U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
LAKE WALLENPAUPACK
PIKE AND WW€ COUNTIES
PENNSYLVANIA
EPA REGION III
WORKING PAPER No, 428
PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
An Associate Laboratory of the
NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
and
NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
&GPO 697-032
-------
REPORT
ON
LAKE WAL1ENPAUPACK
PIKE AND WAVNE COUNTIES
PENNSYLVANIA
EPA REGION III
WORKING PAPER No, 428
WITH THE COOPERATION OF THE
PENNSYLVANIA DEPARTMENT OF ENVIRONMENTAL RESOURCES
AND THE
PENNSYLVANIA NATIONAL GUARD
JUNE, 1975
603
-------
CONTENTS
Page
Foreword 1i
List of Pennsylvania Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 10
V. Literature Reviewed 16
VI. Appendices 17
-------
11
FOREWORD
The National Eutrophication Survey was initiated in 1972 in
response to an Administration commitment to investigate the nation-
wide threat of accelerated eutrophication to fresh water lakes and
reservoirs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concentrations,
and impact on selected freshwater lakes as a basis for formulating
comprehensive and coordinated national, regional, and state management
practices relating to point-source discharge reduction and non-point
source pollution abatement in lake watersheds.
ANALYTIC APPROACH
The mathematical and statistical procedures selected for the
Survey's eutrophication analysis are based on related concepts that:
a. A generalized representation or model relating
sources, concentrations, and impacts can be constructed.
b. By applying measurements of relevant parameters
associated with lake degradation, the generalized model
can be transformed into an operational representation of
a lake, its drainage basin, and related nutrients.
c. With such a transformation, an assessment of the
potential for eutrophication control can be made.
LAKE ANALYSIS
In this report, the first stage of evaluation of lake and water-
shed data collected from the study lake and its drainage basin is
documented. The report is formatted to provide state environmental
agencies with specific information for basin planning [§303(e)], water
quality criteria/standards review [§303(c)], clean lakes [1314(a,b)],
and water quality monitoring [§106 and §305{b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
-------
111
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condi-
tion are being made to advance the rationale and data base for
refinement of nutrient water quality criteria for the Nation's
fresh water lakes. Likewise, multivarlate evaluations for the
relationships between land use, nutrient export, and trophic
condition, by lake class or use, are being developed to assist
in the formulation of planning guidelines and policies by EPA
and to augment plans implementation by the states.
ACKNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Pennsylvania Department
of Environmental Resources for professional involvement and to
the Pennsylvania National Guard for conducting the tributary
sampling phase of the Survey,
Walter A. Lyon, Director of the Bureau of Water Quality
Management, Richard M. Boardman, Chief of the Division of Water
Quality, and James T. Ulanoski, Aquatic Biologist of the Division
of Water Quality, provided invaluable lake documentation and
counsel during the Survey, reviewed the preliminary reports, and
provided critiques most useful in the preparation of this Working
Paper series.
Major General Harry J. Mier, Jr., the Adjutant General of
Pennsylvania, and Project Officer Major Ronald E. Wickard, who
directed the volunteer efforts of the Pennsylvania National
Guardsmen, are also gratefully acknowledged for their assistance
to the Survey.
-------
IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF PENNSYLVANIA
LAKE NAME
Allegheny Reservoir
Beaver Run Reservoir
Beltzville
Blanchard Reservoir
Canadohta
Conneaut
Conewago (Pinchot)
Greenlane
Harveys
Indian
Naomi
Ontelaunee
Pocono
Pymatuning Reservoir
Shenango River Reservoir
Stillwater
Wallenpaupack
COUNTY
McKean, Warren, PA;
Cattaraugus, NY
Westmoreland
Carbon
Centre
Crawford
Crawford
York
Montgomery
Luzerne
Somerset
Monroe
Berks
Monroe
Crawford, PA;
Ashtabula, OH
Mercer
Monroe
Pike, Wayne
-------
41«25'—
LAKE
WALLENPAUPACK
LAKE
WALLENPAUPACK
Tributary Sampling Site
X Lake Sampling Site
7 Sewage Treatment Plant
9 . . . 1 ,8Km.
4M1.
Scale
Penn.
