs. If wells become

damaged, they will be replaced by the Navy and the cost will be borne by the GRANTEE or its

successors and assigns.

17. Other Land Use Controls: The GRANTEE, its successors, and assigns agree that they will

comply with provisions for all existing or future Land Use Controls established for sites as part of

CERCLA Records of Decision and Remedial Design documents, or Petroleum Program decision

documents.

G-7

Exhibit G-2 Environmental Notices, Restrictions, and Covenants

FOST 2013-5 Transfer Parcels AIR-10, AIR-13, EDC-27, EDC-45, and EDC-46 Former Naval Air Station Brunswick

Brunswick, Maine


Parcels AIR-10, AIR-13, EDC-27, EDC-45, and EDC-46 (PROPERTY) is contained in the

document known as the Finding of Suitability to Transfer (FOST) 2013-5 dated _____ 2014,

which is attached hereto and made a part hereof as Exhibit “_”, the receipt of which is hereby

acknowledged by the GRANTEE. An Environmental Condition of Property (ECP) report and

other environmental documents are referenced in the FOST; the FOST, ECP and referenced

environmental documents describe environmental conditions on the PROPERTY. The FOST

sets forth the basis for the GOVERNMENT’s determination that the PROPERTY is suitable for

transfer. Together, the FOST, ECP and referenced environmental documents contain all

pertinent information currently known by GOVERNMENT as to the environmental condition of the

PROPERTY. GRANTEE hereby acknowledges that it has been provided copies of the ECP and

FOST. The specific environmental conditions described in the FOST and ECP, which are

applicable to the PROPERTY, are contained in this Quitclaim Deed.

2. CERCLA Covenant: Pursuant to §120(h)(3)(A)(ii) and (B) of the Comprehensive Environmental

Response, Compensation and Liability Act of 1980 (42 U.S.C. Section 9620(h)(3)(A)(ii) and (B)), the United States warrants that:

a. All remedial action necessary to protect human health and the environment with respect

to any hazardous substances identified pursuant to §120(h)(3)(A)(i)(I) of the

Comprehensive Environmental Response, Compensation and Liability Act of 1980

remaining on the PROPERTY has been taken before the date of this deed, and

b. Any additional remedial action found to be necessary after the date of this deed shall be

conducted by the United States. This covenant shall not apply to the extent that the

GRANTEE caused or contributed to any release or threatened release of any hazardous

substance, pollutant, or contaminant.

3. Reservation of Access as Required by 42 U.S.C. §9620(h)(3)(A)(iii): The United States

retains and reserves a perpetual and assignable easement and right of access on, over, and

through the PROPERTY, to enter upon the PROPERTY in any case in which an environmental

response or corrective action is found to be necessary on the part of the United States, without

regard to whether such environmental response or corrective action is on the PROPERTY or on

G-8

adjoining or nearby lands. Such easement and right of access includes, without limitation, the

right to perform any environmental investigation, survey, monitoring, sampling, testing, drilling,

boring, coring, test pitting, installing monitoring or pumping wells or other treatment facilities,

response action, corrective action, or any other action necessary for the United States to meet its

responsibilities under applicable laws and as provided for in this instrument. Such easement and

right of access shall be binding on the GRANTEE and its successors and assigns and shall run

with the land.

In exercising such easement and right of access, the United States shall provide the GRANTEE

or its successors or assigns, as the case may be, with reasonable notice of its intent to enter

upon the PROPERTY and exercise its rights under this clause, which notice may be severely

curtailed or even eliminated in emergency situations. The United States shall use reasonable

means to avoid and to minimize interference with the GRANTEE’s and the GRANTEE’s

successors’ and assigns’ quiet enjoyment of the PROPERTY. At the completion of work, the

work site shall be reasonably restored. Such easement and right of access includes the right to

obtain and use utility services, including water, gas, electricity, sewer, and communications

services available on the PROPERTY at a reasonable charge to the United States. Excluding the

reasonable charges for such utility services, no fee, charge, or compensation will be due the

GRANTEE, nor its successor and assigns, for the exercise of the easement and right of access

hereby retained and reserved by the United States.

In exercising such easement and right of access, neither the GRANTEE nor its successors and

assigns, as the case may be, shall have any claim at law or equity against the United States or

any officer, employee, agent, contractor of any tier, or servant of the United States based on

actions taken by the United States or its officers, employees, agents, contractors of any tier, or

servants pursuant to and in accordance with this clause; provided, however, that nothing in this

paragraph shall be considered as a waiver by the GRANTEE and its successors and assigns of

any remedy available to them under the Federal Tort Claims Act.

4. Notices Pursuant to Section 120(h)(3)(A)(i)(I) and (II) of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (42 U.S.C. § 9620(h)(3)(A)(i)(I) and (II)):

Pursuant to section 120(h)(3)(A)(i)(I) and (II) of CERCLA (42 U.S.C. § 9620(h)(3)(A)(i)(I) and (II)),

available information regarding the type, quantity, and location of hazardous substances and the

time at which such substances were stored, released, or disposed of, as defined in section

120(h), is provided for Parcels AIR-13, EDC-27, EDC-45, and EDC-46 in Exhibit “ ” attached

hereto and made a part hereof.

G-9

5. Description of Remedial Action Taken, if Any, Pursuant to Section 120(h)(3)(A)(i)(III) of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (42 U.S.C. § 9620(h)(3)(A)(i)(III)): Pursuant to section 120(h)(3)(A)(i)(III) of CERCLA (42 U.S.C. §

9620(h)(3)(A)(i)(III)), a description of the remedial action taken, if any, on Parcels AIR-13, EDC-

27, EDC-45, and EDC-46 is provided in Exhibit “_”, attached hereto and made a part hereof.





























G-10

8. Parcels AIR-10 and AIR-13 Reuse Restriction: The GRANTEE, its successors, and assigns

agree that reuse of Parcels AIR-10 and AIR-13 shall be restricted to airport/aviation-related

activities and that these parcels cannot be used for residential or office scenarios that include

long-term elder care facilities, child day care, pre-school, child playground or any other similar

child-occupied facility or activity. These parcels shall not be used for dwellings of any kind,

lodgings, campgrounds, community centers, recreational facilities, stables, farms, or vegetable

gardens.

9. Parcel EDC-45 Reuse Restriction: The GRANTEE, its successors, and assigns agree that

Parcel EDC-45 shall be restricted to commercial/industrial reuse, and that this parcel cannot be

used for residential or office scenarios that include long-term elder care facilities, child day care,

pre-school, child playground or any other similar child occupied facility or activity. This parcel

shall not be used for dwellings of any kind, lodgings, campgrounds, community centers,

recreational facilities, stables, farms, or vegetable gardens.





appropriate.

11. Parcel EDC-45 Soil Disturbance Restriction: The GRANTEE, its successors, and assigns

agree that no soil excavation, drilling, digging or other ground-disturbing activities, including

disturbance of building slabs, roads and other structures and paved areas, shall be allowed within

Parcel EDC-45 without prior written approval of the Navy, and the applicable federal and state

regulatory agencies, as appropriate.


acknowledges that PAHs are likely to exist in soils on Parcel AIR-10 and AIR-13 as a result of

airport operations including but not limited to emissions from aircraft engine exhaust; e.g., at the

ends of runway, edges of apron areas and locations where engine testing occurred on a regular

basis. Emissions from engine exhaust of a motor vehicle, rolling stock, aircraft, or vessel or

pipeline pumping station engine are specifically excluded from the definition of release under

CERCLA Section 101(22). The GRANTEE will need to manage potential risk to




G-11

13. Presence of PAHs in Soil on Parcel EDC-45: The GRANTEE acknowledges that PAHs are

likely to exist in soils on Parcel EDC-45 as a result of historical industrial activities at former

Building 13. The GRANTEE will need to manage potential risk to commercial / industrial /

construction workers from exposure to soils containing PAHs at levels that may exceed human

health exposure guidelines in accordance with the Materials Management Plan for MRRA

Property, Brunswick Landing, Brunswick, Maine.

14. Maintenance and Protection of Building 102 Protective Floor and Wall Coatings: The

GRANTEE, its successors, and assigns acknowledge they are aware of and agree that they will

maintain and protect the following areas in Building 102 that were encapsulated with protective

coatings to prevent lead exposure to occupants: floor areas - firing line, firing range, and

backstop and trap cleaning rooms; wall areas - backstop and trap cleaning rooms, up to 8 feet

high.






and paved areas.















Asbestos Hazard Disclosure and Acknowledgment Form included as Exhibit E of the FOST prior


G-12










based Paint Hazard Disclosure and Acknowledgment Form included as Exhibit F of the FOST






















G-13

20. Parcels AIR-10, EDC-27, and EDC-45 Groundwater Monitoring Wells: The GRANTOR

reserves for itself an easement to certain areas, more fully described in the deed, and located

within Parcels AIR-10, EDC-27, and EDC-45 as shown on FOST Figures B-5, B-8, and B-11 and

as listed on FOST Table B-10, for (a) the periodic sampling of existing groundwater monitoring

wells to satisfy the requirements of the Navy Installation Restoration (IR) and Petroleum

Programs and (b) the maintenance or abandonment of the monitoring wells. The GRANTOR

shall further have the right, in common with all others entitled thereto, to pass and repass on

streets, roadways, and passageways as may exist and as reasonably necessary to install new

wells and perform periodic sampling and required maintenance of the existing and any future

groundwater monitoring wells on the PROPERTY. The GRANTEE, its successors, and assigns

shall be able to use the PROPERTY in any manner that does not relocate or otherwise interfere

with the integrity, maintenance or continued usefulness of the monitoring wells, or any part or

portion thereof without the prior written consent of the GRANTOR. This restriction will be

required for as long as the wells are needed to meet the requirements of the Navy IR and

Petroleum Programs. If wells become damaged, they will be replaced by the Navy and the cost

will be borne by the GRANTEE or its successors and assigns.




documents.

G-14

Exhibit G-3

Environmental Notices, Restrictions, and Covenants FOST 2013-5 Transfer Parcels AIR-8 and AIR-11

Former Naval Air Station Brunswick Brunswick, Maine


Parcels AIR-8 and AIR-11 (PROPERTY) is contained in the document known as the Finding of

Suitability to Transfer (FOST) 2013-5 dated _____ 2014, which is attached hereto and made a

part hereof as Exhibit “_”, the receipt of which is hereby acknowledged by the GRANTEE. An

Environmental Condition of Property (ECP) report and other environmental documents are

referenced in the FOST; the FOST, ECP and referenced environmental documents describe

environmental conditions on the PROPERTY. The FOST sets forth the basis for the

GOVERNMENT’s determination that the PROPERTY is suitable for transfer. Together, the

FOST, ECP and referenced environmental documents contain all pertinent information currently

known by GOVERNMENT as to the environmental condition of the PROPERTY. GRANTEE

hereby acknowledges that it has been provided copies of the ECP and FOST. The specific

environmental conditions described in the FOST and ECP, which are applicable to the

PROPERTY, are contained in this Quitclaim Deed.














