epa mtg - 10 nov 2010 - longwall report[1]
TRANSCRIPT
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1201 Cedar Grove Road
Media, PA 19063
610-356-1416www.schmidco.com
Experts in: Ecology
Wetlands
Environmental Regulation
Impact Assessment
Dr. James A. Schmid, President
Stephen P. Kunz, Senior Ecologist
http://www.schmidco.com/http://www.schmidco.com/ -
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The Citizens Coal Council
is a national alliance of
social and environmental justice grassroots groups andindividuals working to protect communities affected by
the mining, processing, and burning of coal through
advocating enforcement and strengthening ofenvironmental laws as they relate to coal.
Aimee Erickson, Executive Director724-222-5602
citizenscoalcouncil.org
mailto:[email protected]:[email protected] -
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BACKGROUND
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Pennsylvania Coalfields
Longwall Mining Area
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Typically 6 to 8 feet thick
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PA Coal Mining Statistics -
2009
SURFACE
UNDERGROUND
TOTAL
# of Mines
196 (80%)
48 (20%)
244
Coal Production 9,300,000 (16%)
48,679,000 (84%)
57,979,000*
(LWM: 37,985,000)(short tons)
* Peak production, 1918: 277,000,000
Pennsylvania: #4 State in total coal production (after WY, WV, KY)
#1 State in coal produced by Longwall
method
(None MTR)
(None by MTR)
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UNDERGROUND
COAL MINING
Room and Pillar
Surface impacts (subsidence)not expected
LongwallSubsidence (surface impacts) an integral part of method
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Back inthe day
Coal has beenmined in
Pennsylvania since
the late-1700s
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Employment in Coal Mining
Pennsylvania
Peak 1918 330,000*Today 2009 8,081**
* Pennsylvania Geological Survey
** US Dept. of Energy
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Enough coal is left (in pillars)
to prevent roof collapse
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Room and pillar is used
along gates/entries
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Longwall Mining
has been compared
to a
slow moving
earthquake
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Two examples of
trough subsidence
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Areas of likely pooling behind gates at arrows
Buffalo Creek (HQ-WWF)
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Stream pooling due to longwall subsidence behind gate
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Streams can bedewatered as cracks
extend all the way to
the surface
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Surface cracks from subsidence
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Stream water quality appeared degraded
as evidenced by higher conductivity
in
longwall mined streams.
In this study, there was lit tle evidence of
streams recovering from the dewatering
effects of longwall mining.
Temporally, there was no evidence ofstream recovery over the twelve-year
period of t ime
that had elapsed since
longwall mining occurred
Longwall mining resulted in a net loss of
approximately one-half of all headwaterstreams
in Marshall County, West
Virginia. Streams were particularly
impacted near the source .....
.... neither diversity nor longevity of the
macroinvertebrate community recovered
along the stream gradient. There was
no indication that the physical,
chemical, or biological impacts of
longwall mined streams recover
over time.
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Schmid &Company
Report
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Report can be read or
downloaded at:
Schmid & Company website
www.schmidco.comCCC website
www.citizenscoalcouncil.org/
Investigation began
autumn 2009
195 pages
http://www.schmidco.com/http://www.schmidco.com/ -
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PURPOSE
Determine current effectiveness of
the PA permit application, review,
and monitoring process in protecting
water resources
from the impacts of
longwall coal mining operations
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STUDY METHODOLOGY 75,000+
pages of PADEP regulatory files
3 Major Existing Longwall Coal Mines
Time period: 2007 through 2009
permit applications correspondence
background and ongoing monitoring data
public review and comments
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3 Longwall Mines = 137 square miles approved as of 2009
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Heretofore mostly avoided HQ and (recently recognized) EV Waters
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FINDING
Strong legal framework in PAfor the protection of water resources
(on paper)
State Constitution
Laws
Regulations
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SMCRA - Surface Mining Control andReclamation Act of 1977
MAJOR LEGISLATION
Bituminous Mine Subsidence and Land
Conservation Act of 1966
Act 54Amendments of 1994
Clean Streams Law of 1937
Dam Safety and Encroachments Act of 1978
Clean Water Act of 1972, Amendments 1977
FEDERAL
PENNSYLVANIA
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Bituminous Mine Subsidence and
Land Conservation Act(Mine Subsidence Act)
Act of April 27, 1966, P.L. 31, as amended, 52 P.S. 1406.1 -
1406.21
Several of the original purposes:
protection of the health, safety, and general welfare of the
people of the Commonwealth
providing for the conservation of surface land areas
aid in the preservation of surface water drainage
and generally to improve the use and enjoyment of such lands
The clear intent was to prevent environmental damagewhen allowing the underground mining of coal.