75*25'
75T15'
Map Location
75-05'
4115'-
-------
LAKE WALLENPAUPACK*
STORE! NO. 4229
I. CONCLUSIONS
A. Trophic Condition:
Survey data indicate that Lake Wallenpaupack is mesotropMc,
although the blue-green algal blooms that have only recently
occurred (see below) indicate this lake is becoming eutrophic.
It ranked seventh in overall trophic quality when the 17
Pennsylvania lakes sampled in 1973 were compared using a combi-
nation of six parameters**. Four of the lakes had less and two
had the same median total phosphorus, five had less and three
had the same median dissolved phosphorus, eight had less median
inorganic nitrogen, eight had less mean chlorophyll a_, and three
had greater mean Secchi disc transparency. Marked depression of
dissolved oxygen with depth occured at all four sampling stations
in July and October, 1973.
Survey limnologists noted submerged aquatic vegetation along
the east shore south of sampling station 1 but did not observe
algal concentrations during sampling visits in April, July, and
October of 1973 (the numbers of algae in the samples collected
at those times confirm the observations). However, in early
September, 1973, personnel of the Academy of Natural Sciences
* Table of metric conversions—Appendix A.
** See Appendix B.
-------
of Philadelphia investigated a blue-green algal bloom at the
lake (Anonymous, 1973). They found the dominant alga was
Anabaena circinalis, and total algal counts ranged from about
3,000 to 20,000 cells per milliliter at the 16 stations
sampled (mean count per station = 8,750 cells per milliliter).
Also, while algal blooms were absent in 1974, another blue-
green algal bloom occurred in the summer of 1975 (Ulanoski,
1975).
B. Rate-Limiting Nutrient:
The algal assay results indicate the primary productivity
of Lake Wallenpaupack was limited by phosphorus at the time the
sample was collected. The lake data indicate phosphorus limi-
tation in July as well but marginal nitrogen limitation in
October.
C. Nutrient Controllability:
1. Point sources—The phosphorus contribution of known
point sources accounted for 10.4% of the total load reaching
Lake Wallenpaupack during the sampling year. The major portion
of this load came from the wastewater treatment plant at Cove
Haven (6.6% of the total).
The present loading rate of 0.36 g/m2/yr is well below the
rate proposed by Vollenweider (Vollenweider and Dillon, 1974)
as a eutrophic rate (see page 15). However, the blue-green
-------
algal blooms noted by other Investigators (Anonymous, op. cit.)
is indicative of cultural enrichment. Therefore, point-source
reduction of phosphorus should be provided to slow the eutro-
phication of this lake.
2. Non-point sources—Non-point sources accounted for
89.5% of the mean annual total phosphorus load. Wallenpaupack
Creek contributed 47.1% of the total, Ariel Creek contributed
5.5%, Purdy Creek contributed 4.0%, and the unnamed creek (G-l)
contributed 11.0%. The remaining four tributaries collectively
contributed 5.0% of the load. Ungaged tributaries were estimated
to have contributed 11.6% of the total.
The nutrient export rate of Unnamed Creek G-l (209 kg P/km2/yr)
is over 12 times greater than the mean of the export rates of the
other tributaries of Lake Wallenpaupack (see page 15). This very
high rate and the low export N/P ratio strongly Indicate either
unsampled point sources impact this creek, or the phosphorus loads
from Cove Haven Resort were underestimated.
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
A. Lake Morphometry :
1. Surface area: 23.31 kilometers2.
2. Mean depth: 8.5 meters.
3. Maximum depth: 13.4 meters.
4. Volume: 198.135 x 106 m3.
5. Mean hydraulic retention time: 229 days.
B. Tributary and Outlet:
(See Appendix C for flow data)
1. Tributaries -
Drainage Mean flow
Name area .Ckm.2)* (m3/sec)*
Wailenpaupack Creek 391.1 4.8
Mill Brook 12.4 0.3
Kleinhans Creek 10.6 0.2
Unnamed Creek (D-l) 3.8 <0.1
Ariel Creek 40.4 0.5
Purdy Creek 21.2 0.4
Unnamed Creek (G-l) 4.4 <0.1
Spinner Brook 7.1 0.1
Minor tributaries &
immediate drainage - 76.2 3^6
Totals 567.2 10.0
2. Outlet -
Wallenpaupack Creek 590.5** 10.0
C. Precipitation***:
1. Year of sampling: 89.1 centimeters.
2. Mean annual: 97.8 centimeters.
t Ulanoski, 1975.