3. Reservation of Access: The GRANTOR reserves for itself, USEPA and MEDEP, their officers,

agents, employees, contractors, and subcontractors all reasonable and appropriate rights of

access to the PROPERTY for the purpose of monitoring and enforcing these restrictions,

provisions and conditions, for the purposes described below, and for such other purposes

G-15

consistent with any provision of the FFA. The right of access described herein shall include the

right to conduct tests, investigations, and surveys (including, where necessary, drilling, soil and

water sampling, test pitting, boring, soil gas surveys and other similar activities), and to conduct

tests or surveys required by the USEPA or MEDEP relating to assessment of environmental

conditions on the PROPERTY. Such right shall also include the right to conduct, operate,

maintain, or undertake any other response as reasonably necessary (including but not limited to

soil removals, monitoring wells, pumping wells, and treatment facilities). Any such entry, and all

responses, shall be coordinated in advance by GRANTOR, with such coordination including

reasonable notice provided to GRANTEE or its successors and assigns, and shall be performed

in a manner which eliminates, or minimizes to the maximum extent possible, (i) any damage to

any structures now or hereafter located on the PROPERTY and (ii) any disruption or disturbance

of the use and enjoyment of the PROPERTY.
















5. Reuse Restriction: The GRANTEE, its successors, and assigns agree that reuse of Parcels

AIR-8 and AIR-11 shall be restricted to airport/aviation-related activities and that the PROPERTY

cannot be used for residential or office scenarios that include long-term elder care facilities, child

day care, pre-school, child playground or any other similar child-occupied facility or activity.

These parcels shall not be used for dwellings of any kind, lodgings, campgrounds, community

centers, recreational facilities, stables, farms, or vegetable gardens.



G-16



appropriate.


acknowledges that PAHs are likely to exist in soils on Parcels AIR-8 and AIR-11 as a result of

airport operations including but not limited to emissions from aircraft engine exhaust; e.g., at the

ends of runway, edges of apron areas and locations where engine testing occurred on a regular

basis. Emissions from engine exhaust of a motor vehicle, rolling stock, aircraft, or vessel or

pipeline pumping station engine are specifically excluded from the definition of release under

CERCLA Section 101(22). The GRANTEE will need to manage potential risk to









and paved areas.















Asbestos Hazard Disclosure and Acknowledgment Form included as Exhibit D of the FOST prior


G-17










based Paint Hazard Disclosure and Acknowledgment Form included as Exhibit E of the FOST






















13. Groundwater Monitoring Wells: The GRANTOR reserves for itself an easement to certain

areas, more fully described in the deed, and located within Parcels AIR-8 and AIR-11, as shown

on FOST Figure B-4, and as listed on FOST Table B-10, for (a) the periodic sampling of existing

G-18

groundwater monitoring wells to satisfy the requirements of the Navy Installation Restoration (IR)

and Petroleum Programs and (b) the maintenance or abandonment of the monitoring wells. The

GRANTOR shall further have the right, in common with all others entitled thereto, to pass and

repass on streets, roadways, and passageways as may exist and as reasonably necessary to

install new wells and perform periodic sampling and required maintenance of the existing and any

future groundwater monitoring wells on the PROPERTY. The GRANTEE, its successors, and

assigns shall be able to use the PROPERTY in any manner that does not relocate or otherwise

interfere with the integrity, maintenance or continued usefulness of the monitoring wells, or any

part or portion thereof without the prior written consent of the GRANTOR. This restriction will be

required for as long as the wells are needed to meet the requirements of the Navy IR and

Petroleum Programs. If wells become damaged, they will be replaced by the Navy and the cost

will be borne by the GRANTEE or its successors and assigns.




documents.

EXHIBIT H

Comments and Responses

Toll Free • 1-888-372-7341 Internet Address (URL) • http://www.epa.gov/region1

Recycled/Recyclable • Printed with Vegetable Oil Based Inks on Recycled Paper (Minimum 30% Postconsumer)

February 12, 2014 Mr. Paul Burgio Department of Navy Base Realignment and Closure Program Management Office-Northeast 4911 South Broad Street Philadelphia, PA 19112-1303

Re: Finding of Suitability to Transfer (FOST 2013-5) for Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 at the Former Naval Air Station Brunswick, ME, February 2014 Dear Mr. Burgio: EPA has completed its review of the above referenced document. This Finding of Suitability to Transfer (FOST) serves as the basis for documenting the Navy’s decision that approximately 59.6 acres of land and improvements are suitable to be transferred from the Navy to the Midcoast Regional Redevelopment Authority (MRRA). The conveyance of these former NAS Brunswick parcels to MRRA is consistent with the Final NAS Brunswick Reuse Master Plan. Based on a review of the FOST and without any independent investigations or verification of the information outlined therein, EPA finds that the information presented in the document is sufficient to support this property conveyance, consistent with Department of Defense (DOD) policy. EPA reserves all rights and authorities relating to information not contained in the FOST whether or not such information was known when the FOST was issued or is discovered after such issuance. Please note that EPA reviewed this document solely for the purpose of determining whether it meets the requirements of DOD policy. EPA has not reviewed the document for any other purpose, including compliance with the National Environmental Policy Act.

Should you have any questions with regard to this letter, please feel free to contact me at (617) 918-1386.

UNITED STATES ENVIRONMENTAL PROTECTION AGENCYREGION 1

5 POST OFFICE SQUARE, SUITE 100BOSTON, MASSACHUSETTS 02109-3912

Sincerely, Michael J. Daly Remedial Project Manager Federal Facilities Superfund Section cc: Steve Levesque, MRRA Anna Breinich, Town of Brunswick Greg Preston, USN-BRAC PMO Todd Bober, USN-BRAC PMO Robert Leclerc, USN-Brunswick CSO Claudia Sait, MEDEP Lynne Jennings, USEPA Region I Steve Giannino, TetraTech Jeff Orient, TetraTech Ed Benedikt, BACSE

STATE OF MAINE

DEPARTMENT OF ENVIRONMENTAL PROTECTION

PAUL R. LEPAGE PATRICIA W. AHO

GOVERNOR COMMISSIONER

AUGUSTA BANGOR PORTLAND PRESQUE ISLE 17 STATE HOUSE STATION 106 HOGAN ROAD, SUITE 6 312 CANCO ROAD 1235 CENTRAL DRIVE, SKYWAY PARK AUGUSTA, MAINE 04333-0017 BANGOR, MAINE 04401 PORTLAND, MAINE 04103 PRESQUE ISLE, MAINE 04769 (207) 287-7688 FAX: (207) 287-7826 (207) 941-4570 FAX: (207) 941-4584 (207) 822-6300 FAX: (207) 822-6303 (207) 764-0477 FAX: (207) 760-3143

web site: www.maine.gov/dep

February 12, 2014 Mr. Paul Burgio OASN (EI&E), BRAC PMO NE Building 679, Naval Business Center 4911 South Broad Street Philadelphia, PA 19112-1303 Re: Finding of Suitability to Transfer - 2013-5,

Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46

Former Naval Air Station, Brunswick, Maine Dear Mr. Burgio:

The Maine Department of Environmental Protection (MEDEP) has reviewed the revised “Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46”, dated February 2014 along with the Navy’s responses to comments. This Finding of Suitability to Transfer (FOST) proposes to transfer 12 parcels totaling approximately 59.58 acres under an Airport Public Benefit Conveyance (AIR) or Economic Development Conveyance (EDC) to the Midcoast Regional Redevelopment Authority (MRRA) for airport related uses or economic related uses respectively. In FOST-2013-5 the Navy proposes to transfer the following parcels:

Parcels AIR 8 and 11 (25 acres) are adjoining parcels on the southeast end of the runway. AIR 8 contains Building 611 (Engine Test Facility) and AIR 11 contains Building 555 (Sonobuoy/Vehicle Storage).

Parcel AIR 10 (24 acres) is located on the west side of the runway. It contains Building 63 (Storage/High Explosive Magazine): the Fire Training Area – West, and the Former Munitions Bunker West, which were an Area of Potential Interest (AOPI) and a Munitions Response Program (MRP) site, respectively.

Parcels AIR 13 (4.4 acres) and EDC-15 (2.9 acres) are immediately adjacent to each other in the north central portion of the Base just east of the airfield. AIR 13 is located on both sides of Orion Street and contains Building 292 (Fire & Rescue Facility) and Building 45 (Hazardous Waste Transfer Facility). EDC 15 currently contains Buildings 41 (Security Office) and 647 (Bottled Gas Storage/Pest Control Shop). Parcel AIR 18 (5.74 acres) is in the northwest section of Base and contains the Air Traffic Control Tower (Building 231).

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AIR 8, 11 and 13 are located within the Aviation-Related Business District and MMRA proposes continued operation of the of the airfield and development of aviation-related business, industry, transportation and distribution, technology employment and other uses that rely on, or directly benefit from proximity to airport facilities and operations. AIR 18 was not included in the Reuse Master Plan because it was originally intended for transfer to the FAA but will be transferred to MMRA for airfield operations purposes.

Parcel EDC-35 (0.88 acres) contains an earthen bunker (Building 44) and loading dock.

Parcel EDC-27 (8.5 acres) is located east of Hangar 5 and includes Buildings 51 (NCIS/Fire Prevention) and 55 (Security Generator). The Machine Gun Boresight Range, a MRP site, is located within this parcel and a hot spot removal was undertaken based on a soil investigation of the area.

Parcel EDC-28 (4.7 acres), currently undeveloped, lies to the northeast where the former Air Force transmitter building (Building 586) was located. This area was investigated as an AOPI in 2012 and as part of an investigation of the Old Navy Fuel Farm in 2013.

Parcel EDC-34 (3.7 acres) contains the majority of the SeaBee Compound on the north central boundary of the Base near Route 24. Buildings 404, 629, 630, 631, 633, 634, 635, 636, 659, 661 & 662 are located within this parcel. This area was investigated as an AOPI in 2012.

Parcel EDC-45 (1.29 acres) is located in the north central portion of the Base and currently contains Building 102 (Indoor Small Arms Range). Historically, the parcel contained a hazardous materials supply storage facility along with several training buildings, an oil tank and drum crushing operation. This area was investigated under the RCRA program in 2010.

Parcel EDC-46 (0.3 acres) includes the Navy College Office (Building 20) and the land within the building footprint only. The surrounding land was transferred as part of EDC-9 in FOST 2012-1.