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FINDING
Protections on paper ......
... to ensure the protection of the hydrological balance
and to prevent adverse hydrological consequences ...
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FINDING
Permit Decisions Permit Enforcement(routine) (rare)
based on incompleteor inaccurate data
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TEN
YEARSAGO
2000
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REGULATORY
DISCONNECT
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Applicants not collecting or providingany baseline information
on surface water
features necessary to evaluate potential oractual impacts, as required by existing
laws and regulations.
PADEP-BMR issuing longwall miningpermits anyway.
Streams and wetlands being destroyed
without notice or mitigation.
Findings 10 years ago:
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FIVE
YEARSAGO
2005
The department shall compile and analyze the information contained in deep mine
permit applications, monitoring reports, enforcement actions, etc., and determine
the effects of deep mining on surface structures and features and on waterresources. and provide a report at five-year intervals.
Act 54 Section 18.1.
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2005
Walter N. Heine, Chairperson
The report de-emphasizes concerns based on
insufficient or no data. Stating that no data in thisstudy has been able to support that belief maytechnically be accurate, but
a lack of data is not
equivalent to disproving a hypothesis, which is the
conclusion the reader is led to.
If
available data is
insufficient to reach a valid conclusion, then the
solution is to address the data issue and ensure that
we are collecting the needed information.
The report acknowledges the need for regional
base level studies of wetlands to serve as abaseline.
Citizens Advisory Council
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If a wetland is
dried up,
and no regulator
notices,
is there an
impact?
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FIVE
YEARSAGO
2005
A revised PADEPTechnical Guidance Document
Surface Water Protection -Underground Bituminous Coal
Mining Operations
effective 8 October 2005
A glimmer of hope:
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TODAY
2010 Not only is detailedpremining information on
streams and wetlandsnow being required, it
actually is being provided
by mine applicants. This
is a great improvement
from a decade ago.
GOOD NEWS!
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ANTIDEGRADATION
Under the CWA, States are required to adopt an antidegradationpolicy and standards that meet minimum federal requirements.
Maintain and protect existing uses of all waters [floor] - fishable/swimmable standard
Maintain and protect uses and quality of high quality
waters
-
degradation allowed if SEJ
Maintain and protect outstanding resource waters (EV, in PA)
- no degradation
allowed
40 CFR 131.12
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PENNSYLVANIA ANTIDEGRADATIONPROGRAM
25 Pa. Code Chapter 93
Water Quality Standards
Recognizes EV and HQ waters as special protection
waters
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93.2. Scope.
(a) This chapter sets forth water
quality standards for surface
waters of this Commonwealth,
including wetlands.
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93.4c. Implementation of
antidegradation requirements.
(a)(1)
(i) Existing use protection shall be provided when the
Departments evaluation of information (including data gathered atthe Departments own initiative, data contained in a petition to
change a designated use submitted to the Environmental Quality
Board pursuant to 93.4d(a), or data considered in the context
of a Department permit or approval action) indicates that asurface water has attained an existing use.
and
(iv) The Department will make a final determination of existinguse protection for the surface water as part of the final approval
action.
[Existing use never investigated for mine applications,seldom for any PADEP permits statewide.]
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Technical Guidance Document 563-2000-655
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Previously:
Year-round flow in stream?
If not, no protection.
Stream Survey Protocol for Delineating
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Stream Survey Protocol for Delineating
Protected Stream Segments
Statewide Surface Water Assessment Program (SSWAP)
TGD
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PreminingBioassessment
Inventories 800
1,000 pages in length
Comprehensive documentation
regarding wetlands, streams, waterquality, and macroinvertebrate
communities
Example
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Civil & Environmental Consultants, Inc. (CEC)
Pittsburgh PA 986 p.
BAILEY MINE
EXPANSION AREA
(3,135 acres)
p
Example
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Biostation
p
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When field-checking actually
is done,mining industry data turn out to
be questionable.
Outright falsehood in wetland
reporting was encountered at
Vesta
(Schmid 1998), but
PADEP and Corps readilyapproved permits.
Instead of downgradingstreams, PADEP upgraded them
to Exceptional Value (highest
class), repeating and confirming
our work.
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Physical, chemical, andbiological data being
collected sufficientlycharacterize streams which
likely have existing useshigher than their
designated uses.
