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NC0069761
Beech Mountain / Pond Creek WWTP
NPDES Permit:
Document Type:
Permit Issuance
Wasteload Allocation
Authorization to Construct (AtC)
Permit Modification
Complete File - Historical
Engineering Alternatives (EAA)
Owner Name Change
Instream Assessment (67b)
Speculative Limits
Environmental Assessment (EA)
Document Date:
December 22, 1987
This document is printed on reuse paper - iggnore any
content on tine re'rerse side
MEMORANDUM
TO:
THROUGH:
FROM:
DIVISION OF ENVIRONMENTAL MANAGEMENT
22 September 1987
Steve Tedder
Jimmie Overton�v
Ken Eaglesomic,
David Lenatett
us
t.
SUBJECT: Biomonitoring of Ponds Creek/Beech Creek below the discharge
from the Beech Mountain WWTP, Watauga County.
BACKGROUND
The Beech Mountain WWTP (NPDES permit number NC0069761) discharges
to Ponds Creek in Watauga County. The plant h ndles only domestic waste and
has a permitted flow of 0.4MGD. The effluent may make up to 50% of stream
flow during drought periods, but the volume o.f the flow varies seasonally.
The greatest volume of effluent occurs during the winter, when the
maximu number of tourists come to the Beech Mountain area. This effluent
is disin ected using ultraviolet light. The discharge permit for this plant is
scheduled for r-eissuance in 1987.
Due to an administrative error, all of Pond Creek was classified as WS-III,
although only a small headwater segment is used for water supply. It is
likely tiat the middle and lower segments will be reclassified as C or
C-Trout waters. Pond Creek flows into Beech Creek, a small C-Trout stream.
There is some residential land use in the watersheds of both streams, but
the Pond Creek watershed has a greater proportion of development.
The Environmental Management Commission has received complaints from
the Friends of the Watauga River streamwatch group concerning the Beech
Mountain WWTP. A letter from Mr. George Dula listed a number of concerns
about water quality in Pond Creek below the Beech Mountain discharge. The
group used a Hach kit (supplied by TVA) to measure chemical parameters in
Beech and Pond Creek at sites just above the confluence of these two
streams. Measurements included temperature, pH, dissolved oxygen,
settleable matter, total chlorine, nitrogen and phosphorus (4 parameters)
and total hardness. Of particular concern were, a mesurement of 0.07 mg/1
total chlorine and 5.0 mg/1 dissolved oxygen in Pond Creek. Phosphorus and
nitrogen concentrations were elevated (relative to Beech Creek), but they
were not at a harmful level. Note that the Beech Mountain WWTP is not
designed to remove nutrients. The chlorine measurements (including a •
reading of 0..04 mg/1 in Beech Creek) were. puzz.l ing, as the. Beech Mountain.
effluent is not chlorinated. The determination of detectable chlorine in Don.
streams suggested that the Hach kits may have produced inaccurate
measurements of total chlorine.
The Friends of the Watauga River also complained of turbid water and a
"slightly musty odor" in Pond Creek and noted a "siltly coating" on the
stream bed. Few fish or invertebrates Were observed by the streamwatch
group in Pond Creek and they concluded .that "there definitely appears to be
stress on the water life in Pond Creek". They list both nonpoint source
runoff and the Beech Mountain effluent as possible sources of these
problems and asked for a thorough study of the stream prior to reissuance of
the p l ant's discharge permit.
In response to these citizen complaints, the Asheville field office
requested a biological survey of Pond Creek and Beech Creek. 0n 17-18
September 1987, the Biological Monitoring Group sampled two sites on Pond
Creek_(above and_below the WWTP) and two. sites on Beech Creek (above and
below the confluence with Pond Creek). This report will also utilize data
previously collected at two other streams in the Watauga River basin:
Buckeye Creek and the Upper Watauga River.
STUDY SITES (Figure 1, Table 1)
All study sites were small, high gradient streams, characterized by large
boulder substrate and small waterfalls. It is expected that these turbulent
streams would have a high aeration rate and high dissolved oxygen levels.
There was some sand/silt deposited at all sites, but much of the sediment
is probably washed out during high flow periods. The greatest amount of
sediment was noted in Pond Creek above the wastewater treatment plant. In
this area the substrate was usually "embedded", i.e., the interstial areas
were filled with sand. Sand had been deposited along the bank and in lateral
pools at this site and in Beech Creek below the confluence of Pond Creek.
Some fish were observed at all sites, and a small trout was accidentally
collected in the lower portion of Pond Creek.
