Marshall Steam Station (8)

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ALINCDENR
North Carolina Department of Environment and Natural Resources
Division of Water Quality
Beverly Eaves Perdue Coleen H. Sullins
Governor director
May 20, 2011
MEMORANDUM
TO: Chuck Waklid, MO Matthews
FROM: Jay Sau e , Eric Flee
Dee Freeman
Secretary
SUBJECT: Environmental Sciences Section (ESS) Review of 316(a) and 316(b) Documents
This Memorandum serves to detail three specific changes in how the ESS reviews and tracks these
documents Existing conditions and their corresponding changes are detailed below
1) Traditionally, permittees interact with at least two NCDWQ sections during the servicing of
permits with Biological Monitoring Requirements ESS and the Complex Permitting Unit
Specifically, the permittee submits biological monitoring reports and proposed biological study
plans to the ESS for review ESS comments are then sent directly to the permittee with
appropriate copies to the DWQ permitting staff.
When dealing with specifics about the permit, the permittee coordinates directly with the Complex
Permitting Unit However, based on several interactions between Biological Assessment Unit
(BAU) staff and permittees, it has become obvious that this multi -contact approach for the
maintenance of these permits has caused confusion and frustration for the regulated community
Permittees are unsure where correspondence should be addressed and who to contact if they
have questions. Therefore, ESS is recommending that the permittee should address all
correspondence directly to the Complex Permitting Unit, including, but not limited to biological
monitoring reports and proposed biological study plans. The Complex Permitting Unit can then
forward these documents to the ESS for review The ESS will then provide consultation back to
the Complex Permitting Unit In essence, ESS will act as technical consultants to the Complex
Permitting Unit. This will eliminate confusion among the permit holders and will provide them with
a more predictable and user-friendly regulatory environment. The Complex Permitting Unit can
thea incorporate recommendations from the ESS with reviews from other agencies including EPA
oversight comments
2) Traditionally, ESS reviews of biological monitoring reports and proposed monitoring plans were
not systematically managed ESS reviews of biological monitoring reports and proposed
biological study plans will be henceforth executed following a standardized methodology
(attached). This methodology is based (in part) on EPA guidance regarding Balanced and
Indigenous Population (BIP) determinations but also represents an aggregate of ESS technical
expertise as it pertains to the review and interpretation of biological data and biological study
Environmental Sciences Section
1621 Mail Service Center, Raleigh, North Carolina 27699-1621
Location 4401 Reedy Cr Road Raleigh, North Carolina 27604
Phone. [phone] FAX. [phone] Customer Service. 1-677-623-6748
Internet wwev ncwater4uality org
An Equal Opportunity i Afiirmahve Achon Emolover
MAY 2 5 2011
NarthCarofina
Aahmally

design In short, a standardized review method will provide the regulated community with a high
degree of predictability and will also result in efficient reviews.
3) Until recently, ESS review of these documents excluded internal tracking. To ensure timely and
accountable reviews of these documents, an internal tracking database (attached) has been
developed This database will allow for a verifiable catalog of reviews and dates and will further
enhance internal administration of this process.
If you should have any questions regarding this document or the associated attachments please feel free
to contact Eric Reek
Cc. ,;eff Poupart
Xo,mAelnick-=
Sergei Chernikov

Review Document for Environmental Sciences Section Evaluations of
316(a) Balanced and Indigenous Populations Reports (BIP)
Introduction
Study plans constructed for the evaluation of biological communities associated with facilities requiring a 316(a)
thermal variance will be reviewed by the North Carolina Division of Water Quality (NCDWQ) based in part upon the
definitions below (1-2) These definitions are pursuant to the requirements of 40 CFR Part 125 Based on these
requirements, study plans and the subsequent monitoring reports submitted to the NCDWQ must contain the
monitoring components (for lakes and rivers) detailed in the benthos and fish community methodology sections
Variation on these monitoring components will be considered on a case-by-case basis Inquires regarding modification
of these components must be directed to Jay H. Sauber, Chief Environmental Sciences Section (ESS) at
iay.sauber(&ncdenr eov.