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BSW 18
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Characterizedphysical
habitat of
100-meterstream reach
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Habitat
Assessment
Evaluation
BSW 18
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Habitat
Assessment
Evaluation
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Enlow Fork Mine Expansion
Crafts Creek
(TSF)
STATIONBSW 18
5 biological metrics
Possibly EV or HQ?
Enlow Fork Mine
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Possible HQ or EV streams at Stations 15 and 18
Crafts Creek headwaters dewatered not expected
Potential dewatering of HQ Buffalo Creek headwaters
Buffalo Creek
(HQ)
Crafts Creek
(TSF)
18
15
Enlow Fork Mine
Expansion
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CRAFTS CREEK DEWATERING Enlow Fork Mine
Permit Expansion approved
January 2008
Ch. 105 Environmental Review not completed until February 2008 Flow loss/fish kill occurred November 2008
not predicted
Two other flow loss/fish kills by January 2010
(3 in 14-month period)
Required streamflow monitoring done quarterly since 2002
(HMRs)
Quarterly monitoring throughout flow loss period
no indications
Weekly/daily monitoring also done
but kept in Consols files
No change in plans for pending undermining of HQ headwaters
Adverse impact
=
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Cumulative Hydrologic Impact Assessment
(CHIA)
Done by PADEP for Enlow Fork Expansion
prior to permit approval
Effects on Groundwater?
- Wells and springs may be impacted quantitatively
[no further explanation]Effects on Surface Waters?
- No flow losses expected
[yet Crafts Creek dried up]
Material damage to hydrologic balance? Provide specifics.- see Modules 8 and 15 [no discussions there]
Discuss potential for adverse hydrological impacts.
-
Nothing provided
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POST-MINING ASSESSMENTS
WETLANDS
Required 12 months after undermining
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But cant determine that quickly
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Not being done anyway
STREAMS
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Not using premining assessments
COMPREHENSIVE DATA ARE BEING COLLECTED
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* To identify special protection waters andavoid/minimize impacts* To identify the nature and extent of cumulative
hydrologic impacts* To serve as a yardstick for restoring/replacing
individual water resources or the overall
hydrologic balance
DATA ARE NOT
BEING REVIEWED
DATA ARE NOT
BEING USED:
COMPREHENSIVE DATA ARE BEING COLLECTED
BUT
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1. Antidegradation: Designated and Existing Uses(pre-mining inventory and permit review)2. NPDES Permitting
(during mining):
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PADEP Basis for Effluent Limitations
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NPDES Monitoring and Discharge Limits
- Sample DMR (Discharge Monitoring Report)-
Monthly DMRs
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PADEP Followup/Follow Through
Issues/Problems with Stream Protection
in PADEP Longwall Coal Mine Regulation
PADEP NPDES Permit Effluent Limitations
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Prepared
by Bureau of Water Quality Management in
Southwest Regional Office, Pittsburgh
Engineering review to establish discharge limits for
each(?) outfall
Prepared always
for sanitary sewage, but erratic for
mine discharges (9/17 = 53% unavailable Emerald
)
Recommendations to California DMO permit writers
are seldom adopted (2/8 = 25% at Emerald
) for Part A
discharge limits for mine outfalls
Mine effluent discharge limits never derived from
actually attained uses, only from designated uses
Dramatically different format for sewage and mine DMRs
PADEP NPDES Permit Effluent Limitations
NPDES Monitoring and Discharge Limits
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Errors in stream name (3/15 = 20%at Emerald
), latitude and
longitude (6/15 = 40% at Emerald
)
in Part A for outfalls
enforceable? Monitoring required for a few parameters
varies by outfall
Part A specifies measurement units, sampling type,
frequency for most, but not all, parameters
Average, Maximum, Minimum Outfall-specific Limits set
in Part A but unlike PADEP Bur. Water Qual. Mgmt.recommendations (6/8 = 75% at Emerald
)
Permit Part B Standard Limits
ignored, superfluous (?)