* For limits of accuracy, see Working Paper No. 175, "...Survey Methods,
1973-1976".
** Includes area of lake.
*** See Working Paper No. 175.
-------
III. LAKE WATER QUALITY SUMMARY
Lake Wallenpaupack was sampled three times during the open-water
season of 1973 by means of a pontoon-equipped Huey helicopter. Each
time, samples for physical and chemical parameters were collected
from four stations on the lake and from a number of depths at each
station (see map, page v). During each visit, a single depth-integrated
(4.6 m to surface) sample was composited from the stations for phyto-
plankton identification and enumeration; and during the first visit, a
single 18.9-liter depth-integrated sample was composited for algal
assays. Also each time, a depth-integrated sample was collected from
each of the stations for chlorophyll a_ analysis. The maximum depths
sampled were 14.9 meters at station 1, 11.6 meters at station 2, 11.3
meters at station 3, and 9.1 meters at station 4.
The lake sampling results are presented in full in Appendix D and
are summarized in the following table.
-------
A. SUMMARY OF PHYSICAL AND
CHEMICAL CHARACTERISTICS FOR LAKE UALLENPAUPACK
STORET CODE 4229
1ST SAMPLING ( 4/12/73)
4 SITES
2ND SAMPLING ( 7/23/73»
4 SITES
3ftO SAMPLING (10/ 3/73)
4 SITES
PARAMETER
TENP
N02*N03 (MS/L)
AMMONIA (MG/L)
KJEL N IMG/L)
IN006 N (MG/L)
TOTAL N
CHLRPYL A
SECCML (METERS)
RANGE
6.7
11.1
65.
8.2
10.
0.010
0.005
0.200
0.020
0.200
0.230
0.400
4.6
1.4
- 7.7
- 12.0
70.
8.9
16.
- 0.017
- 0.016
- 0.260
- 0.050
-. 0.400
- 0.300
- 0.6SO
9.1
1.5
MEAN
7.1
11.6
66.
8.7
13.
0.013
0.007
0.234
0.031
0.267
0.265
0.500
7.3
1.5
MEDIAN
6.9
11.9
65.
a. a
14.
0.013
0.006
0.2SO
0.030
0.300
0.270
0.500
7.5
1.5
RANGE
11.1
0.9
42.
5.9
13.
0.010
0.004
0.030
0.030
0.200
0.060
0.280
6.0
3.4
- 25.2
6.9
54.
7.0
26.
- O.OS3
- 0.019
- 0.2*0
- 0.310
- o.aoo
- 0.430
- 0.900
- 13.9
4.9
MEAN
20.4
4.9
49.
6.4
19.
0.018
0.008
0.095
0.124
0.400
0.219
0.495
8.B
4.3
MEDIAN
23.2
3.6
48.
6.5
IB.
0.014
0.007
0.070
0.070
0.400
0.130
0.460
7.7
4.6
RANGE
10.8
0.0
48.
6.3
14.
0.016
0.002
0.020
0.040
0.500
0.060
0.520
10.1
1.7
- 18.3
9.4
83.
7.0
- 29.
- 0.330
- 0.174
- 0.040
- 1.370
- 2.000
- 1.410
- 2.040
- 14.9
3.1
MEAN
16.8
5.9
55.
6.6
20.
0.052
0.024
0.026
0.284
0.906
0.310
0.932
12.8
2.2
MEDIAN
17.6
7.4
50.
6.5
21.
0.023
0.005
0.020
o.oao
o.aoo
0.115
0.825
13.1
2.0
-------
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
04/12/73
07/23/73
10/03/73
Dominant
Genera
1. Asterionella
2. Flagellates
3. Dinobryon
4. Cryptomonas
5. Meridion
Other genera
Total
1. Chrysophycean
flagellates
2. Aphanizomenon
3. Tabellaria
4. Anabaena
5. Cryptomonas
Other genera
Total
1. Anabaena
2. Flagellates
3. Fragilaria
4. Aphanizomenon
5. Asterionella
Other genera
Algal units
per ml
2,447
256
181
115
33
58
3,090
1,983
174
144
123
72
72
154
Total
739
-------
8
2. Chlorophyll £ -
Sampling
Date
04/12/73
07/23/73
10/03/73
Station
Number
01
02
03
04
01
02
03
04
01
02
03
04
Chlorophyll a
(iig/1)
8.5
9.1
6.5
4.6
6.4
6.0
9.1
13.9
11.6
10.1
14.9
14.7
Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P Inorganic N Maximum yield
Spike (mg/1) Cone, (mg/1) Cone, (mg/1) (mg/l-dry wt.)
