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2031782

S C S E N G I N E E R S

REPORT OF SURFACE EMISSION MONITORINGAND

METHANE MONITORING IN STRUCTURES

SUNRISE MOUNTAIN LANDFILL PROPERTY(720-ACRE PARCEL)

INCLUDING THENORTHEAST CANYON AREA,

EASTERN PERMIMETER AREA,AND WESTERN BURN PITS AREA

_/

• SCS ENGINEERS •

REPORT OF SURFACE EMISSION MONITORINGAND

METHANE MONITORING IN STRUCTURES

SUNRISE MOUNTAIN LANDFILL PROPERTY(720-ACRE PARCEL)

INCLUDING THENORTHEAST CANYON AREA,

EASTERN PERMIMETER AREA,AND WESTERN BURN PITS AREA

CLARK COUNTY, NEVADA

Prepared for:

Republic DUMPCo770 East Sahara Avenue

Las Vegas, Nevada 89104(702) 644-4594

Prepared by:

SCS ENGINEERS2702 North 44th Street, Suite 105B

Phoenix, Arizona 85008(602) 840-2596

May 26,2000File No. 10.199007.01.T3

Environmental Consultants 2702 North 44th StreetSuite 105BPhoenix, AZ 85008-1583

602.840.2596FAX 602.224.0572

SCS ENGINEERS

May 31,2000File No. 10.99007.01

Ms. Susanna Trujillo, Project CoordinatorU.S. EPA Region IX75 Hawthorne Street (WST-7)San Francisco, CA 94105-3901

Re: Report of Surface Emission Monitoring and Methane Monitoring in StructuresSunrise Mountain Landfill

Dear Ms. Trujillo:

On behalf of Republic DUMPCo, SCS Engineers is submitting two copies of the Report ofSurface Emission Monitoring and Methane Monitoring in Structures conducted betweenDecember 15,1999 and January 28, 2000. The submitted report is dated May 26, 2000 andcompletes subtasks 3.4.4.2 and 3.4.4.3 of the Final Landfill Assessment Work Plan datedFebruary 29, 2000.

If you have any questions or comments concerning this submittal, please feel free tocontact Mr. Alan Gaddy at (702) 734-5400.

Respectfully,

David J. Mezzacappa, P.E.Project Engineer

Stephen B. Smith, P.E.Project DirectorSCS ENGINEERS

cc: Mr. Alan J. GaddyRepublic DUMPCo770 E. Sahara Ave.Las Vegas, NV 89104

OFFICES NATIONWIDE

•SCS ENGINEERS —

TABLE OF CONTENTS

SECTION

1 0 SURFACE EMISSION MONITORING

1 1 Tntrnrli irti on

1 9 Field Activities1.3 Results

PAGE

1

113

2.0 METHANE MONITORING IN STRUCTURES 4

2.1 Introduction 42.2 Field Activities 52.3 Results 5

LIST OF TABLES

1 - Emission Monitoring Data

LIST OF DRAWINGS (DRAWINGS PROVIDED INBOUND SET SEPARATELY)

1 - Title Sheet2A - Monitoring Points (N10000 to N13850)2B - Monitoring Points (N13850 to N17850)2C - Monitoring Points (N17850 to N23000)3 A - Surface Methane Concentrations (^500 ppm)3B - Breathing Zone Hydrogen Sulfide Concentrations (^ 15 ppm)4A - Data Points 1 through 11404B - Data Points 1141 through 2078

LIST OF APPENDICES

A - Daily Equipment Calibration LogsB - Daily Surface Emission LogsC - Calibration Logs for StructuresD - Emission Logs for StructuresE - Barometric Pressure


1.0 SURFACE EMISSION MONITORING

1.1 Introduction

Surface emission monitoring at the Sunrise Mountain Landfill, which is located in ClarkCounty, Nevada, was performed as part of Task Item (d) of the Final Landfill AssessmentWork Plan (subtask 3.4.4.2, USEPA approved 12/02/99), dated February 29,2000.