Three of the sites were accessed via SR 1126 in Watauga County. Station
4 Was established in Beech Creek above this road crossing. Two other sites
were established about 0.2 miles upstream, above the confluence of Beech
Creek and Pond Creek: Station 3 on Beech Creek and Station 2 on Pond Creek.
Station 1 located just above the WWTP and was accessed via the Beech
Mountain area in Avery County.
METHODS
Benthlc macrolnvertebrates were collected using DEM's standardized
qua iative sa
mpling Thes. a wide variety of collection.
.ampling method - --is method us ..
techniques to inventory the aquatic fauna. The primary output is a species
list with some indication of relative abundance (Rare, Common, Abundant)
for each taxon. Both total taxa richness and the taxa richness of the most
intolerant (EPT) invertebrate groups can be used with DEM criteria to assign
water quality ratings. Unstressed streams and rivers have many species,
while polluted areas have fewer species. Water quality assessments also
may use the abundance of "pollution indicator" groups .
RESULTS
MACROINVERTEBRATES
EPT taxa richness indicated a Good -Fair rating for all sites on both Pond
and Beech Creek (Table 2). Greater emphasis has been placed on EPT taxa
richness than on total taxa richness, as these small streams would be
expected to have a lower diversity of invertebrates relative to the streams
and dvers normally sampled by DEM biologists. Comparison data (Buckeye
Creek and the Upper Watauga River) indicate that Pond Creek and Beech
Creek -have -a macroinvertebrate assemblage -that is normal for this region of
the 1'atauga River basin. Comparison data has been used only from small
streams that were similar in size to Pond and Beech Creeks.
Both EPT taxa richness and total taxa richness were remarkably constant
at st tions 1,3 and 4: Total=53-54, EPT=29-30. All summary parameters
were reduced at station 2, below the Beech Mountain discharge, but these
changes indicated only a slight decline in water quality. Relatively low
totals taxa richness values are due, in part, to a low diversity in the family
Chiranomidae (midges). Midges were particularly sparse in Pond Creek. The
low number of chironomids reflects both the small size of the streams and
the effects of sediment. Chironomidae are particularly susceptible to
sediment scour (Lenat 1983).
The dominant species were the same at all sites: Heptagen i a spp.,
Mal irekus nastatus, pipleetrona jnodestum, pol iphi lodes sp., and
Hydropsyche jnacleodi, This pattern again suggested that only slight changes
in water quality occurred between sites.
Nol pollution indicator species were found to be abundant at any of the
sites on Pond and Beech.Creeks. The lack of organic indicator species in
lower Pond Creek suggests that low dissolved oxygen is not a chronic
problem in this stream. Highly intolerant or unusual species occurred at all
sites, but were most likely to be found at upstream sites (1 and 3):
Drunella wayah: Rare at Station 1, Common at Station 4.
Rnithrogenia sp.: Rare at Station 1, Common at Station 3
Epeorus sp.: Common at Stations 1 and 4, Abundant at Station 3.
Pert inel la ephyre: Rare at Station 2
Hastaperla Drevis; Common at Stations 1, 3, and 4
Rhyacophi la_ torva:..Rare at_Station 1 _
Prlstinella jenkinae: Rare at Station 1
A characteristic dominant in unpolluted mountain stream is Epeorus spp.
This species was not dominant at any of the sites on Pond and Beech Creeks,
but it was most abundant at Station 3, above the effects on the Pond Creek
waters ed. It was absent at Station 2 (below the Beech Mountain effluent)
and only, common at the remaining sites. A reduction in abundance at lower
Pond Creek was also observed for Stenonema carlsoni and Hastaperla Drevis.
FISH
Although we did not sample the fish community of Pond or Beech Creek, a
limited amount of information is available from the NC Wildlife Resources
Commission (Bonner 1983). Beech Creek at SR 1 126 (DEM station 4) was
sampedon 19 August 1980. About 300 feet of stream were e l ectrof i shed,
yielding 17 brook trout, 1 brown trout and 1 blacknose dace. Trout density
was estimated_to be 6 pounds/acre. The low diversity of fish species is
typical of small, high -gradient trout streams. This investigation
recommended a B classification for Beech Creek, indicating that natural
reproduction is not expected during all years and the stream should be
stocked, with fingerling trout. Moderate silt and heavy sand deposits were
noted in this portion of Beech Creek, but the report also indicated good
-boulder cover for trout species.
SUMMARY AND CONCLUSIONS
All sites on Pond Creek and Beech Creek received a Good -Fair
bioclassiflcation and the same macroinvertebrate species were dominant at
all sites. Similar invertebrate communities have been observed in two other
nearby streams: Buckeye Creek and the headwater of the Watauga River.