Control 0.012 0.296 0.1
0.050 P 0.062 0.296 6.8
0.050 P + 1.0 N 0.062 1.296 18.5
1.0 N 0.012 1.296 0.1
2. Discussion -
The control yield of the assay alga, Selenastrum capri-
cornutum, indicates that the potential primary productivity
of Lake Wallenpaupack was relatively low at the time the
sample was taken. Also, a significant increase in yield
with the addition of phosphorus alone indicates that the
lake was limited by phosphrous at that time. Note that the
-------
addition of only nitrogen resulted in a yield no greater
than the control.
The lake data indicate phosphorus limitation 1n July
as well (the mean N/P ratio was 27/1) but marginal nitrogen
limitation in October (the mean N/P ratio was 13/1).
-------
10
IV. NUTRIENT LOADINGS
(See Appendix E for data)
For the determination of nutrient loadings, the Pennsylvania
National Guard collected monthly near-surface grab samples from each
of the tributary sites indicated on the map {page v), except for the
i
high runoff month of March when two samples were collected. Sampling
was begun in May, 1973, and was completed in April, 1974.
Through an interagency agreement, stream flow estimates for the
year of sampling and a "normalized" or average year were provided by
the Pennsylvania District Office of the U.S. Geological Survey for the
tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries were deter-
mined by using a modification of a U.S. Geological Survey computer
program for calculating stream loadings*. Nutrient loads shown are
those measured minus point-source loads, if any.
Nutrient loads for unsampled "minor tributaries and immediate
drainage" ("ZZ" of U.S.G.S.) were estimated using the means of the
nutrient exports, in kg/km2/year, at stations B-l, C-l, and D-l and
multiplying the means by the ZZ area in km2.
The operators of the Hideout, Pocono Plateau Christian Association,
Cove Haven, and Wallenpaupack Area High School wastewater treatment
plants provided monthly effluent samples and corresponding flow data.
* See Working Paper No. 175.
-------
11
Estimates of nutrient contributions by wild ducks were based on
the following numbers of waterfowl using Lake Wallenpaupack as
provided by the Pennsylvania Department of Environmental Resources
(Ulanoski, 1975):
Summer resident ducks 100
Migratory ducks 1,500
In calculating the nutrient loads, the following assumptions were
made:
1. Each wild duck contributed 0.45 kg total nitrogen and
0.20 kg total phosphorus per year (Paloumpls and Starrett,
1960).
2. Summer resident ducks are at the lake for six months
of the year.
3. Migratory ducks spend a total of one month per year at
the lake; i.e., 15 days during Spring migration and 15 days
during Fall migration.
-------
12
A. Waste Sources:
1. Known muncipal* -
Name
The Hideout
Cove Haven
Honeymoon
Resort
Wallenpaupack 1,000
Area High Sen.
Pocono Plateau 16**
Christian Assoc.
2. Known industrial -
Pop.
Served
494**
300
Treatment
act. sludge
act. sludge
Mean Flow
(mVd)
187.0
136.0
Receiving
Water
Ariel Creek
Unnamed Cr. (G-l)/
Lk. Wallenpaupack
act. sludge, 20.9
trickling
filter
act. sludge 6.0
Lk. Wallenpaupack
Taylor Creek/
Wallenpaupack Cr.
Name
Dairymen's
Co-op
League
Product Treatment
dairy ?
products
Mean Flow
(m'/d)
?
Receiving
Water
Wallenpaupack
Creek
* Treatment plant questionnaires.