Under the FOST environmental restriction, provisions and conditions, the Navy is restricting the use of groundwater on all of the Transfer Parcels without the approval of the Navy and applicable state and federal regulatory agencies. AIR 8, AIR 10, AIR 11, AIR 13, AIR 18 and EDC 45 will be included in the Materials Management Plan for the airport and notification and prior approval is required for soil disturbance on EDC 15, EDC 35 and EDC 45. MEDEP concurs that the FOST meets the requirements of Section 120(h)(3) of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) for transfer of the parcel included in FOST 2013-5. The FOST process is primarily a record search and very little information is available for the 20-30 years that the Base operated prior to environmental regulation. Consequently the lack of reported storage, release or disposal of hazardous substances cited in the FOST may not represent the actual site conditions. If the site has or will be participating in the MEDEP Voluntary Response Action Program (VRAP) pursuant to Title 38 MRSA § 343-E, the protections provided by the VRAP “No Further Action Assurance” letter or the VRAP “Commissioner’s Certificate of Completion” are not superseded by anything in this concurrence letter.

of 3 Thank you for the opportunity to review this document and please contact me at (207) 287-7713 or [email protected], if you have any questions or comments. Respectfully, Claudia Sait Project Manager-Federal Facilities Bureau of Remediation & Waste Management Cf: Electronic Copy

Chris Evans-MEDEP Robert Leclerc-BNAS Todd Bober–BRAC PMO Mike Daly-EPA David W. Chipman Tom Brubaker-MMRA Carol Warren Scott Libby Suzanne Johnson-BASCE Ed Benedikt-BACSE Anna Breinich-Town of Brunswick Steve Giannino – Tetra Tech Carol White – CA White & Assoc. Jeff Orient – Tetra Tech

STATE OF MAINE

DEPARTMENT OF ENVIRONMENTAL PROTECTION

PAUL R. LEPAGE PATRICIA W. AHO

GOVERNOR COMMISSIONER

AUGUSTA BANGOR PORTLAND PRESQUE ISLE 17 STATE HOUSE STATION HOGAN ROAD, SUITE 6 312 CANCO ROAD 1235 CENTRAL DRIVE, SKYWAY PARK AUGUSTA, MAINE 04333-0017 BANGOR, MAINE 04401 PORTLAND, MAINE 04103 PRESQUE ISLE, MAINE 04769 (207) 287-7688 FAX: (207) 287-7826 (207) 941-4570 FAX: (207) 941-4584 (207) 822-6300 FAX: (207) 822-6303 (207) 764-0477 FAX: (207) 760-3143

web site: www.maine.gov/dep

August 16, 2013 Mr. Paul Burgio OASN (EI&E), BRAC PMO NE Building 679, Naval Business Center 4911 South Broad Street Philadelphia, PA 19112-1303 Re: Finding of Suitability to Transfer (FOST) 2013-5 Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18 EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 Former Naval Air Station, Brunswick, Maine

Dear Mr. Burgio: Maine Department of Environmental Protection (MEDEP) has reviewed the draft “Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46”, dated July 2013. This Finding of Suitability to Transfer (FOST) proposes to transfer 12 parcels totaling approximately 59.58 acres under an Airport Public Benefit Conveyance (AIR) or Economic Development Conveyance (EDC) to the Midcoast Regional Redevelopment Authority (MRRA) for airport related uses or economic related uses respectively. In FOST-2013-5 the Navy proposes to transfer the following parcels:

Parcels AIR 8 and 11 (25 acres) are adjoining parcels on the southeast end of the runway. AIR 8 contains Building 611 (Engine Test Facility) and AIR 11 contains Building 555 (Sonobuoy/Vehicle Storage).

Parcel AIR 10 (24 acres) is located on the west side of the runway. It contains Building 63 (Storage/High Explosive Magazine): the Fire Training Area – West, and the Former Munitions Bunker West, which were an Area of Potential Interest; and a Munitions Response Program (MRP) site, respectively. Site 18, the West Runway Study Area is excluded from this parcel.

Parcels AIR 13 (4.4 acres) and EDC-15 (2.9 acres) are immediately adjacent to each other in the north central portion of the Base just east of the airfield. AIR 13 contains Building 292 (Fire & Rescue Facility) and Building 45 (Hazardous Waste Transfer Facility) and is located on both sides of Orion Street. EDC 15 currently contains Buildings 41 (Security Office) and 647 (Bottled Gas Storage/Pest Control Shop). Historically EDC 15 contained a paint locker/storage shop, supply/classroom buildings, an indoor mobile shooting range, a beacon tower and a ready magazine. Parcel AIR 18 (5.74 acres) is in the northwest section of Base and contains the Air Traffic Control Tower (Building 231). AIR 8, 11 and 13 are located within the Aviation-Related Business District and MMRA proposes continued operation of the of the airfield and development of aviation-related business, industry, transportation and distribution, technology employment and other uses that rely on, or directly benefit from proximity to airport facilities and operations. AIR 18 was not included in the Reuse Master Plan

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because it was originally intended for transfer to the FAA but will be transferred to MMRA for airfield operations purposes.

Parcel EDC-35 (0.88 acres) contains an earthen bunker (Building 44) and loading dock (Building 556).

Parcel EDC-27 (8.5 acres) is located east of Hangar 5 and includes Buildings 51 (NCIS/Fire Prevention) and 55 (Security Generator). The Machine Gun Boresight Range, a MRP site, is located within this parcel.

Parcel EDC-28 (4.7 acres), currently undeveloped, lies to the northeast where the former Air Force transmitter building (Building 586) was located.

Parcel EDC-34 (3.7 acres) contains the majority of the SeaBee Compound on the north central boundary of the Base near Route 24. Buildings 404, 629, 630, 631, 633, 634, 635, 636, 659, 661 & 662 are located within this parcel.

Parcel EDC-45 (1.29 acres) is located in the north central portion of the Base and currently contains Building 102 (Indoor Small Arms Range). Historically, the parcel contained a hazardous materials supply storage facility along with several training buildings and an oil tank.

Parcel EDC-46 (0.3 acres) includes the Navy College Office (Building 20) and the land within the building footprint only. The surrounding land was transferred as part of EDC-9 in FOST 2012-1. EDC parcels are destined for economic development purposes. The EDC parcels are located within a variety of districts including the Business and Technology Industry District (EDC-15, 27, 35 & 45), Professional Office District (EDC-34), Residential District (EDC-28) and Community Mixed Use District (EDC-46).

Based on its review MEDEP has the following comments and issues. General Comments: 1. Some of parcels (AIR 8, 11, 18 and EDC 15) proposed for transferred have had their soil tested for

Polycyclic Aromatic Hydrocarbons (PAHs) and show exceedances of regulatory criteria. Any parcel with PAH concentrations above residential standards must be included in and handled in accordance with the Materials Management Plan (MMP). Other parcels not sampled but based on their location that should also be included in the MMP are AIR 13 and EDC-45 as a precaution.

2. According to the Resource Conservation and Recovery Act (RCRA) closure report for Building 292,

approximately 9891 pounds of Aqueous Fire Fighting Foam (AFFF) were disposed of from this building from 1990 to 2009. AFFF is known to contain the emerging contaminants, Perfluorooctanic Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA). Was AFFF stored either recently or historically at Building 292? If it was, then it may be necessary to sample groundwater and/or soil depending on how the material was stored.

3. Building 51 on Parcel EDC-27 was used to house the Naval Criminal Investigation Services (NCIS)

and Fire Prevention office and storage area for its entire history according to the RCRA closure report (January 2011). Is it known if AFFF was stored at Building 51?

4. The draft “Site Investigation Report for Four Areas of Potential Interest and Supplemental

Groundwater Characterization of Buildings 225 and 252” which included the investigation of the Fire Training Area-West was issued April 2011 and MEDEP sent comments dated June 14, 2011. The Navy needs to address MEDEP’s comments and finalize the report. Also in Section 3.2 of that report it states that groundwater was analyzed for PFOA and PFOS but the results did not seem to be included in the reports. What were the results?

of 4 5. The Navy should respond to MEDEP’s comments dated May 28, 2013 on the draft “Technical

Memorandum, Soil and Groundwater Investigation Building 611/555” (April 2013) and finalize the report.

6. The Navy may want to consider abandoning the four historic wells prior to transferring AIR 8 & 11. It

should also be discussed whether to abandon the new wells. One potential reason to keep some of them might be if there is a chance that we will need to pursue PFC distribution/sources around the base and this area had a reported release and data on PFCs in soil and groundwater.

7. Also the Navy may want to consider sealing off the floor drains in Buildings 611 and 555 and any

other building with floor drains prior to transfer. Specific Comments: 8. Section 3.1.1, CERCLA Hazardous Substance Notice, para 2: EDC-34 is listed as having no

hazardous substances known to have been stored or released or disposed of in excess of their respective threshold quantities, yet a Navy figure dated 1983 showing Solid Waste Management Units indicates that a waste oil Underground Storage Tank (UST) being on the parcel. Please check the information and revise as necessary.

9. Section 3.1.2, CERCLA Responses on the Transfer Parcels, para 2: Parcel EDC-27, as shown on figure B-8, encroaches onto the Orion Street Skeet Range (OSSR) to the north and east. Since the OSSR is still under investigation, those portions within the skeet range should be removed from the proposed transfer however the remaining property and buildings can still be transferred. .

10. Section 3.1.4, CERCLA Covenant, para 1: The Fire Training Area-West within AIR 10 had

Tetrachloroethene (PCE) above the leaching to groundwater criteria under the RAGs so please provide the rationale for stating that no hazardous substances and no petroleum products or their derivatives are known to have been released or disposed of in excess of their respective threshold quantities.

11. Section 3.2, Resource Conservation and Recovery Act, para 4: It is not clear under which programs

these investigations were performed and at least some of them were done under CERCLA in addition to the RCRA closure requirements. If these were performed under CERCLA it is not clear why it is included under this section. Please clarify/revise, as necessary.

12. Section 3.3.2, Petroleum Releases Originating on Adjoining Properties: “There are no other known or

suspected petroleum disposals or releases to the environment that originated within 200 feet of the Transfer Parcels.” MEDEP has noted and informed the Navy on numerous occasions starting in the Fall 2012 that a petroleum odor was evident from the storm grates on First Avenue on EDC-28 and across the road. On some occasions a sheen which seemed characteristic of petroleum not biological was visible in the ditch on the eastside of the road. It is unclear where the source might be located but the Old Fuel Farm is located upgradient although the most recent monitoring of groundwater for EPH and VPH were non detect. The Harpswell Pipeline runs just west of EDC 28 which also be a potential source.

13. Section 3.5, Munitions and Explosives of Concern, para 2: It is notable that soil analysis for lead in

soil at the Mobile Shooting Range was Toxicity Characteristic Leaching Procedure (TCLP). TCLP is used for disposal purposes not for risk. Is this information correct that the analysis was TCLP and not Total Lead?

14. Table B-2:

a. Machine Gun Boresight Range: The table should briefly discuss the removal of the backstop/berm. It appears that the berm was intact in 1966, but in the 1970’s some work on the berms was visible on aerial photos but it appeared to be excavated around 1981.