As outlined in the Final Landfill Assessment Work Plan (Work Plan), surface emissionsmonitoring was performed for methane (Cfy) across the surface of the Sunrise MountainLandfill property (720-acre parcel), the Eastern Perimeter Area, the Northeast CanyonArea, and the Western Burn Pit Area. The monitoring was performed over the entirety ofeach of these areas since a definite waste boundary had not been established at the time ofmonitoring. The monitoring for methane was conducted using a Landtech SEM 500portable flame ionization detector (FID) equipped with a probe extension to allow themeasurement of methane concentrations just above (3 inches) ground surface. Inaddition, hydrogen sulfide (H2S) was monitored in the breathing zone (5 feet aboveground) for health and safety purposes using an RKI Eagle photochemical cell. Ifhydrogen sulfide readings in the breathing zone were at or exceeding 15 parts per million(ppm), or if methane readings just above ground surface were at or exceeding 500 partsper million, or in other cases if a surface crack was encountered, hydrogen sulfide wasalso measured just above the surface (3 inches). Any areas where hydrogen sulfideexceeded 15 ppm in the breathing zone were subsequently cordoned-off via specialflagging for safety.

Surface monitoring methodology described in 40 CFR, Part 60, Subpart WWW wasemployed to perform the surface scan for methane as outlined in the Work Plan. The Site

' grid system was employed to establish the serpentine walk path prescribed by 40 CFR,Part 60, Subpart WWW. A global positioning system (GPS) device was used to aid fieldpersonnel in walking the monitoring path, which essentially traversed the site in 30-meter-wide strips. Spot checks were also performed and readings recorded atapproximate 200-foot intervals coinciding with the site grid to provide additionalinformation. Any surface cracks observed along the monitoring path were noted andtheir position recorded.

The surface monitoring program's purpose is twofold. It provides information on surfaceemissions as well as information regarding surface cracks. This information can be usedto assist in evaluating cover integrity, unsafe areas high in hydrogen sulfide emissions,and waste limits.

1.2 Field Activities

Landfill surface emission monitoring was conducted at the Sunrise Mountain Landfillbetween December 15, 1999 and January 28, 2000. A 3-person crew monitored surfaceemissions across the entire surface of the Sunrise Mountain Landfill (720-acre parcel),the Eastern Perimeter Area, the Northeast Canyon Area, and the Western Burn Pit Area.

o


Specific personnel involved in the monitoring activities included Angel Ramos, SteveHavens, and Douglas Bell from Converse Consultants, and Jose Luis Davila and FrankLiu from SCS Engineers.

Each day prior to monitoring, the FID utilized to detect methane was tested andcalibrated in accordance with 40 CFR Section 60.755(d) and U.S. EPA Method 21,Section 4.4. The FID was operated according to manufacturer recommendations at alltimes. Calibration and startup testing are required at the beginning of each day ofsampling per EPA Method 21. Daily calibration logs were filled out to documentcompliance with this daily requirement and are included in Appendix A of this report.The RKI Eagle utilized to monitor for hydrogen sulfide was calibrated and operated permanufacturer's recommendations.

It should be noted that during calibration, the FID used on this project can either bezeroed manually to match the zero gas, or the instrument can be programmed so that thereading displayed during zero gas calibration can be internally set as corresponding tozero methane concentration. For example, in Appendix A, the calibration log forDecember 15,1999 shows that the zero gas reading on the FID was zero. This is becausethe instrument was zeroed during calibration. On the log for December 17, 1999,however, the zero gas calibrated reading was 3,535. In this instance the FID wasinternally set to read 3,535 as being zero for methane. Although these calibrationtechniques differ, they do not affect the accuracy or comparability of the resultingmonitoring data.

Per 40 CFR Section 60.755, surface emission monitoring was only conducted duringtypical meteorological conditions. Specifically, surface emission monitoring wasperformed while wind speeds were less than 5 miles per hour (mph) average and less than10 mph instantaneous. Measurements were made at the site by monitoring personnelusing a handheld anemometer. Barometric pressure readings for each day thatmonitoring took place are included after all field logs as Appendix E of this report.