BIP determinaiaons will be made by ESS staff and subsequent recommendation_s,__"rey- ging the BIP determination will
be conveyed from ESS to the NPDES Unit within 45 business days of ESS receipt 'TW.:NPDES unit is ultimately
responsible for issuance of the final 316(a) thermal variance. Contact T 6 Belnic7[ m.belnickna ncdenr.sov),
Supervisor of the NPDES Complex Permitting Unit for additional guidance on the forigal issuance of 316(a)
-
thermal variances. All materials pertaining to the NPDES perm
if;neluding but not limilterl, ,to 316(a) Study
Plans, Fish Tissue Reports, and Environmental Monitoring Reports must be directed to tiie:iRPDES Complex
Permitting Unit at the following address:_
Mr. Tom Belni&.: ,,
Supervisor, NPDES Complex Fermitdng Unit
Complex Permitting Unit,1617 Mail Service CentelSal,e► h, NC 27699-1617
Although fish tissue monitoring and physical and cheriii.,cal,,water quality parameters are not specifically covered m the
below definitions, these data, if currently collected pursu 5to,existing permit requirements, are still required
components of the monitoring plan This document does not relie�v'kheapermittee frfl'm these monitonng requirements.
I- :..-
1) 40 CFR Part 125.71(c). Thetalanced, indigenousicommunity�synonymous with the tens:
"balanced, in ' r s popul ' " it the Act and Weans a biotic community typically characterized by
diversity, the sustai eljthrough cycl eeasonal changes, presence of necessary food chain
species and by a lac mi ollution to nt species".
2) 40 CFR PartdZ5.,T,1'(c�).;Balance digeno lations (Continued):
Y k'x b
_� balanced and rndrge�aous popu include historically non-native species introduced in
:' v.
w�connedion with a program oJwil agement and species whose presence or abundance results from
sirbst�ntia� irreversible "ronme modifications Normally, however, such a community will not
inclu"dle�species whose pr`e'sence or abundance is attributable to the introduction of pollutants that will be
eliminate`dl¢y compliance�,y all sources with section 301(6)(2) of the Act; and may not include species
whose presence. or abundbnce is attributable to alternative eJJluent limitations imposed pursuant to section
Methods
Benthic Macroinvertebrate Sampling Requirements (Reservoirs)
1) Where site conditions allow, aminimum of three (3) sampling stations are required One (1) station should be
uplake of the discharge, one (1) station near the discharge, and one (1) station downlake of the discharge.
Incorporating uplake, downlake, and near discharge sampling stations will allow the NCDWQ to accurately
evaluate the possible effects of the thermal discharge on the benthic macroinvertebrate community and will
allow a more effective e,,aluawn of any unacceptable damage done to these communities or populations or
the recovery of perturbed ones, and which may be the result of unacceptable environmental stress.
2) Benthic macroinvertebrate monitoring shall be annual. Annual sampling will provide the NCnta
WQ with da
of sufficient ieniporal resolution to assess benthic macroinvertebrate corrin-waity structure and trends
3) Benthic macroinvertebrate samples should be collected in the same month as previous collections to preserve
year-to-year data comparability.

4) At each station, if the burrowing mayflies of the genus Hexagenia spp or Ephemera spp are present,
quantitative assessments of the bottom substrate shall be made. Sediment from each of the three ponar
replicates per station shall be composited and passed through a USA Standard Testing Sieve (or equivalent
manufacturer) with percentages (by weight) of each sediment fraction retained on each respective sieve
reported The following sieve sizes (micrometers) are required 4, 6, 8, 12, 16, 20, 30, 40, 60, 80,100, 120,
140, 200, and 270. Hexagenia spp and Ephemera spp are sensitive to particle size and low dissolved oxygen
Quantitatively measuring the sediment size will help rule out possible confounding factors associated with
particle size and will allow NCDWQ to more accurately assess any possible effects the thermal discharge is
having on these communities.
5) A minimum of three ponar replicates per sampling station shall be collected A minimum of three ponar
replicates will provide sufficient sampling resolution to comprise a representative sample of the benthic
community at each sampling station
6) All taxa shall be identified to the lowest practical taxonomic level. Lowest practical taxonomic identification
is necessary in order to make accurate determinations of the community struotiu`e of the BMI community and
to detect possible changes in its structure over time typically characterizedvly diversity, the capacity to
sustain itself throu h cyclic seasonal changes, the presence of necessaryfood chains ecies and b a lack of
g Y g P,...�., P� Y
domination by pollutiomtolerant species. Please contact Enc Fleek (ei�c.fleekQncdenr.govl for guidance on
acceptable taxonomic identification for benthic macro
7) Relative abundances of all taxa shall be enumerated fc
(NCDWQ 2006) Specifically, 0-2 specimens are recd.