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b. POL Site 1, Old Navy Fuel Farm, Site Impact on Subject Property: Based on MEDEP observations of the storm drain on and adjacent to Parcel 328 there is the potential that the Old Navy Fuel Farm is impacting Parcel 328. (See comment 12 above.)

c. Investigation and Remedial Action…: LTM has continued since 2000. The last report was in

January 2011. Please correct.

d. IR Site 4, Acid/Caustic Disposal Pit, Investigation and Remedial Action…: To date only limited geophysical survey has been performed at Site 4. MEDEP suggests: “The Navy has conducted limited geophysical survey within Building 584 some additional work to more precisely identify the location of the former pit as part of the Data Gap Work Plan.” Please revise or clarify the last sentence.

e. AOPI Fire Training Area-West, Investigation and Remedial Action…: It should be noted in the

Table that the exact location of the FTA-W could not be determined.

f. AOPI Fire Training Area-West, Site-Specific Restrictions:

• Please consider the following change: “The Groundwater restrictions were recommended for the AOPI based on MEDEP concerns regarding the exceedance of leaching to groundwater criteria for PCE in soil.”

• Based on the exceedance of PCE for leaching to groundwater the Navy should consider a notification of digging within the Fire Training Area-West AOPI and a restriction on excess soil similar to that for the Airport Parcel.

g. Former Building 233 Investigation Area Investigation and Remedial Action…: Please use the site

specific background which is preferable to State-wide background.

h. Building 611/555 Investigation Area, Investigation and Remedial Action…: Please note if it was site specific background and, if not, please correct.

i. Building 611/555 Investigation Area, Site Impact on Subject Property: If the property is to be

transferred then appropriate restrictive language to protect workers must be developed and included in the Materials Management Plan.

15. Table B-4, EDC-15, Notes: See comment 12 above. Thank you for the opportunity to review this document and please contact me at (207) 287-7713 or [email protected], if you have any questions or comments. Respectfully, Claudia Sait Project Manager-Federal Facilities Bureau of Remediation & Waste Management Cf: Electronic Copy

Chris Evans-MEDEP Robert Leclerc-BNAS Mike Daly-EPA Todd Bober–BRAC PMO David W. Chipman Tom Brubaker-MMRA Carol Warren Scott Libby Ed Benedikt-BACSE Suzanne Johnson-BASCE Denise Clavette-Town of Brunswick Carolyn Lepage-Lepage Environmental

1

Response to MEDEP Comments Dated August 16, 2013, on the July 2013 Draft Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18,

EDC-15, EDC-7, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately 59.58 acres), Former Naval Air Station Brunswick, Brunswick, Maine

General Comments: 1. Some of parcels (AIR 8, 11, 18 and EDC 15) proposed for transferred have had their soil tested for

Polycyclic Aromatic Hydrocarbons (PAHs) and show exceedances of regulatory criteria. Any parcel with PAH concentrations above residential standards must be included in and handled in accordance with the Materials Management Plan (MMP). Other parcels not sampled but based on their location that should also be included in the MMP are AIR 13 and EDC-45 as a precaution.

Response: The requirement for the MMP (an agreement between MRRA and MEDEP) was developed

by the Navy for the first Airport FOST to address management of soil with PAHs at levels that could exceed commercial/industrial regulatory criteria present due to airfield operations. The airfield and other “AIR” parcels were not intended to support any residential reuse. The Navy has added this requirement to FOSTs for all “AIR” Parcels, and therefore it applies to AIR-8, -10, -11, -13, and -18. This requirement has been included in Exhibit G-1, Clause 10 for Parcel AIR-18; Exhibit G-2, Clause 12 for Parcels AIR-10 and AIR-13; and Exhibit G-3, Clause 7 for Parcels AIR-8 & AIR-11.

Due to the historical industrial activities at former Building 13 in Parcel EDC-45, the Navy has agreed to apply a PAH soil restriction to Parcel EDC-45 requiring that soils be managed in accordance with the MMP. This requirement has been added to Exhibit G-2 as new Clause 13.

2. According to the Resource Conservation and Recovery Act (RCRA) closure report for Building 292,

approximately 9891 pounds of Aqueous Fire Fighting Foam (AFFF) were disposed of from this building from 1990 to 2009. AFFF is known to contain the emerging contaminants, Perfluorooctanic Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA). Was AFFF stored either recently or historically at Building 292? If it was, then it may be necessary to sample groundwater and/or soil depending on how the material was stored.

Response: AFFF concentrate was typically shipped in boxes packed with absorbent and stored in 5-gallon containers. Expired containers of AFFF would have been disposed through the hazardous waste system as noted in the RCRA Closure Report, even though AFFF was not a hazardous waste. AFFF concentrate containers were not reported to have been stored in Building 292. The concentrate was used in tanks on the fire engines and Air Rescue Fire Fighter (ARFF) crash vehicles. Foam was generated on the trucks by mixing the concentrate with water using a foam induction system.

The Navy follows Department of Defense Instruction number 4715.18 for addressing Emerging Contaminants (EC). This instruction allows the Navy to sample for, and when appropriate, to take action to reduce risks related to ECs. Typically, sampling for these emerging contaminants has been conducted at fire-fighter training areas or locations of large, known spills, and the Navy has begun using this approach by sampling at the FTA, the FTA-W, and B611/555 (known spill). No AFFF spills or releases were reported at Building 292. The Navy will consider sampling at other locations should information become available at a future time that indicates sampling is warranted.

3. Building 51 on Parcel EDC-27 was used to house the Naval Criminal Investigation Services (NCIS)

and Fire Prevention office and storage area for its entire history according to the RCRA closure report (January 2011). Is it known if AFFF was stored at Building 51?

Response: Building 51 was included in a previous FOST and is not in Parcel EDC-27. References to

the building have been removed from text and tables of this FOST. AFFF was stored at Building 51 (constructed in 2005) in 5-gallon containers of concentrate as reported in the January 2011 RCRA

2

closure report. Twenty-seven containers were stored in the Fire Prevention portion of the building at the time of the December 2010 site visit for the RCRA closure report. Chemical inventories between 2006 and 2009 indicated that 140 to 150 containers may have been present during a year, but it is not known how many were present at any given time. No AFFF spills or releases were reported in Building 51.

4. The draft “Site Investigation Report for Four Areas of Potential Interest and Supplemental

Groundwater Characterization of Buildings 225 and 252” which included the investigation of the Fire Training Area-West was issued April 2011 and MEDEP sent comments dated June 14, 2011. The Navy needs to address MEDEP’s comments and finalize the report. Also in Section 3.2 of that report it states that groundwater was analyzed for PFOA and PFOS but the results did not seem to be included in the reports. What were the results?

Response: The Four Areas AOPI report was finalized on January 10, 2014. Groundwater was analyzed

for PFOA and PFOS, but since the results were non-detect, they were not included in the table of detected analytes in the Draft Report or discussed in the text. The groundwater data were included in Appendix B-2. Neither PFOA nor PFOS was detected in the groundwater sample from the FTA-W well sampled (UJ at 2 ng/l).

5. The Navy should respond to MEDEP’s comments dated May 28, 2013 on the draft “Technical

Memorandum, Soil and Groundwater Investigation Building 611/555” (April 2013) and finalize the report.

Response: The Technical Memorandum was finalized on January 13, 2014. MEDEP comments were

addressed in the Response to Comments. 6. The Navy may want to consider abandoning the four historic wells prior to transferring AIR 8 & 11. It

should also be discussed whether to abandon the new wells. One potential reason to keep some of them might be if there is a chance that we will need to pursue PFC distribution/sources around the base and this area had a reported release and data on PFCs in soil and groundwater.

Response: During the investigation conducted at Buildings 611/555, the Navy determined that four

possible historical wells identified in the Work Plan (conceivably associated with a former UST removal) were not actually wells. Rather, there were three clean outs associated with the Building 611 trench drains. A fourth location was a 1” hole in the asphalt with no PVC observed. This hole may have been associated with former tank piping, and all tanks were closed in accordance with the MEDEP requirements. Therefore, the only known wells on the parcels are those associated with the 2012 investigation. It is expected that the monitoring wells installed as part of the Buildings 611/555 study will eventually be abandoned; however, that decision has not been made at this time. While PFOS was detected at levels slightly greater than its EPA PHA in two wells, the overall levels of PFC detections were very low and are not indicative of a significant PFC release in the Buildings 611/555 area.

7. Also the Navy may want to consider sealing off the floor drains in Buildings 611 and 555 and any

other building with floor drains prior to transfer. Response: The Navy will consider sealing floor drains in these buildings in consultation with the

Transferee. No decision has been made at this time. Specific Comments: 8. Section 3.1.1, CERCLA Hazardous Substance Notice, para 2: EDC-34 is listed as having no

hazardous substances known to have been stored or released or disposed of in excess of their respective threshold quantities, yet a Navy figure dated 1983 showing Solid Waste Management Units indicates that a waste oil Underground Storage Tank (UST) being on the parcel. Please check the information and revise as necessary.

3

Response: Neither petroleum products nor waste oil are CERCLA hazardous substances; therefore, the

presence of the UST was not considered when EDC-34 was evaluated for the hazardous substance notice. The referenced UST (Tank 635.1) was listed in the NASB database as a 250-gallon lubricating oil tank that was removed in 1989. No revision to the text is necessary.

9. Section 3.1.2, CERCLA Responses on the Transfer Parcels, para 2: Parcel EDC-27, as shown on figure B-8, encroaches onto the Orion Street Skeet Range (OSSR) to the north and east. Since the OSSR is still under investigation, those portions within the skeet range should be removed from the proposed transfer however the remaining property and buildings can still be transferred.

Response: As shown on Figure B-8, no portion of the Orion Street Skeet Range lies within Parcel EDC-

27. The northeast corner of Parcel EDC-27 was altered to avoid such an overlap. 10. Section 3.1.4, CERCLA Covenant, para 1: The Fire Training Area-West within AIR 10 had

Tetrachloroethene (PCE) above the leaching to groundwater criteria under the RAGs so please provide the rationale for stating that no hazardous substances and no petroleum products or their derivatives are known to have been released or disposed of in excess of their respective threshold quantities.

Response: The highest concentration of PCE detected in soil was 0.68 micrograms per kilogram

(µg/kg), less than 1 part per billion. This value does not exceed the current EPA soil screening levels (SSLs) of 4.4 µg/kg (risk-based) or 2.3 µg/kg (MCL-based) for protection of groundwater. The Navy does not believe the threshold quantity for a release of PCE (100 lbs/45.4 kgs) was exceeded because all detected values in soil were less than one part per billion, and PCE was not detected in the groundwater sample. Also, the maximum detected value is orders of magnitude less than the MEDEP leaching to groundwater criterion of 2,700 µg/kg and the direct contact residential criterion of 1,000,000 µg/kg.

11. Section 3.2, Resource Conservation and Recovery Act, para 4: It is not clear under which programs

these investigations were performed and at least some of them were done under CERCLA in addition to the RCRA closure requirements. If these were performed under CERCLA it is not clear why it is included under this section. Please clarify/revise, as necessary.