However, the abundance of some intolerant species was reduced in lower
Pond Creek (below the Beech Mountain effluent). Residential development
has added sediment to both streams, with the greatest amount of habitat
change noted in Pond Creek. Sediment scour during high flow conditions may
reduce the abundance of macroinvertebrates in Pond Creek.
The minor changes observed in Pond Creek below the Beech Mountain
WWTP do not suggest any significant problems at this facility. The
discharge permit should be reissued without change.
REFERENCES.
Bonner, W.R. 1983. Survey and claslflcation of state managed -trout streams
in district seven. Federal aid in fish restoration project F24-S, Final
report. NC Wildlife Resources Commission.
Division of Environmental Management (DEM). 1984. Use attainability
surveys at Buckeye and Hyatt Creeks, North Carolina, September 1984.
Biological Monitoring Group. Unpublished report.
Division of Environmental Management (DEM). 1985. Watauga River biological
survey. Biological Monitoring Group, Memo.: 30 August 85.
Lenat, D.R. 1983. Chironomid taxa richness: natural variation and use in
pollution assessment. Freshwat. Invertebr. Biol. 2: 192-198.
cc: Lee Gabele
Randy Dodd
Peter Nathanson, Asheville field office
Jim Rogers, Beech Mountain Sanitary District, 510 Beech Mountain
Parkway, Banner Elk NC 28604
George T. Everett
Joe Mickey, Inland Fisheries
FIGURE 1
STUDY: PpND CREEK AND BEECH CREEK
RIVER BASIN: WATAUGA •
COUNTY: V4ATAUGA/AYERY
KELLERSV ILLE
SR 1126
SR 1125
BEECH
CREEK
• • • • • • • • • • • • OOOOO
• - - • • • • • CREEK
••••••••••••. OOOO
• • • • • • rn • • • • • • • OOO
' " • • • "Z • ' • • • OO .
. . . . . • . . . . . . . . .
• • • • • • - 07 - • • • • • • • •
• • • • • *I • • • • • • • • • •
• • • • • • -0 • • • • •
• I • • ' • • ' " • "
. . . 2 . . . . . . . . . . . . . .
. . . . ....... ... . • m " • •
• SR 1124
BEECH CREEK
BEECH MNT.
WTP
. . . . . . . . . . . .
• . " . ' . • . ' . *x . • . ' . ' .
" • ' • rn ' ' •
• • ' • - • - Z • - • -
• • • • • • u) • • - ' -
- • • • • . • -
- • - - • • • • -
• • • • • r r • • - - •
• • • •
. . . . . . . . . . . . . ....... . . . . . . . . . . . . . .
. . . . . . . . . . . . . . . .
SR 1127
CREEK
Table 1. Station descriptions, Pond Creek and
1987, Watauga County.
._...-__STATIONS
_
Pond Creek
LOCATION
WIDTH (11)
DEPTH (I1)
AVERAGE
MAXIMUM
CANOPY (%)
AUFWUCHS
BANK EROSION
SUBSTRATE (%)
BOULDER
RUBBLE
GRAVEL
SAND
SILT 1 _
COMMENTS
1
Above WWTP
3
0.2
1.2
90
Moderate
None
50
20
15-
15
Trace
Substrate
Embedded
Beech Creek, 17-18 September
• Beech Creek
2 4
Below WWTP, Above Pond Below Pond
3 2 5
0.2
0.8
90
Moderate
None
50
20
Trace
30
Trace
• 0.2
1.2
90
Moderate
None
40
20
10
30
Trace
0.2
1.0
90
Moderate
None
50
20
10
20
Trace
Sand
Deposition
in pools
Table 2. Taxa richness, by group, Pond Creek and Beech Creek. 17-18
September 1987, Watauga County.
Station:
Group
EPHEMEROPTERA
PLECOPTERA
TR I CHOPIITERA
COLE0PTERA
ODONATA
MEGALOPTERA
DI PTER,MI SC.
DI PTERa. CHIRON.