Exceedances to be discussed quarterly by permittee --
cause, corrective measures, expected compliance
Dry weather versus precipitation event discharge limitsNever meaningful, no relevant data recorded
NPDES Monitoring and Discharge Limits
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Bl k DMR f E h O tf ll
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Provided by PADEP to permittee as guidance
for each months DMR format and content
Frequent conflict with Part A directives - neverquestioned or resolved (9/11 = 82% at Emerald
)
Inappropriate sampling frequencies for limits Inappropriate measurement units
No relationship to designated or attained uses Errors in latitude and longitude
Some add-in limits absent from Part A, some dont
Blank DMR for Each Outfall
Typical Blank DMR
L t/L f thi E ld
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Lat/Long for this Emerald
Mine
Outfall 13
contradict
Part A of the permit
Numeric values for iron
and manganese limits
contradict Part A of permit
DMR limits for aluminum
and osmotic pressure are
not in Part A of permit
No monitoring frequency or
sample types noted
Part A has limit for
settleable solids
(0.5 ml/l),
but Blank DMR has limits for
suspended sol ids
(35/70
mg/l)
No provision to record
floating solids or visible foam
No provision to indicate
weather conditions or torecord dry-weather effluent
Monthly Permittee DMRs
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Parameters, limits, units, frequencies often atodds with NPDES Part A and Sample DMR Data confusion with HMRs, anonymouslabs (Consol), no professed accreditation
DMR self-monitoring data often incomplete,
sampling optional, pre-printed results notdependent on actual sampling
Exceedances on DMRs seldom explained; Part
B exceedances never addressed
Exceedances not terminated for months, years
Some outfalls always report zero flow
Monthly Permittee DMRs
Completed DMR
Emerald Mine
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Emerald Mine
Outfall 013
Req.
for iron
matches
neither Blank DMR
nor Part A
Temperature
parameter
added, but not reported
No quarterly mention of
high specific conductance
(no limit set)
but Part B?
No mention of high sulfates
in excess of Part B (>500mg/l; or routinely >100 mg/l)Order of parametersrearranged alphabetically
Permittee investigating
osmotic pressure, monthafter month, per note inquarterly transmittal
Exceedance of Permit Limitations
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Exceedance of Permit Limitations
No Emerald mine outfall with credible, complete data set for the
27 months under review
One or more exceedances self-reported in data from 9/14 = 64%of Emerald outfalls with any monitoring data Some, but not all, exceedances of iron, manganese, osmotic
pressure acknowledged by permittee Nearly 150 sulfate
measurements at Emerald above Part B re-
porting threshold (often >1,000 mg/l); none acknowledged
Specific conductance
typically 10x local background data in
HMRs; often >2,000 mhos/cm at 8 outfalls; highest 16,300
at 016 and averaged >11,750 there in 2008-2009 DMRs
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Grimes Run at Emerald MineOutfall 017, 13 August 2008
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, g
(PADEP photo)
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PADEP Followup/Follow Through
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PADEP unaware of data gaps, wrong parameters, or
exceedances at mine outfalls (or chooses to ignore them) No professional competence, knowledge ofdiscrepancies in monitoring or violations ornonsensical, bogus data submitted
No PADEP mention of exceedances in DMR or
correspondence or enforcement files
No comparison of PADEP monthly random samples
with permittee monitoring data
No review of DMR data when investigating
complaints, fish kills
Sewage DMRs show perfect compliance butno PADEP inspection for 10 years
Laws are being broken or not enforced
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THE REAL PROBLEMS:
No incentive to minimize impacts
Highest quality waters are being destroyed
Communities are being put in danger from loss &
pollution of groundwater and drinking water supplies
Future generations are being denied safe, cleanwater that most people expect and take for granted Data just gather dust
PA Department of Environmental Pretense?
Indifference, political directive, corruption?
No oversight!
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Looking Forward
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Longwall mining is equally destructive to streams as
mountaintop removal, but less obvious
One consequence of slowing or stopping MTR wil l be
pressure to increase LWM. Impacts will increase as more EV/HQ waters are
subsided in Washington and Greene Counties
Marcellus shale gas threatens 54 counties, not 2; PADEPcurrently is as inept when faced by shale gas
as it was in 1994 faced by longwall mining
Official state policy is to keep environmental regulationto the minimum allowed by federal laws
These industrial extraction activit ies need oversight
Review of Clean Water Act 402 Permitting
for Surface Coal Mines by Appalachian States:
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The CWA entrusts EPA with overall responsibility to administer its
provisions, including protection of human health, water
quality, and the environment in coalfield communities
throughout Appalachia. This responsibility also includespreserving the long-term integrity of Appalachian
watersheds, which is important in protecting their ecological
condition and maintaining safe, clean, and abundant water forlocal communities.
for Surface Coal Mines by Appalachian States:
Findings & Recommendations
July 13, 2010
Water Permits Division
Office of Wastewater Management
U.S. Environmental Protection Agency1200 Pennsylvania Avenue N.W.
Washington D.C. 20460
SUMMARY
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THE END