Response: The investigations were not initially included in the CERCLA section because the areas

investigated were not officially designated as IR, MRP, or AOPI sites. The investigations were performed under CERCLA and requested by USEPA or MEDEP based on initial RCRA sampling results and/or on the historical information compiled as part of the RCRA closure research. The investigation discussions have been moved to the CERCLA section in the Final FOST.

12. Section 3.3.2, Petroleum Releases Originating on Adjoining Properties: “There are no other known or

suspected petroleum disposals or releases to the environment that originated within 200 feet of the Transfer Parcels.” MEDEP has noted and informed the Navy on numerous occasions starting in the Fall 2012 that a petroleum odor was evident from the storm grates on First Avenue on EDC-28 and across the road. On some occasions a sheen which seemed characteristic of petroleum not biological was visible in the ditch on the eastside of the road. It is unclear where the source might be located but the Old Fuel Farm is located upgradient although the most recent monitoring of groundwater for EPH and VPH were non detect. The Harpswell Pipeline runs just west of EDC 28 which [could] also be a potential source.

Response: December 2012 VOC sampling results for the three temporary monitoring wells installed on

Parcel EDC-28 during the former Building 586 investigation resulted in one trace-level detection of carbon disulfide at 0.26 ug/L which has an EPA tap water RSL of 72 ug/L and a MEG of 600 ug/L. No evidence of fuel contamination was observed. There were also no VPH or EPH detections in nearby monitoring wells MW-NASB-206 and MW-NASB-207 during the July 2010 ONFF groundwater monitoring event. These wells are on the east and west sides of Parcel EDC-28, respectively.

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Furthermore, no significant PID responses, staining or odors were observed during screening of the soil borings associated with the three temporary wells installed on Parcel EDC-28 in late 2012. The Navy initiated a limited investigation of the stormwater system as part of further investigation of the ONFF in November 2013 to try to determine the source of the petroleum odor. No samples were collected on Parcel EDC-28. Sediment and water samples were collected from Catch Basins 1 (CB-1) and 6 (CB-6) near the east and west sides of the northern end of the parcel, respectively. CB-6 is near the location of a former 900-gallon oil-water separator (OWS) and the Casco Bay (aka, Harpswell) Fuel Pipeline. A soil sample was collected from a direct push soil boring at the former OWS location. Sediment and water samples were also collected from the ditch on the north side of First Street at the storm sewer outfall structure and approximately 150 downstream from the structure. All samples were analyzed for PAHs, EPH, and VPH. Soil and sediment samples were screened against the most conservative of the Maine Remedial Action Guidelines (RAG) for Residential, Commercial Worker, Construction Worker, Park User, and Leaching to Groundwater criteria. Water samples were screened against Maine DEP stormwater criteria unless a Maine DEP stormwater criterion was unavailable for a given compound, in which case the Maine RAG for direct contact residential groundwater was used. The Navy is currently preparing a technical memorandum (projected draft by February 2014) for the former ONFF site assessment, including the findings of the storm sewer investigation. EPH and VPH were essentially not present in any of the samples except at very low concentrations in the ditch sediment. Excluding the ditch sediment, PAH constituents were rarely detected in most samples and when detected they were at threshold concentrations. The only PAH exceedance in ditch sediment was benzo(a)pyrene at 640 µg/kg at the outfall structure. This exceeds its Project Action Limit for soil/sediment of 260 µg/kg (the MEDEP RAG for Residential Soil). The presence of PAHs in the ditch could be partly attributable to runoff from First Street which is immediately adjacent and parallel to the ditch. Also, the detected concentrations of benzo(a)pyrene (640 and 120J µg/kg) are well below its Maine Rural Developed Background value for soil of 1.5 mg/kg (1,500 µg/kg). These sample results, along with the 2010 and 2012 groundwater monitoring results for wells on and near Parcel EDC-28, do not indicate that the parcel has been impacted by petroleum releases on the property or on adjacent properties, or from the former ONFF or the storm sewer system.

13. Section 3.5, Munitions and Explosives of Concern, para 2: It is notable that soil analysis for lead in

soil at the Mobile Shooting Range was Toxicity Characteristic Leaching Procedure (TCLP). TCLP is used for disposal purposes not for risk. Is this information correct that the analysis was TCLP and not Total Lead?

Response: Based on the August 25, 1993 letter from the former NASB to MEDEP; TCLP lead was the analytical procedure utilized. The Navy collected seven surface soil and two concrete surface wipe samples for total lead analysis in the vicinity of the former MSR location in December 2013. Lead results for all soil samples collected during this investigation were below the MEDEP RAGs (residential, commercial worker, construction worker and leaching to ground water) for soil, indicating that historical MSR operations have not adversely impacted surrounding surface soil conditions. The results for surface wipe samples collected from the outdoor concrete pad where the MSR was located indicate low levels of lead that do not represent an environmental hazard. The Navy issued the final technical memorandum describing the investigation and findings on January 30, 2014.

14. Table B-2:

a. Machine Gun Boresight Range: The table should briefly discuss the removal of the backstop/berm. It appears that the berm was intact in 1966, but in the 1970’s some work on the berms was visible on aerial photos but it appeared to be excavated around 1981.

Response: The requested discussion has been added to the table.

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b. POL Site 1, Old Navy Fuel Farm, Site Impact on Subject Property: Based on MEDEP observations of the storm drain on and adjacent to Parcel 328 there is the potential that the Old Navy Fuel Farm is impacting Parcel 328. (See response to comment 12 above.)

Response: See Response to Comment 12 regarding Parcel EDC-28.

c. Investigation and Remedial Action…: LTM has continued since 2000. The last report was in January 2011. Please correct.

Response: The discussion has been revised to state that LTM was conducted between 2000 and 2010.

d. IR Site 4, Acid/Caustic Disposal Pit, Investigation and Remedial Action…: To date only limited geophysical survey has been performed at Site 4. MEDEP suggests: “The Navy has conducted limited geophysical survey within Building 584 some additional work to more precisely identify the location of the former pit as part of the Data Gap Work Plan.” Please revise or clarify the last sentence.

Response: The suggested edits have been incorporated into the FOST.

e. AOPI Fire Training Area-West, Investigation and Remedial Action…: It should be noted in the Table that the exact location of the FTA-W could not be determined.

Response: The text has been edited as requested.

f. AOPI Fire Training Area-West, Site-Specific Restrictions:

Please consider the following change: “The Groundwater restrictions were recommended for the AOPI based on MEDEP concerns regarding the exceedance of leaching to groundwater criteria for PCE in soil.”

Response: See response to Comment 10. The maximum detected PCE concentration did not exceed

any of the leaching to groundwater criteria. However, Table B-2 has been edited to state that groundwater restrictions will be implemented basewide.

Based on the exceedance of PCE for leaching to groundwater the Navy should consider a notification of digging within the Fire Training Area-West AOPI and a restriction on excess soil similar to that for the Airport Parcel.

Response: See response to Comment 10. The maximum detected PCE concentration did not exceed

any of the leaching to groundwater criteria. Navy does not believe a soil restriction is necessary given the very low PCE concentrations detected in soil. The maximum concentration of 0.68 µg/kg does not exceed the current leaching to groundwater RAG of 2.7 mg/kg or the residential RAG of 1,000 mg/kg.

g. Former Building 233 Investigation Area Investigation and Remedial Action…: Please use the site

specific background which is preferable to State-wide background. Response: The text in Table B-2 was based on the June 2013 Draft Multiple Area Investigation

Technical Memorandum which cited the NASB background UPL concentrations for mixed soil. The text in Table B-2 has been revised to make this clearer and delete the reference to the state-wide background concentration.

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h. Building 611/555 Investigation Area, Investigation and Remedial Action…: Please note if it was site specific background and, if not, please correct.

Response: The summary in Table B-2 is based on the April 2013 Technical Memorandum, Soil and

Groundwater Investigation, Building 611/555 Area which cited the Maine background values in use at the time the report was prepared. Table B-2 has been updated to state the arsenic concentration at one location exceeded the NASB Upper Sand background UPL.

i. Building 611/555 Investigation Area, Site Impact on Subject Property: If the property is to be

transferred then appropriate restrictive language to protect workers must be developed and included in the Materials Management Plan.

Response: There already exists a PAH notification clause in Exhibit G-3, Clause 7 covering Parcels AIR-

8 & 11. The MMP is an agreement between the MEDEP and MRRA, and the Navy is not a signatory to that agreement.

15. Table B-4, EDC-15, Notes: See comment 12 above. Response: The discussion in the Notes column of Table B-4 regarding Parcel EDC-15 have been

updated to include the findings of the December 2013 soil and concrete sampling performed in the vicinity of the former Mobile Shooting Range as described in the response to Comment 13 above.

Lepage Environmental Services, Inc. P. O. Box 1195 •Auburn, Maine 04211-1195 • 207-777-1049

August 15, 2013

Mr. Paul Burgio & Mr. Todd Bober

Department of Navy

Base Realignment and Closure PMO-Northeast

4911 South Broad Street

Philadelphia, PA 19112-1303

Subject: July 2013 Draft Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8,

AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35,

EDC-45, and EDC-46 (Approximately 59.58 acres), Former Naval Air Station

Brunswick, Maine

Dear Mr. Burgio and Mr. Bober:

This letter is submitted on behalf of the Brunswick Area Citizens for a Safe Environment

(BACSE), regarding the July 2013 Draft Finding of Suitability to Transfer, FOST 2013-5,

Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35,

EDC-45, and EDC-46 (Approximately 59.58 acres), Former Naval Air Station Brunswick, Maine

Particular areas of concern and recommended actions are as follows:

1. Perfluorinated Compounds (PFCs). The August 2012 sampling conducted in a limited

number of wells within the Eastern Plume has revealed the presence of an “emerging

contaminant”, PFCs, in groundwater. The detection of PFCs in these wells will likely lead to

additional sampling to determine their actual extent with regard to the Eastern Plume. However,

BACSE is concerned that the occurrence of PFCs has not been investigated in a systematic way

elsewhere on the former base property and that parcels are being transferred without the presence

or absence of PFCs being determined. PFCs are a component of AFFF, the aqueous film forming

foam that was stored and used to fight fires at various locations around the base property. As an

example, comment number 3, below, outlines the problem specific to two parcels. Going

forward, what actions will the Navy take should PFCs be discovered on parcels that have already

been transferred?

2. Abandoned Fuel Pipelines. BACSE is very concerned that the potential hazards associated

with abandoned fuel pipelines on the former base property have not been adequately evaluated.

Therefore, unless there is documentation to the contrary, the pipelines should be assumed to

contain fuel and/or fuel residuals, and present risks normally posed by fuels, such as explosion,

fire, groundwater contamination, vapors, etc. For that reason, the areas above and around the

pipelines should be retained by the Navy until such time as the risks are documented and any

appropriate remediation has been implemented. Restrictions should also be put in place to

prevent excavation and construction in the area over-lying and immediately adjacent to any

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abandoned fuel pipelines. Restrictions should only be lifted for those sections of fuel pipeline

where appropriate remediation has reduced risk enough to allow unrestricted use. Unless

removed, the pipeline corridors should be excluded from this FOST.