OL I GOCHAETA
CRUSTACEA
MOLLUSCA
OTHER
TOTAL TAXA RICHNESS
EPT TAX1A RICHNESS
EPT ABUNDANCE2
RATING 1
Pond Cr Beech Cr Comparison Data3
1 2 A UWR
12 9 9 .12 13 7
6 7 8 7 6 9
11 8 12 14 14
2 0 2 io 2 1
2 1 2 :2 1 1
1 1 1 1 0 0
7 5 5 5 6 5
10 7 11 14 14 12
2 3 2 1. 1 2
1 1 1 :1 1 1
0 0 0 0 2 0
0 0 0 0 1 0
54 42 53 54 61 52
29 24 29 30 33 30
129 94 123 137 175 127
G-F G-F G-F G-F G G-F
1 G-F=Go d-Fa 1 r, G=Good
2Abunda' t=10, Common=3, Rare=1; summed for all EPT taxa
3UWR=Upper Watauga River (Station 5), 13 August 85 (DEM 1985)
BC=BuckeYe Creek (Station 2), 17 April 84 (DAM 1984)
A PD NC I X 1' SP F r:_ S LIFT —FOP rit•, r. i R c K eTUDY
PCM:) 4'4D f : CCF' nEEKS. fC^TEr11'71 l.'?:• 7. R=RARF'•A=A?UN^A':T.
n
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►iPPr"f'!IX 1. SPFCIS LIST F-9R. Pr-, :^• CR-; u STUDY
PO',A'r7 :'•E 'CH C?FKS. SEPT7.1ER, °=RARL, f �".'.7'y• a=A%�„� �A'��T,
ORCFR
?LECGATERA
TRICHG?TERA
13P _CICs
ALL^CAPNIA SPA'
ALL9NARCYS SP°
rCCI2TIMA
XA"r'TAENEj.
STATION
01
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2'.:N7 2 1 'OND c 1 ;�r� C� C'
A 7) vC 1 .A TX/C 1 V:JVE 1 'YT `_7A
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+
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+
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+ + + +
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. 4PP.E'•JDIX I. SPr =S LIST; F P 0'0 CR.Ec7k ¶TUM+
PCA�C+ AN ','EECH CREEKS. SEFT'M► SEE, L ?- 7. ^=PARF, C 74mCN, A=A`:UMOANI .
3TATI`)N
12
24
1 1 1
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+ + +
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Afr-OIX 1. Sn'-FCIrS LIST -OR 0')Nn CREEV STUDY
PON'' A` n ''-rCH C2r7:<S. L1:?7. /APF, Cf''' h, A=Al'AINDA`,JT.
JR^ER
G1G'1ATA
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f v
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1 1126
r + + +
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+ + +
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+ + +
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^jc-, cHil 1 1 1 1
+ •• - + + +
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GR UP. 1
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(CCNTI"JrD1
AP?OIY 1. SP'CI?:S LIST Fr. PT.:R- CRVHK STUDY
PIN!) AND 'EFCH C;.F=KS. StPTF IR• 1937. ° AqE♦ C=C7Ns A=ASUNCANT.
JTPTERA:Cft y
I. °-17 J :� Lc. S
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+ + + +
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+ + +
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S °P 1 ? 1 1 F. I
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+ + + +
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1
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(CONTINUED)
APPE7T)IX 1. SPPCTES LIST F'J1 Pr''N= CREEK- STUOY
PON^ AND 9E=CH CREEKS. SEPTEERN 19 37. P=°ARE• C=CO'4MON♦ A=A!'UNDANT.
LR^ER
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CRUSTACEA',
1SeECICS
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SYR'HIOAE
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+
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1 n3
+
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+ +
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4r'V= 1 ArICVE 1 AEZVE 1 AT SR
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+ + +
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+
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PRISTINA
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DIVISION OF ENVIRONMENTAL MANAGEMENT
July 28, 1987
MEMORANDUM
TO: Arthur Mouberry
FROM: Randy Dodd P117,
THRU: Steve Tedder
SUBJECT:
Pond Creek Draft Permit
This memorandum is in response to Mr. George E. Dula's letter regarding
Pond Creek and the Pond Creek WWTP in Watauga County. Pond Creek (WS-III)
flows into Beech Creek (C-Trout). The WWTP discharges 0.64 miles above
Beech Creek.
The observations of the Friends of the Watauga River are appropriate as
degraded conditions in Pond Creek are apparent. With regard to comments
about elevated nitrogen and phosphorus levels in Pond Creek: since the WWTP
is not designed to remove these constituents and a golf course is upstream,
the results are not surprising. Biological observations are particularly
troubling.
Please note that Pond Creek is not currently classified as Trout Waters
(either by the EMC or Inland Fisheries). Therefore, pertinent requirements
are water quality standards for WS-III waters, and limits necessary to pro-
tect downstream (i.e., Beech Creek) classifications and uses.
Technical Support recommends a residual chlorine limit of 7 ug/l, which
is the level necessary to protect the standard in Beech Creek, assuming no
decay in Pond Creek.