COMMON and 10 or more specimens are recorded as
taxa by these methods will provide the NCDWQ with,
pollution tolerant and pollution intolerant taxa withiiiKl
8) All historic benthic macroinvertebrate data shall be sul
IQ Standard -Operating Procedures
3-9 speeimensre recorded as
Enumerating liZ ic macroinvertebrate
and coarse -scale relative abundance data of the
e
wertebrate'=mmumty.
ted in conjunction with current data Including the
historic data will allow NCDWQ to more efficiently and ef&b1ye jyevaluate any possible changes in the
benthos community through time Please refer to Table 1 for guidance on how to submit these data. Although
this example is tabular, graphical formifis.are also acceptable pro*-ddd,all of the sampling years and
associated data are included.
9) All benthic macroinvertebrate samples musfbeected and identified*_ -staff affiliated with a North
Carolina Certified Biological Laboratory puisuari tci' A;NCAC 02H.1107=:1110
Benthic Macroinvertebrate Sampling Requiremients, fjA vers)`
1) Where site conditions allow, aminimum of three ') sampling stations are required. One (1) station shall be
upstream of the discharge, one (1) station shall bettear the discharge, and one (1) station shall be downstream
of the discharge. Incorporating upstream, downstreaatrb and near discharge sampling stations will allow the
NCDWQ to accurately evaluate the possible effects a 6�thermal discharge on the benthic
macromvertebrate community and will allow a more, ctive evaluation of any unacceptable damage done
to these communities or populations or the recovery of perturbed ones, and which may be the result of
unacce�,ftW6-ftnmental stress
2) Benthic macroinv,'et#ebrate monitoring shall be annual. Annual sampling will provide the NCDWQ with data
#o sufficient temporaLTSolution to assess the benthic macroinvertebrate community structure and trends.
I -f les should be cof . d in the same month as previous collections to preserve year-to-year data
4) All f Uh sliall be identifies tto the lowest practical taxonomic level Lowest practical taxonomic identification
is nece`sso z i order to made accurate determinations of the benthic macroinvertebrate community structure
and to det"I"ossible changes in its structure over time typically characterized by diversity, the capacity to
sustain rtselgh cy4l'ic seasonal changes, the presence of necessary food chain species and by a lack of
domination by pdIdtion'tolerant species Please contact Eric Fleek (eric.fleek(aa ncdenr.¢ov) for guidance on
accentable taxonomic identification for benthic macroinvertebrates.
5) All samples in streams and rivers shall be collected using the NCDWQ Standard Full -Scale collection
method (NCDWQ 2006). The Standard Full -Scale collection method will provide a comprehensive benthic
macroinvertebrate community assessment including both pollution tolerant and pollution intolerant
invertebrate taxa.
6) Relative abundances of all taxa shall be enumerated following NCDWQ Standard Operating Procedures
(NCDWQ 2006). Specifically, 0-2 specimens are recorded as RARE, 3-9 specimens are recorded as
COMMON and 10 or more specimens are recorded as ABUNDANT Enumerating benthic macroinvertebrate
taxa by these methods will provide the NCDWQ with fine and coarse -scale relative abundance data of the
pollution tolerant and pollution intolerant taxa within the invertebrate community,
7) All samples in streams and rivers shall require a habitat assessment (NCDWQ 2006). Habitat data at each
monitoring station must be reported concurrent with the benthic macroinvertebrate data Collecting habitat
data will help mitigate potential confounding instream and riparian habitat factors and will therefore better
enable NCDWQ to evaluate the possible effects of the thermal discharge on the invertebrate community

All historic benthic macroinvertebrate data shall be submitted in conjunction with current data Including the
historic data will allow NCDWQ to more efficiently and effectively evaluate any possible changes in the
benthos community through time Please refer to Table 1 for guidance on how to submit these data Although
this example is tabular, graphical formats are also acceptable pro"ided all of the sampling years and
associated data are included.