At the beginning of each monitoring day, the GPS system was used to determine astarting point on the site grid system to ensure complete site coverage. Monitoring thenproceeded in a serpentine path across the site in 30-meter strips. The established 200-foot grid system was used to assist in maintaining the 30-meter monitoring path. At theintersection of the monitoring path with each 200-foot grid line, spot readings (readingsin a single location) were taken and recorded. Additional spot readings were also takenin some cases to ensure coverage or to follow surface features of interest (i.e. surfacecracks). Drawings 2A, 2B, and 2C show the spot monitoring points along the monitoringpath for different areas of the Site. As indicated in the table of contents of this report, alldrawings are in a bound, full-size set, separate from this report narrative and appendices.

The FID used to detect methane is equipped with an extension so that monitoring formethane was conducted 3 inches above ground surface. The FID tip was not inserted intocracks or voids, but was held 3 inches above a point where the surface would be if the

• SCS ENGINEERS •

imperfection did not exist. As methane monitoring was being performed at the surface,hydrogen sulfide monitoring was performed in the breathing zone (5 feet above ground).

Field logs were maintained during monitoring that included the monitored point'sposition (northing and easting based on the Site grid system), monitored gasconcentration, and any comments. Copies of the logs are contained in Appendix B. Anymethane measurements at or exceeding 500 ppm methane along the monitoring path wererecorded and the location staked/flagged (13 locations at or above 500 ppm were found).It should be noted that if a surface crack's start and endpoint locations were recorded andmethane readings at or in excess of 500 ppm were measured along the crack's length,only the starting point was counted as one of the thirteen points where methane was at orexceeded 500 ppm. Methane readings were also recorded at spot monitoring points (i.e.on the 200-foot grid), whether above 500 ppm or not. All recorded locations wereidentified using the GPS for accurate plotting on a site map. If hydrogen sulfideconcentrations in the breathing zone at or in excess of 15 ppm were found along themonitoring path, they were recorded, and the location staked/flagged (one such readingwas found). Monitoring personnel were instructed to immediately moved upwind of anyareas where hydrogen sulfide exceeded 15 ppm in the breathing zone. Hydrogen sulfidereadings in the breathing zone were also recorded at spot measuring points, whether inexcess of 15 ppm or not.

In addition to monitoring for methane at surface level and hydrogen sulfide at breathingzone level, surface cracks in the cover were logged as encountered and the data is shownin the tables on Drawings 4A and 4B.

1.3 Results

All methane readings at or above 500 ppm near ground level, and breathing zonehydrogen sulfide concentrations at or above 15 ppm are listed in Table 1. The locationsof these readings are shown in Drawing 3 A for methane and Drawing 3B for hydrogensulfide. The hydrogen sulfide map also serves as the "breathing zone" map. The areaaround the one instance where the concentration of hydrogen sulfide in the breathingzone concentration was at or in excess of 15 ppm was cordoned off with special flaggingfor health and safety purposes.

• SCS ENGINEERS —

Table 1. Emission Monitoring Data

Overall Point Number(see Drawings 4A and 4B)

1683564131424146914771708170917201777204320442045

Date(mm/dd/yy)

12/17/9912/21/9912/21/9901/04/0001/04/0001/04/0001/06/0001/06/0001/07/0001/07/0001/14/0001/14/0001/14/00

LocationNorthing

133031209512685

L 14330137571362913000130001290116102133611335313312

Easting

14156117901140613993141751471312200118401171413876140641406614113

CH4 ppmGS

600818

200011005031500500500

2250900856916715

H2S ppmBZ

18.0000000000000

GS

640.00.031.0

05.500000

20.015.83.5

SurfaceDescription

Surface crackSurface crackSurface crackSurface crackSurface crackSurface crackSurface crackSurface crackSurface crack

Gas ventGas ventGas ventGas vent

BZ - Concentration at breathing zone (approx. 5 ft)GS - Concentration above ground surface (approx. 3 in)

The tables shown on Drawings 4A and 4B contain a complete listing of all pointsmonitored for methane and hydrogen sulfide. Drawing 4A lists the first 1140 monitoredpoints while drawing 4B lists points 1141 through 2078. It should be noted that somecoordinates may vary slightly between the field logs and the drawings. This is due to acorrection factor that is applied after field measurement to refine the GPS field data. InDrawings 4A and 4B, monitoring points, which were located at surface cracks, are notedwith an "sc" designation. If a start or endpoint was located for the surface crack, it wasnoted with an additional "sp" or "ep" designation.