3. Parcels AIR-8 and AIR-11. These parcels include Buildings 611 and 555, which have been

the subject of recent soil and groundwater investigation. The most recent results are reported in

the April 22, 2013, Draft Technical Memorandum, Soil and Groundwater Investigation, Building

611/555 Area, Former Naval Air Station, Brunswick, Maine. BACSE is concerned with several

specific contamination issues identified at the site that potentially affect future uses, and must be

addressed in the FOST and subsequent documents related to transfer and use of the property.

PAHs. Because the concentrations of several PAHs (polynuclear aromatic

hydrocarbons) exceed MEDEP Urban Background criteria, the soil needs to be managed

appropriately during any future excavation and construction activities at the parcels to

prevent exposure to contamination. A Navy soil management plan should be part of the

FOST.

PFCs. The one spill of AFFF that was reported in the April 2013 Draft Tech Memo is

described as discharging through the oil/water separator to the sanitary sewer system.

However, PFCs typically found in AFFF were detected in subsurface soil and

groundwater at the site, which could indicate that undocumented spills also took place

and/or AFFF was used at the area to extinguish fires.

Detection of PFCs in Upgradient Well. Furthermore, the detection of PFCs in the well

upgradient of Building 611 could indicate an additional source of PFCs that is affecting

these parcels. Additional investigation of PFCs is required and these parcels should be

excluded from this FOST.

Groundwater Restriction. The concentrations of PFCs in groundwater exceed

regulatory criteria at two well locations. Therefore, use of groundwater must continue to

be restricted in the future.

Well Abandonment. The Navy should consider properly abandoning monitoring wells

before the property is transferred.

Floor Drains. The Navy should consider sealing the floor drains in the buildings before

property transfer.

4. Parcel AIR-13. Parcel Air-13 includes Building 292, the Fire/Rescue Facility. Where was

AFFF stored at this site, and how was it handled, used, and disposed? Were there any spills or

intentional applications of AFFF at this location?

Figure B-6 shows an abandoned fuel pipeline crossing the parcel. The text on page 2 describes

two aviation gasoline pipelines that connected former Hangers 1, 2, and 3 to the Old Navy Fuel

Farm in the 1940’s as present on the parcel and believed to have been abandoned in place. Given

the apparent lack of documentation regarding if and how the fuel pipeline was abandoned, the

area overlying and immediately adjacent to the pipeline should not be transferred until sufficient

information is available to assess hazards and implement any necessary remedial action. Parcel

AIR-13 requires further investigation before inclusion in this FOST.

5. Parcel AIR-18. Table B-1 states that Building 231 is connected to the basewide potable water

supply, but the connection to the building is not shown on Figure B-7. Please add this

information to the figure, or add a footnote if the location of the connection is not known.

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6. Parcel ECD-28. Figure B-9 shows an abandoned pipeline running within fifty feet of the

parcel boundary. Is this part of the pipeline that connected the former base with the Harpswell

Fuel Farm? How was this pipeline abandoned, and what documentation is available?

7. Page 14, Section 3.3.2 Petroleum Releases Originating on adjoining Properties. This

section must be updated to include information from the June 2013 Draft Technical

Memorandum, Soil and Groundwater Investigation for Building 44-Fitch Avenue Magazine Area,

NMCB-27 (SEABEE) Compound Area, Former Building 233-Former Central Heating Plant

Area, Former Naval Air Station Brunswick, Brunswick, Maine. There is evidence of petroleum

contamination at sampling location B233-SB-06, which is adjacent to a former underground

storage tank location at the former Building 233 area. The Draft Tech Memo recommends a

limited groundwater investigation to determine the horizontal extent of petroleum contamination

in groundwater at the area, and MEDEP (see comment letter dated August 7, 2013) suggests test

pits and temporary microwells to confirm the extent of residual petroleum.

The former Building 233 site is located within two hundred feet of Parcels AIR-13, ECD-15, and

ECD-35. Please revise the FOST appropriately in all applicable passages to identify this

petroleum contamination location and the unknown (at this time) hazards and risks it poses to the

adjacent parcels. It would be advantageous if the work could be completed at the former

Building 233 location prior to the finalization of the FOST so that the potential risk to the

neighboring parcels can be determined and presented accurately in the final FOST.

Please do not hesitate to call if you have any questions.

Sincerely,

Carolyn A. Lepage, C.G. & P.G.

President

State of Maine Certified Geologist No. GE202

cc: Hard Copy: BACSE Archives (c/o David W. Chipman)

Mike Daly, USEPA

Curtis Memorial Library – Brunswick NAS Archive

Claudia Sait, MEDEP

Email Only: BACSE Internal Distribution (c/o Ed Benedikt)

Evan Barman, Watermark Environmental, Inc.

Tom Brubaker, MRRA

David W. Chipman, Harpswell Rep. to RAB

Denise Clavette, Brunswick Dept. Econ. Development

Jennifer Good, H & S Environmental, Inc.

Pamela Harting-Barrat, USEPA

Suzanne Johnson, RAB Co-Chair

Robert LeClerc, NAVFAC

Scott Libby, Topsham Rep. to RAB

Jeff Orient, TetraTech

Carol G. Warren, RAB/BACSE

102FOST2013-5 Draft 15.AG3

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Response to BACSE Comments Dated August 15, 2013, on the July 2013 Draft Finding of Suitability to Transfer FOST 2013-5

Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately 59.58 acres),

Former Naval Air Station Brunswick, Brunswick, Maine

Particular areas of concern and recommended actions are as follows: 1. Perfluorinated Compounds (PFCs). The August 2012 sampling conducted in a limited number of wells within the Eastern Plume has revealed the presence of an “emerging contaminant”, PFCs, in groundwater. The detection of PFCs in these wells will likely lead to additional sampling to determine their actual extent with regard to the Eastern Plume. However, BACSE is concerned that the occurrence of PFCs has not been investigated in a systematic way elsewhere on the former base property and that parcels are being transferred without the presence or absence of PFCs being determined. PFCs are a component of AFFF, the aqueous film forming foam that was stored and used to fight fires at various locations around the base property. As an example, comment number 3, below, outlines the problem specific to two parcels. Going forward, what actions will the Navy take should PFCs be discovered on parcels that have already been transferred? Response: The Navy follows Department of Defense Instruction number 4715.18 for addressing Emerging Contaminants (EC). This instruction allows the Navy to sample for, and when appropriate, to take action to reduce risks related to ECs. Typically, sampling for these emerging contaminants has been conducted at fire-fighter training areas or locations of large, known spills, and the Navy has begun using this approach by sampling at the FTA, the FTA-W, and B611/555 (known spill). The Navy will consider sampling at locations on previously transferred parcels should information become available to indicate that sampling is warranted at a future time. 2. Abandoned Fuel Pipelines. BACSE is very concerned that the potential hazards associated with abandoned fuel pipelines on the former base property have not been adequately evaluated. Therefore, unless there is documentation to the contrary, the pipelines should be assumed to contain fuel and/or fuel residuals, and present risks normally posed by fuels, such as explosion, fire, groundwater contamination, vapors, etc. For that reason, the areas above and around the pipelines should be retained by the Navy until such time as the risks are documented and any appropriate remediation has been implemented. Restrictions should also be put in place to prevent excavation and construction in the area over-lying and immediately adjacent to any abandoned fuel pipelines. Restrictions should only be lifted for those sections of fuel pipeline where appropriate remediation has reduced risk enough to allow unrestricted use. Unless removed, the pipeline corridors should be excluded from this FOST. Response: The Navy has provided notification of the presence of the pipelines in the FOST and in transfer deeds and has already transferred multiple areas that contained abandoned pipelines. Also the FOST contains provisions requiring the Grantee to notify the Navy regarding discovery of previously unknown contamination during any ground-disturbing activities, as described in Exhibit G. Therefore, pipeline corridors will not be removed from the FOST. Some additional information about the pipelines and references are cited below: The Casco Bay pipelines were drained and cleaned and pressurized with nitrogen when they were taken out of service in 1991 as reported in the following reference:

GZA,1997. Environmental Baseline Survey, Defense Fuel Support Point - Casco Bay

Terminal, Casco Bay to Brunswick Naval Air Station Pipeline, South Harpswell, Maine. GZA GeoEnvironmental, Inc., Portland, Maine. November.

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A portion of the pipeline within the NAS Brunswick property boundary near the Eastern Plume was investigated in June (GZA, 2000). Four test pits were excavated to assess the condition of the pipeline and the adjacent soil (GZA 2000). No evidence of petroleum contamination was observed during test pitting activities or subsequent laboratory analysis.

GZA, 2000. Results of Supplemental Evaluation of Pipeline Conditions, Response to DEP

Comments, Defense Fuel Support Point – Casco Bay to Brunswick Naval Air Station Pipeline EBS, South Harpswell, Maine. GZA GeoEnvironmental, Inc. Portland, Maine. August.

During removal of the Casco Bay Pipeline from privately-owned, off-base property, PAHs associated with the asphalt coating on the pipeline were detected in soil adjacent to the pipeline at multiple locations. The PAHs were further investigated by Tetra Tech (Tetra Tech, 2011). Using the test results and MEDEP risk assessment guidelines, the Navy and toxicologists from the Maine Department of Health and Human Services concluded no unacceptable risk to human health exists from the soil along the pipeline. Even though PAHs are in the soil, no unreasonable risk to human health remains, and soil remediation was not required.

Tetra Tech, 2011. Soil Investigation Report for Casco Bay Pipeline Decommissioning Project, Harpswell and Brunswick, Maine, prepared for the Naval Facilities Engineering Command Mid-Atlantic. April. The WWII era fuel pipelines that connected the Fuel Farm to Hangars 1, 2, and 3 are shown as “abandoned in place” on engineering drawings. The pipelines are nested in existing utility corridors and have reportedly been encountered during rerouting of other utilities. The location of the pipelines and the refueling pits to which they were connected were investigated as part of the Hangar 1, 2, and 3 AOPI investigation. No evidence of a significant release was found. The FOST provides notification of the presence of the pipelines. Unless there is evidence of a significant release, there is no further investigation planned for these pipelines. Tetra Tech, 2011. Technical Memorandum for the Groundwater Screening Investigation, Hangars 1, 2, and 3, Former Naval Air Station Brunswick, Brunswick, Maine. June. 3. Parcels AIR-8 and AIR-11. These parcels include Buildings 611 and 555, which have been the subject of recent soil and groundwater investigation. The most recent results are reported in the April 22, 2013, Draft Technical Memorandum, Soil and Groundwater Investigation, Building 611/555 Area, Former Naval Air Station, Brunswick, Maine. BACSE is concerned with several specific contamination issues identified at the site that potentially affect future uses, and must be addressed in the FOST and subsequent documents related to transfer and use of the property.