911 All benthic macroinvertebrate samples must be collected and identified by staff affiliated with a North
Carolina Certified Biological Laboratory pursuant to 15A NCAC 02H 1101- 1110
Fish Community Sampling Requirements (Reservoirs)
1) Where site conditions allow, a minimum of three (3) sampling stations are required One (1) station should be
uplake of the discharge, one (1) station near the discharge, and one (1) station downlake of the discharge
Incorporating upiake, duwniake, and i,ear discharge sampling stations will allow, the NCDWQ to accu,ately
evaluate the possible effects of the thermal discharge on the fisheries commWu—t' and will allow a more
effective evaluation of any unacceptable damage done to communities or populations or the recovery of
perturbed ones, and which may be the result of unacceptable environmen&I,stress
2) Monitoring shall be conducted biennially (every two years) in the spzing'azihall. Biennial sampling will
provide the NCDWQ with data of sufficient temporal resolution 41ssess th`e-5sfiery community structure
and trends within it through time and will result in two (2) con. letvassessmen`is during the five year permit
life cycle This level of effort will provide sufficient info
permit period and will help evaluate any community pupil+
3) Monitoring shall be conducted in the spring and in theta' I
specifically determine if there are seasonal effects,4the tau
fishery, will help contribute sufficient information to suppo
and will aid m the evaluation of any community population
4) Samples should be collected m the same month as previous
comparability
5) Relative weights of the fishery (by specs
the possible effects the heated discharge
and will enable the NCDWQ to more efi
populations or the recovery of perturbed ones; and
stress F
6) The proportional sto qty d relative stock de
species and non in enous fi _ cies shall be rep
a confident B %pol
tion li on a biotic co
to sustain itseclic si�sonal changes, the
of domination b,, ,cies. These d
rmatton-to support BIP detbrminations within the
anon changes with augmetitetTTigor.
Seasonal sampling will allow#t"ce NCDWQ to
'.harge on the commuriit}r structure of the
ierriiinations within theF=permrt period
with augmented confidence
ns to preserve year-to-year data
reported. Includifik.,11us data will provide information on
lithe metabolism ofdtdPs
pecies comprising the fishery
h{r s :
iluate any unaccepWe damage done to communities or
whie'li-i 'le Ytthhe^result of unacceptable environmental
nsity measurettients for recreationally important fish
orted. This information is necessary of NCDWQ to make
mmunity typically characterized by diversity, the capacity
V— of necessary food chain species and by a lack
ata will provide more comprehensive information on the
7) All fish —a As`haMbe identNits
est{ hWical taxonomic level possible Lowest practical taxonomic
identification is necessary ke accurate determinations of the fishery community and to detect
n* ossible changes in its strue,4In addition, these data will allow NCDWQ the ability to make a
rciinfident BIP determma: evaluation of the biotic community typically characterized by
dive si.Z, the capacity tom -Sough cyclic seasonal changes, the presence of necessary food chain
spec esand by a lack of domination by pollution tolerant species. Please contact Bryn Tracy
(brvn.ti&VAncdenr eov) f6r guidance on acceptable taxonomic identification for fish
81 All historic ash data shaII466 submitted in conjunction with current data Including the historic data will allow
NCDWQ to m41exefficiently and effectively evaluate any possible changes in the subject fishery through
time. Please refe%to'Zalile 2 for guidance on how to submit these data Although this example is tabular,
cgraptiical niaL iie aacceptablese provide_ l_1 of the sampling yers and associated data- are included
9) All fish community samples must be collected and identified by staff affiliated with a North Carolina
Certified Biological Laboratory pursuant to 15A NCAC 02H 1101-.1110
Fish Community Sampling Requirements (Rivers)
1) Where site conditions allow, a minimum of three (3) sampling stations are required. One (1) station should be
upstream of the discharge, one (1) station near the discharge, and one (1) station downstream of the
discharge Incorporating upstream, downstream, and near discharge sampling stations will allow the
NCDWQ to more effectively evoluate any tinacceptable damage done to corrminir;es nr populabons or the
recovery erapcrturbcu ones, arlu, which may be u,,w rLJWIt vfw.a+Ceptobl2 environmental
stress
2) All fish taxa shall be identified to the lowest practical taxonomic level possible. Lowest practical taxonomic
effort is necessary in order to make accurate determinations of the fishery community and to detect possible
changes in its structure over time. In addition, these data will allow NCDWQ the ability to make a confident
BIP determination based on an evaluation of the biotic community typically characterized by diversity, the

capacity to sustain itself through cyclic seasonal changes, the presence of necessary food chain species and
by a lack of domination by pollution tolerant species. Please contact Bryn Tracy (bryn.tracy(@ncdenr.Qov)
guidance on acceptable taxonomic effort for fish
3) At each station, habitat assessments following NCDWQ 2006(b) must be conducted and results reported
concurrent With the fish commumty results Collecting habitat data will help mitigate potential Confounding
factors that may be present at stations with poor mstream habitat and will therefore allow NCDWQ to more
accurately evaluate the possible effects of the thermal discharge on the fish community
4) All stream and river collections of fish shall be conducted following the methods detailed in NCDWQ
2006(b) This information is necessary of NCDWQ to make a confident BIP determination based on a biotic
community typically characterized by diversity, the capacity to sustain itself through cyclic seasonal changes,
the presence of necessary food chain species and by a lack of domination by pollution tolerant species. These
data will provide more comprehensive information on population dynamics of the biological community and
will allow the NCDWQ to assess the community structure of the fishery and trends within it over time.