If staff interprets regulations as requiring maintenance of the DO
standard for trout waters in Pond Creek, then an effluent limit of 4 mg/1
for DO would apply.
Please advise if questions.
RD:gh
cc: Forrest Westall
N.C. Environmental Management Commission
P.O. Box 27687
Raleigh, N.C. 27611-7687
Dear Commission Members:
Route 1, Box 233
Sugar Grove, N.C. 28679
D#d. of Environmental Mgt
July 19, 1987 Raleigh, N. G.
RE.CERIFID
JUL 2 ,JUL 2 3 1
,. rt7
TECHNICAL SERVICES BRANCH
RECErvjD
JUL 21 1987
This letter is in response to the proposed reissuance of the NPDES Permit Number
NC0069761 for the Beech Mountain Sanitary District, Pond Creek wastewater treatment
plant. Stream surveys were conducted on both Pond Creek and Beech Creek just up-
stream of their juncture, with data and conclusions listed below. All chemical
test data were obtained using Hach test kits provided to our StreamWatch group by
the Tennessee Valley Authority (TVA) to monitor water quality in the Watauga River
watershed.
TROUT WATER STDS. BEECH CR. POND CR. FACTOR OF
Pond Creek).
TEST PERFORMED
Temperature (°C) A 20 = 17 7 1 ,l
pH 6-9 r •.6 7.2 6 xl
Dissolved Oxygen (mg/L) 6.0 10 5 -2
....k5
Settleable Matter (mL/L) �� 0 0 (.d`�'"
Nitrate Nitrogen (mg/L) 10 0.1 0.8
Nitrate (mg/L) 0.5 3.5 8
Total Chlorine (mg/L) .002 0.04 0.07 1.8
Phosphate (mg/L) 0 1.7 1.7
Phosphorous (mg/L) 0 0.6 0.6
Ca/Mg Total Hardness (mg/L) 100 34.2 77.0 2.3
Beech Creek is r{ated as Class C-Trout from its source to the Watauga River and its
tributary, Pond Creek, is rated as Class A -II from its source to Beech Creek. As
indicated by my test results, Pond Creek is in the worse condition except for pH,
temperature, and settleable matter. The dissolved oxygen is twice as to
Creek, and is 1 mg/L below the minimum required for trout waters. Water hardness
(calcium and magnesium) was about a times greater in Pond Creek, approaching the
maximum allowable for water supplies. While the nitrate nitrogen and phosphate ��
were well within' the standards, they were considerably higher in Pond Creek, and 44'0,.
could indicate inadequately treated biological wastes. The higher readings for Ca/a
Mg hardness, nitrate nitrogen, and phosphate could also indicate fertilizer runoff, 11),"
especially in light of the golf course upstream of West Pond Creek (a tributary of kl�•..•,(`-�
Pond Creek).
B & C A -II Class C-Tr Class A -II DIFFERENCE
[1.)/v v er-- 3 / � 7Spy /pig -A
1113 JI:,
s d ��� PERMITS & ENGINEERING
et.6.44.44,-ft)
The readings found for chlorine are of special concern. The trout water stan-
dard is 2.0 ug/L (.002 mg/L) maximum. The concentration in Beech Creek was 20
times the standard and Pond Creek was 35 times higher than the standard. The
high chlorine levels in Pond Creek could be explained by chlorinated discharges
.from the wastewater treatment plant. ;,: a.
The water quality of Pond Creek appears very poor. Its water is turbid, with a
brown silty coating on virtually all of the stream bed, and has a slightly musky
odor. Very few scattered individual fish (only near the juncture with Beech
Creek), and only two types of macroinvertibrates were observed. No crayfish and
few surface insects were found. Beech Creek appeared much healthier with clear,
odor -free water, and very little siltation. Numerous fish, salamanders, and at
least 5 types of macroinvertibrates were observed.
There definaely appears to be stress on the water life in Pond Creek. Perhaps
siltation has killed the filter feeders and the fish no longer have a food source.
0r maybe the higher levels of pH, nitrate nitrogen, total chlorine, phosphate,
and Ca/Mg hardness (and lower dissolved oxygen) are causing the stress. My
recommendation to you is that, before the Pond Creek NPDES permit is renewed, a
thorough study of the stream should be conducted to determine what is impacting
it to such an extent.
Sincerely,
George E. Dula, Chairman
Friends of the Watauga River (StreamWatch)
1
c: Harvard 'Ayers, Sierra Club
Jim Mead, DWR-NRCD
Joe Mickey
Frank Sagona, TVA