PAHs. Because the concentrations of several PAHs (polynuclear aromatic hydrocarbons) exceed MEDEP Urban Background criteria, the soil needs to be managed appropriately during any future excavation and construction activities at the parcels to prevent exposure to contamination. A Navy soil management plan should be part of the FOST.

Response: The requirement for management of soils due to the presence of PAHs in Parcels AIR-8 and AIR-11 is already included in Appendix G-3, as Clause 7, “Presence of Polycyclic Aromatic Hydrocarbons (PAHs) in Soil”.

PFCs. The one spill of AFFF that was reported in the April 2013 Draft Tech Memo is described as discharging through the oil/water separator to the sanitary sewer system. However, PFCs typically found in AFFF were detected in subsurface soil and groundwater at the site, which could indicate that undocumented spills also took place and/or AFFF was used at the area to extinguish fires.

3

Response: There were multiple backups of the OWS at this location in the 1980s and soils were removed in the early 1990s. However, there is no way to tie the PFOCs detections to a specific event. The sample results for PFOCs in soil were all below calculated screening values, and results in groundwater were low and just slightly exceeded provisional health advisories.

Detection of PFCs in Upgradient Well. Furthermore, the detection of PFCs in the well upgradient of Building 611 could indicate an additional source of PFCs that is affecting these parcels. Additional investigation of PFCs is required and these parcels should be excluded from this FOST.

Response: See response to Comment 1 above. The Navy will consider sampling at other locations should information become available at a future time that indicates sampling is warranted. The presence of PFOCs in groundwater is not reason to exclude the parcels from the FOST. There is a groundwater restriction that will prohibit exposure to groundwater.

Groundwater Restriction. The concentrations of PFCs in groundwater exceed regulatory criteria at two well locations. Therefore, use of groundwater must continue to be restricted in the future.

Response: Groundwater use will be restricted in this parcel, consistent with the basewide groundwater restriction.

Well Abandonment. The Navy should consider properly abandoning monitoring wells before the property is transferred.

Response: It is expected that the monitoring wells installed as part of the Buildings 611/555 study will eventually be abandoned; however, that decision has not been made at this time. There are no other wells known to be present.

Floor Drains. The Navy should consider sealing the floor drains in the buildings before property transfer.

Response: The Navy will consider sealing floor drains in these buildings in consultation with the Transferee. No decision has been made at this time. 4. Parcel AIR-13. Parcel Air-13 includes Building 292, the Fire/Rescue Facility. Where was AFFF stored at this site, and how was it handled, used, and disposed? Were there any spills or intentional applications of AFFF at this location? Response: AFFF was typically shipped in boxes packed with absorbent and stored in 5-gallon containers of concentrate. Expired containers of AFFF would have been disposed through the hazardous waste system as noted in the RCRA Closure Report, even though AFFF was not a hazardous waste. AFFF concentrate containers were not reported to have been stored in Building 292. The concentrate was used in tanks on the fire engines and Air Rescue Fire Fighter (ARFF) crash vehicles. Foam was generated on the trucks by mixing the concentrate with water using a foam induction system. No AFFF spills or releases were reported at Building 292. The Navy retains the right of access should information become available to indicate that sampling is warranted at a future time.

Figure B-6 shows an abandoned fuel pipeline crossing the parcel. The text on page 2 describes two aviation gasoline pipelines that connected former Hangers 1, 2, and 3 to the Old Navy Fuel Farm in the 1940’s as present on the parcel and believed to have been abandoned in place. Given the apparent lack of documentation regarding if and how the fuel pipeline was abandoned, the area overlying and immediately adjacent to the pipeline should not be transferred until sufficient information is available to assess hazards and implement

4

any necessary remedial action. Parcel AIR-13 requires further investigation before inclusion in this FOST.

Response: Please see response to Comment 2. 5. Parcel AIR-18. Table B-1 states that Building 231 is connected to the basewide potable water supply, but the connection to the building is not shown on Figure B-7. Please add this information to the figure, or add a footnote if the location of the connection is not known. Response: Building 231 is connected to a 12” water main that was added along the north side of the access road at the time the building was constructed. Drawing updates were not always included in the utility layer that the base used to create their figures, and therefore underground utilities are always noted as approximate on the figures; all utility locations should be field verified prior to excavation. It is recommended that construction drawings maintained at the Navy CSO office be consulted prior to any excavation. 6. Parcel ECD-28. Figure B-9 shows an abandoned pipeline running within fifty feet of the parcel boundary. Is this part of the pipeline that connected the former base with the Harpswell Fuel Farm? How was this pipeline abandoned, and what documentation is available? Response: The pipeline in question is the Casco Bay Pipeline. Please see response to Comment 2. 7. Page 14, Section 3.3.2 Petroleum Releases Originating on adjoining Properties. This section must be updated to include information from the June 2013 Draft Technical Memorandum, Soil and Groundwater Investigation for Building 44-Fitch Avenue Magazine Area, NMCB-27 (SEABEE) Compound Area, Former Building 233-Former Central Heating Plant Area, Former Naval Air Station Brunswick, Brunswick, Maine. There is evidence of petroleum contamination at sampling location B233-SB-06, which is adjacent to a former underground storage tank location at the former Building 233 area. The Draft Tech Memo recommends a limited groundwater investigation to determine the horizontal extent of petroleum contamination in groundwater at the area, and MEDEP (see comment letter dated August 7, 2013) suggests test pits and temporary microwells to confirm the extent of residual petroleum. The former Building 233 site is located within two hundred feet of Parcels AIR-13, ECD-15, and ECD-35. Please revise the FOST appropriately in all applicable passages to identify this petroleum contamination location and the unknown (at this time) hazards and risks it poses to the adjacent parcels. It would be advantageous if the work could be completed at the former Building 233 location prior to the finalization of the FOST so that the potential risk to the neighboring parcels can be determined and presented accurately in the final FOST. Response: Section 3.3.2 is intended to identify contamination on the subject property that has migrated from a release that occurred off the property. In this case, there is a petroleum release on the Building 233 parcel but not on the subject properties, so it is not included in this section. This concern was directly addressed in the FOST in the last column of Table B-2. The results of the Building 233 investigation were reviewed, and no impacts on the Transfer Parcels from the Building 233 parcel have been identified. The groundwater flow direction in the Building 233 investigation area is estimated to be to the southwest, and the Transfer Parcels are located north, east, and upgradient. A small area located on AIR-13 at a former Building 8 transformer pad was investigated for PCBs as part of the Building 233 investigation. However, PCBs were not detected in soil samples collected. Therefore, the FOST for these Transfer Parcels can proceed without concern of impact from the Building 233 parcel.


August 22, 2013


Department of Navy




Subject: Additional Comments Regarding July 2013 Draft Finding of Suitability to

Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-

15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately

59.58 acres), Former Naval Air Station Brunswick, Maine



(BACSE), to provide an additional comment regarding the July 2013 Draft Finding of Suitability

to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27,

EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately 59.58 acres), Former Naval

Air Station Brunswick, Maine . BACSE’s previous comments on the FOST were submitted to

you in a letter dated August 15, 2013, and the following additional comments are intended to

supplement those in the August 15th letter.

1. Identify Abandoned Pipeline Locations. The clear identification of abandoned pipeline

locations is necessary to maintain public safety. The Navy must ensure that all abandoned

pipelines on the former base property are clearly shown on all applicable and appropriate maps

and figures going forward. Furthermore, the Navy must ensure that all abandoned pipelines will

be covered under Digsafe.

2. Pipeline Coatings/Coverings. What are the abandoned pipelines coated or covered with? Do

any of these materials present a hazard to human health or the environment, either while

remaining buried or if they are exposed during excavation?

3. Investigate Petroleum at Parcel ECD-28. In its August 15th comment letter, BACSE had

requested additional information about the abandoned pipeline show on Figure B-9 as running

within fifty feet of the boundary of Parcel ECD-28. The FOST states that there are no known or

suspected petroleum disposals or releases to the environment that originated within 200 feet of

the transfer parcels. Therefore, BACSE was surprised to read the following in MEDEP’s August

16, 2013, comment letter (see comment number 12) regarding Section 3.3.2 of the FOST:

2

“MEDEP has noted and informed the Navy on numerous occasions starting in the Fall 2012 that

a petroleum odor was evident from the storm grates on First Avenue on EDC-28 and across the

road. On some occasions a sheen which seemed characteristic of petroleum not biological was

visible in the ditch on the east side of the road. It is unclear where the source might be located

but the Old Fuel Farm is located upgradient although the most recent monitoring of groundwater

for EPH and VPH were non detect. The Harpswell Pipeline runs just west of EDC-28 which is

also a potential source.”

It is unacceptable with potentially harmful consequences that information regarding petroleum

releases presented in the FOST is incomplete and misleading. Furthermore, Parcel ECD-28 is

certainly not safe for residential development and occupation at this time and must be withdrawn

from FOST 2013-5 until the source of the apparent petroleum contamination observed by

MEDEP can be identified and remediated.


Sincerely,


President



Mike Daly, USEPA


Claudia Sait, MEDEP



Tom Brubaker, MRRA






Robert Leclerc, NAVFAC




102FOST2013-5 Draft Add’lComment22.AG3

1

Additional BACSE Comments Dated August 22, 2013, on the July 2013 Draft Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-7, EDC-28,

EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately 59.58 acres) Former Naval Air Station Brunswick, Brunswick, Maine

1. Identify Abandoned Pipeline Locations. The clear identification of abandoned pipeline locations is necessary to maintain public safety. The Navy must ensure that all abandoned pipelines on the former base property are clearly shown on all applicable and appropriate maps and figures going forward. Furthermore, the Navy must ensure that all abandoned pipelines will be covered under Digsafe.

Response: A portion of the abandoned-in-place fuel pipeline that once connected the ONFF with Hangars 1, 2, and 3 is located on Parcel AIR-13 as shown on Figure B-6. The abandoned-in-place Casco Bay pipeline is shown on Figure B-3 but is not present on any of the transfer parcels. DIGSAFE contacts its member utilities (for example; gas, electric, fiber optics), who mark their utilities where they come into the work area, but often do not come onto private property. When conducting work near NASB utilities, the Navy always (1) contacts DIGSAFE because it is the law, (2) reviews construction/engineering drawings if available, and (3) procures a private utility locator if warranted. The underground utilities are always noted as approximate in FOST maps; all utility locations should be field verified prior to excavation. It is recommended that construction drawings maintained at the Navy CSO office be consulted prior to any excavation. 2. Pipeline Coatings/Coverings. What are the abandoned pipelines coated or covered with? Do any

of these materials present a hazard to human health or the environment, either while remaining buried or if they are exposed during excavation?