5) All historic fish data shall be submitted in conjunction with current data Including the historic data will allow
NCDWQ to more efficiently and effectively evaluate any possible changq:m the subject fishery through
time. Please refer to Table 2 for guidance on how to submit these data.Alfitough this example is tabular,
graphical formats are also acceptable provided all of the sampling years aii&� sociated data are included
6) All fish community samples must be collected and identified by stA affiliateilivith a North Carolina
Certified Biological Laboratory pursuant to 15A NCAC 02H.1;101=;110.
r`
Table 1. Cataloochee Creek (SR 1395, Haywood County): `Historic Benthic Macriii;ttvertebrate Taxa
and Selected Community Metrics: (1990-2007). _ -
_
x"Uk-_
Table 2. Lake Jamesiffistorie- Fish Data. Total Number and Weight of Fish: 1990-1996.
1/24/91)
4/11/90
7/2.5/90-4J
2:3/51q,=�'
7/IiJ91
8/17/92
7/23/97
7/24/02
8/8/07
Order
Family
Scientific Name
5163
5220
5407
Y +1,506_ -'s '
5660
5992
7363
8888
10310
EP
AMEL.ETIDAE
AMELETUSUNEATUS
Name
3
Weight (kg)
Number
Weight
Number
Weight
Number
Weight
Number
BAETIDAE
ACENTRELLA SPP
Blue Tilapia
''I'gp "3,s�
282
M
i .�
218
10
10
3
196
259
ACERPENNAPYGMAEA
;"3'N
�=x -3
1
,, $5
r 3
1
3
LEPOMIS
Redbreast
357
67
125
46
322
61
400
76
367
69
BAETIS FLA VISTRIGA
Sunfish
104
3
10
3
10
BAETISPLUTO�;
Warrnouth
27
Ztl
"�y`<
�'�„„`-' �
;41
3
OS
29
30
17
08
GULOSUS
'
�
*'10?,Y7,P.>r�
BAETISTRICAUDATUS
10
3
z:3`�'4f
3
1
SD
3
SO
CENTROPTILU
DIP"'g4ffi GENT
;
�`
3
3
1
PLA U , t7B US GR
10
PROCLOEO RE
.,_'' 'S
3
PROCLOEON SRS_ �.
�•e fir" ,
x'""
3
;,FP3`EUOOCLOEON FRON
- _PSEL'(IiLYGiDE_D,NSPP
1
10
3
10
10
x"Uk-_
Table 2. Lake Jamesiffistorie- Fish Data. Total Number and Weight of Fish: 1990-1996.
4/14/90
4/14/90 1
4/18/92
4/18/92
4/5/94
1 4/5/94
4/17/96
1 4/17/96
4/2/98
4/2/98
Scientific
Common
Total
Total
Total
Total
Total
Total
Total
Total
Total
Total
Name
Name
Number
Weight (kg)
Number
Weight
Number
Weight
Number
Weight
Number
Weight
TILAPLA
Blue Tilapia
222
282
120
148
218
261
200
246
196
259
AURE4
AUREA
LEPOMIS
Redbreast
357
67
125
46
322
61
400
76
367
69
AURRUS
Sunfish
rEPOMiS
Warrnouth
27
L2
22
10
10
OS
29
09
17
08
GULOSUS

References Cited
40C.T?,Part l25.7l E.'---ton;C'---deofFederal Regi Iatio.nse-CF-R-,-mNational Archlve-,zm-d!ReenrdsAdministration.
http//ecfrgpoaccess.gov
NCDENIL 2007 North Carolina Division of Altlater Quality Admirustrative Code Section 15A NCAC 2b 0100. Procedures for
Assignment of Water Quality Standards. Environmental Management Commission, Raleigh, NC
http-//portal.ncdenr.org/c/docurneniLhbrary/getfile?folderld=285750&narne=DLFE-8513 pff
NCDWQ. 2006. Standard Operating Procedures for Benthic Macroinvertebrates Biological Assessment Unit Environmental
Sciences Section, Division of Water Quality, North Carolina Department of Environment and Natural Resources, Raleigh,
NC
NCDWQ. 2006(b) Standard Operating Procedures for Stream Fish Community Assessmertt. Biological Assessment Unit
Environmental Sciences Section, Division of Water Quality, North Carolina Depart&&nt of Environment and Natural
Resources, Raleigh, NC.
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