2.0 METHANE MONITORING IN STURCTURES

2.1 Introduction

Methane and hydrogen sulfide monitoring in structures was performed at the SunriseMountain Landfill as part of Work Task Item (d) of the Final Landfill Assessment WorkPlan (subtask 3.4.4.3, USEPA approved 12/02/99), dated February 29, 2000.

Two structures were identified for in-structure monitoring. The first is the Clark CountyMeteorological Station located within the 720-acre parcel boundary. The second is theDoppler Station located just off-site on the northwest perimeter of the 720-acre parcel.Both of these structures are shown on Drawing 3 A. Compliance or non-compliance withEPA's 1.25 percent methane and OSHA's 15 ppm hydrogen sulfide short-term exposurelimit standards was assessed.

The survey was conducted using a Landtech SEM 500 portable flame ionization detector(FID) equipped with a probe extension to allow the measurement of methaneconcentrations inside the structures. The probe was run along the baseboard in anyenclosed area to determine any measurable methane concentrations. An RKI Eagle

-SCS ENGINEERS —

photochemical cell was used to monitor any measurable hydrogen sulfide concentrationsat breathing zone level.

2.2 Field Activities

Methane and hydrogen sulfide monitoring was conducted at the Clark CountyMeteorological Station and the Doppler Station on December 29, 1999. A 3-person crewmonitored the methane concentrations across the entire baseboard inside all enclosedareas. The personnel involved in the monitoring activities included were Angel Ramosand Steve Havens from Converse Consultants, and Jose Luis Davila from SCS Engineers.

Prior to monitoring, the FID utilized to detect methane was tested and calibrated inaccordance with 40 CFR Section 60.755(d) and U.S. EPA Method 21, Section 4.4requirements. The FID was operated according to manufacturer recommendations at alltimes. Calibration logs were filled out to document compliance with this requirement andare included in Appendix C of this report. The RKI Eagle utilized to monitor forhydrogen sulfide was also calibrated prior to monitoring and operated per manufacturer'srecommendations.

2.3 Results

No readings exceeding the EPA's 1.25 percent methane and OSHA's 15 ppm hydrogensulfide short-term exposure limit standards were found. The logs recorded for themonitoring of each building are included in Appendix D of this report.

APPENDIX ADAILY EQUIPMENT CALIBRATION LOGS

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APPENDIX BDAILY SURFACE EMISSION LOGS

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APPENDIX CCALIBRATION LOGS FOR STRUCTURES

FIELD INSTRUMENTATION CAUBRAHON/MONITORIN6 LOGPROJECT NAME: C.f=- WIND DIRECTION/SPEED:PROJECT NUMBER: WEATHER:PERSONNEL:DATE:


MONITORING DOCUMENTATIONT»ne Reading Odors? Description/Location

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APPENDIX EBAROMETRIC PRESSURE

APPENDIX EBAROMETRIC PRESSRE'

Standard barometric pressure in

T\rt 4-*^

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12/15/9912/16/9912/17/9912/20/9912/21/9912/22/9912/23/9912/27/9912/28/9912/29/9912/30/991/3/001/4/001/5/001/6/001/7/001/10/001/14/001/28/00

BarometricPressure(inches ofMercury)

30.330.330.230.230.130.430.530.330.230.130.130.430.430.230.430.330.130.230.2

inches of mercury for Las Vegas, Nevada. Source: wunderground.com

OVERSIZE ITEM(S)

Due to the size of this item, it has been scanned separately.

See Document #______________ for scanned image(s).2032106

rpt of surface emission monitoring & methane monitoring … · 2016. 12. 20. · as methane...

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