Response: See response to BACSE Comment 2 dated August 15, 2013. The Casco Bay pipeline is covered in a tar exterior coating and a fire resistant asbestos wrapping. It is not known how the pipelines in Parcel AIR-13 are coated but it is presumed that they are similarly coated. As discussed in the FOST Section 3.6 regarding presence of asbestos, it must be assumed that ACM may be present and it is the responsibility of the Transferee to ensure safety with respect to ACM. During removal of the Casco Bay Pipeline offbase, PAHs associated with the asphalt coating on the pipeline were detected in soil adjacent to the pipeline at multiple locations. The PAHs were further investigated by Tetra Tech in 2011. The Navy and toxicologists from the Maine Department of Health and Human Services concluded no unacceptable risk to human health exists from the soil along the pipeline. Even though PAHs are in the soil, no unreasonable risk to human health remains, and soil remediation was not required. 3. Investigate Petroleum at Parcel ECD-28. In its August 15

th comment letter, BACSE had requested

additional information about the abandoned pipeline show on Figure B-9 as running within fifty feet of the boundary of Parcel ECD-28. The FOST states that there are no known or suspected petroleum disposals or releases to the environment that originated within 200 feet of the transfer parcels. Therefore, BACSE was surprised to read the following in MEDEP’s August 16, 2013, comment letter (see comment number 12) regarding Section 3.3.2 of the FOST: “MEDEP has noted and informed the Navy on numerous occasions starting in the Fall 2012 that a petroleum odor was evident from the storm grates on First Avenue on EDC-28 and across the road. On some occasions a sheen which seemed characteristic of petroleum not biological was visible in the ditch on the east side of the road. It is unclear where the source might be located but the Old Fuel Farm is located upgradient although the most recent monitoring of groundwater for EPH and VPH were non detect. The Harpswell Pipeline runs just west of EDC-28 which is also a potential source.”

It is unacceptable with potentially harmful consequences that information regarding petroleum releases presented in the FOST is incomplete and misleading. Furthermore, Parcel ECD-28 is certainly not safe for residential development and occupation at this time and must be withdrawn from FOST 2013-5 until the source of the apparent petroleum contamination observed by MEDEP can be identified and remediated.

2

Response: December 2012 VOC sampling results for the three temporary monitoring wells installed on Parcel EDC-28 during the former Building 586 investigation resulted in one trace-level detection of carbon disulfide at 0.26 ug/L which has an EPA tap water RSL of 72 ug/L and a MEG of 600 ug/L. No evidence of fuel contamination was observed. There were also no VPH or EPH detections in nearby monitoring wells MW-NASB-206 and MW-NASB-207 during the July 2010 ONFF groundwater monitoring event. These wells are on the east and west sides of Parcel EDC-28, respectively. Furthermore, no significant PID responses, staining or odors were observed during screening of the soil borings associated with the three temporary wells installed on Parcel EDC-28 in late 2012. The Navy initiated a limited investigation of the stormwater system as part of further investigation of the ONFF in November 2013 to try to determine the source of the petroleum odor. No samples were collected on Parcel EDC-28. Sediment and water samples were collected from Catch Basins 1 (CB-1) and 6 (CB-6) near the east and west sides of the northern end of the parcel, respectively. CB-6 is near the location of a former 900-gallon oil-water separator (OWS) and the Casco Bay (aka, Harpswell) Fuel Pipeline. A soil sample was collected from a direct push soil boring at the former OWS location. Sediment and water samples were also collected from the ditch on the north side of First Street at the storm sewer outfall structure and approximately 150 downstream from the structure. All samples were analyzed for PAHs, EPH, and VPH. Soil and sediment samples were screened against the most conservative of the Maine Remedial Action Guidelines (RAG) for Residential, Commercial Worker, Construction Worker, Park User, and Leaching to Groundwater criteria. Water samples were screened against Maine DEP stormwater criteria unless a Maine DEP stormwater criterion was unavailable for a given compound in which case the Maine RAG for direct contact residential groundwater was used. The Navy is currently preparing a technical memorandum (projected draft by February 2014) for the former ONFF site assessment, including the findings of the storm sewer investigation. EPH and VPH were essentially not present in any of the samples except at very low concentrations in the ditch sediment. Excluding the ditch sediment, PAH constituents were rarely detected in most samples and when detected they were at threshold concentrations. The only PAH exceedance in ditch sediment was benzo(a)pyrene at 640 µg/kg at the outfall structure. This exceeds its Project Action Limit for soil/sediment of 260 µg/kg (the MEDEP RAG for Residential Soil). The presence of PAHs in the ditch could be partly attributable to runoff from First Street which is immediately adjacent and parallel to the ditch. Also, the detected concentrations of benzo(a)pyrene (640 and 120J µg/kg) are well below its Maine Rural Developed Background value for soil of 1.5 mg/kg (1,500 µg/kg). These sample results, along with the 2010 and 2012 groundwater monitoring results for wells on and near Parcel EDC-28, do not indicate that the parcel has been impacted by petroleum releases on the property or on adjacent properties, or from the former ONFF or the storm sewer system.


September 23, 2013


Department of Navy




Subject: More Additional Comments Regarding July 2013 Draft Finding of Suitability to

Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-

15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately

59.58 acres), Former Naval Air Station Brunswick, Maine



(BACSE), to provide more additional comments regarding the July 2013 Draft Finding of

Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15,

EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately 59.58 acres),

Former Naval Air Station Brunswick, Maine . BACSE’s previous comments and additional

comments on the FOST were submitted to you in letters dated August 15, 2013, and August 22,

2013. The following additional comments incorporate input from BACSE members and are

intended to supplement the comments in the August 15th and August 22

nd letters.

1. Identify and Manage Steam Line Locations. BACSE has previously commented on the

need for identification and management of abandoned pipelines in the August 22nd

comment letter

and wants to clarify that the clear identification of all steam line locations is also necessary to

maintain public safety. The Navy must ensure that all steam lines on the former base property are

clearly shown on all applicable and appropriate maps and figures going forward, and must ensure

that steam lines will be covered under Digsafe.

Furthermore, because the steam lines may be covered with asbestos-containing materials, their

excavation and handling must be managed properly. This will require appropriate land use

controls and restrictions or requirements in the FOST and any subsequent transfer and/or lease

documents to prevent exposure to hazardous materials.

This comment applies to Parcels AIR-13, ECD-10, ECD-45, and ECD-46 per the site maps in this

FOST, but there may be additional buildings or parcels BACSE is not aware of that also must be

addressed in a similar fashion.

2

2. Testing for PFCs at Former Western Fire Training Area. BACSE had expressed concern

in the August 15, 2013, letter that the occurrence of perfluorinated compounds (PFCs) has not

been investigated in a systematic way on the former base property (other than an initial round of

screening in the Eastern Plume), and that parcels are being transferred without the presence or

absence of PFCs being determined. PFCs are a component of AFFF, the aqueous film forming

foam that was stored and used to fight fires at various locations around the base property. The

August 15th comment letter mentioned several parcels specifically where AFFF may have been

stored, handled, or applied and where testing for PFCs would be appropriate. BACSE also

believes that the Former Western Fire Training Area within Parcel Air-10 should be tested for

PFCs.


Sincerely,


President



Mike Daly, USEPA


Claudia Sait, MEDEP



Tom Brubaker, MRRA






Robert Leclerc, NAVFAC




102FOST2013-5 Draft Add’lCommentsSteamline23.SP3

1

Response to Additional BACSE Comments Dated September 23, 2013, on the July 2013

Draft Finding of Suitability to Transfer, FOST 2013-5, Parcels AIR-8, AIR-10, AIR-11, AIR-13, AIR-18, EDC-15, EDC-27, EDC-28, EDC-34, EDC-35, EDC-45, and EDC-46 (Approximately

59.58 acres), Former Naval Air Station Brunswick, Maine The following additional comments incorporate input from BACSE members and are intended to supplement the comments in the August 15

th and August 22

nd letters.

1. Identify and Manage Steam Line Locations. BACSE has previously commented on the need for identification and management of abandoned pipelines in the August 22

nd comment

letter and wants to clarify that the clear identification of all steam line locations is also necessary to maintain public safety. The Navy must ensure that all steam lines on the former base property are clearly shown on all applicable and appropriate maps and figures going forward, and must ensure that steam lines will be covered under Digsafe. Furthermore, because the steam lines may be covered with asbestos-containing materials, their excavation and handling must be managed properly. This will require appropriate land use controls and restrictions or requirements in the FOST and any subsequent transfer and/or lease documents to prevent exposure to hazardous materials. This comment applies to Parcels AIR-13, ECD-10, ECD-45, and ECD-46 per the site maps in this FOST, but there may be additional buildings or parcels BACSE is not aware of that also must be addressed in a similar fashion. Response: The steam lines must be approached like any of the utilities or fuel pipelines. DIGSAFE contacts its member utilities (for example; gas, electric, fiber optics), who mark their utilities where they come into the work area, but often do not come onto private property. It is recommended that construction drawings maintained at the Navy CSO office be consulted prior to any excavation. When conducting intrusive work near NASB utilities, the Navy always (1) contacts DIGSAFE because it is the law, (2) reviews construction/engineering drawings if available, and (3) procures a private utility locator if warranted. The underground utilities are always noted as approximate in FOST maps; all utility locations should be field verified prior to excavation. The FOST notifies of the potential presence of asbestos in the former steam lines (and in abandoned fuel lines) in Section 3.6. In addition, prior to transfer, the Transferree must sign the Asbestos-Containing Materials Hazard Disclosure and Acknowledgment Form provided in Exhibit E of this FOST. All the FOSTs prepared for the Main Base at NASB have shown steamlines where they were known to have existed, had notifications regarding possible presence of ACM, and included the Asbestos-Containing Materials Hazard Disclosure and Acknowledgment Form for Transferree signature. 2. Testing for PFCs at Former Western Fire Training Area. BACSE had expressed concern in the August 15, 2013, letter that the occurrence of perfluorinated compounds (PFCs) has not been investigated in a systematic way on the former base property (other than an initial round of screening in the Eastern Plume), and that parcels are being transferred without the presence or absence of PFCs being determined. PFCs are a component of AFFF, the aqueous film forming foam that was stored and used to fight fires at various locations around the base property. The August 15

th comment letter mentioned several parcels specifically where AFFF may have been

stored, handled, or applied and where testing for PFCs would be appropriate. BACSE also believes that the Former Western Fire Training Area within Parcel Air-10 should be tested for PFCs.

2

Response: Groundwater was analyzed for PFOA and PFOS, as part of the “Site Investigation for Four Areas of Potential Interest and Supplemental Groundwater Characterization of Buildings 225 and 252” which included the investigation of the Fire Training Area-West (FTA-W). But since the results were non-detect, they were not included in the table of detected analytes in the Draft Report or discussed in the text. The groundwater data were included in Appendix B-2. Neither PFOA nor PFOS was detected in the groundwater sample from the FTA-W well at a detection limit of 2 ng/l. The report was finalized on January 10, 2014.