** Population estimate based on flow of 0.3785 m3/capita/day.
-------
13
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs -
kg P/ . % of
Source yr total
a. Tributaries (non-point load) -
Wallenpaupack Creek 3,920 47.1
Mill Brook 185 2.2
Kleinhans Creek 110 1.3
Unnamed Creek (D-l) 50 0.6
Ariel Creek , 460 5.5
Purdy Creek 335 4.0
Unnamed Creek (G-l) 920 11.0
Spinner Brook 75 0.9
b. Minor tributaries & immediate
drainage (non-point load) - 965 11.6
c. Known municipal STP's -
Pocono Plateau Christian Assoc. <5 <0.1
The Hideout 40 0.5
Cove Haven 550 6.6
Wallenpaupack High Sch. 30 0.4
d. Septic tanks* - 245 2.9
e. Known industrial - Unknown ?
f. Wild ducks - 35 0.4
g. Direct precipitation** - 410 4.9
Total 8,330 100.0
2. Outputs -
Lake outlet - Wallenpaupack Creek 6,940
3. Net annual P accumulation - 1,390 kg.
* Estimate based on six campsites, three parks, and 808 lakeshore
dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
-------
14
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
kg N/ % of
Source yr total
a. Tributaries (non-point load) -
Wallenpaupack Creek 171,470 57.1
Mill Brook 6,695 2.2
Kleinhans Creek 6,025 2.0
Unnnamed Creek (D-l) 2,180 0.7
Ariel Creek 18,010 6.0
Purdy Creek 11,170 3.7
Unnamed Creek (G-l) 3,105 1.0
Spinner Brook 3,245 1.1
b. Minor tributaries & immediate
drainage (non-point load) - 42,725 14.2
c. Known municipal STP's -
Pocono Plateau Christian Assoc. 5 <0.1
The Hideout 325 0.1
Cove Haven 805 0.3
Wallenpaupack High Sch. 125 <0.1
d. Septic tanks* - 9,140 3.0
e. Known industrial - Unknown ?
f. Wild ducks - 80 <0.1
g. Direct precipitation** - 25,165 8.4
Total 300,270 100.0
2. Outputs -
Lake outlet - Wallenpaupack Creek 239,080
3. Net annual N accumulation - 61,190 kg.
* Estimate based on six campsites, three parks, and 808 lakeshore
dwellings; see Working Paper No. 175.
** See Working Paper No. 175.
-------
15
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km2/yr kg N/km2/yr N/P Ratio
Wallenpaupack Creek 10 438 44/1
Mill Brook 15 540 36/1
Kleinhans Creek 10 568 57/1
Unnamed Creek (D-l) 13 574 44/1
Ariel Creek 11 446 41/1
Purdy Creek 16 527 33/1
Unnamed Creek {G-l) 209 706 3/1
Spinner Brook 11 457 42/1
E. Yearly Loading Rates:
In the following table, the existing phosphorus loading
rates are compared to those proposed by Vollenweider (Vollen-
weider and Dillon, 1974). Essentially, his "dangerous" rate
is the rate at which the receiving water would become eutrophic
or remain eutrophic; his "permissible" rate is that which would
result in the receiving water remaining oligotrophic or becoming
oligotrophic if morphometry permitted. A mesotrophic rate would
be considered one between "dangerous" and "permissible".
Note that Vollenweider's model may not be applicable to
water bodies with short hydraulic retention times.
Total Phosphorus Total Nitrogen
Total Accumulated Total Accumulated
grams/m2/yr 0.36 0.06 12.9 2.6
Vollenweider loading rates for phosphorus
(g/m2/yr) based on mean depth and mean
hydraulic retention time of Lake Wallenpaupack:
"Dangerous" (eutrophic rate) 0.72
"Permissible" (oligotrophic rate) 0.36
-------
16
V. LITERATURE REVIEWED
Anonymous, 1973. Chemical and biological studies, Lake Wallenpaupack,
September 9, 1973 (for Lake Wallenpaupack Watershed Ecological
Association). Dept. of Limnology, Acad. Nat. Sci. of Philadelphia,
Paloumpis, A. A., and W. C. Starrett, 1960. An ecological study of
benthic organisms in three Illinois River flood plain lakes. Amer.
Midi. Nat., vol. 64, no. 2, pp. 406-435.
Ulanoski, James, 1975. Personal communication (lake morphometry;
waterfowl numbers; algal blooms). PA Dept. Env. Resources,
Harrisburg.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research. Natl.
Res. Council of Canada Publ. No. 13690, Canada Centre for Inland
Waters, Burlington, Ontario.
-------
17
VII. APPENDICES
APPENDIX A
CONVERSION FACTORS
-------
CONVERSION FACTORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x TO"4 = acre/feet
Square kilometers x 0.3861 = square miles
Cubic meters/sec x 35.315 = cubic feet/sec
Centimeters x 0.3937 = inches
Kilograms x 2.205 = pounds
Kilograms/square kilometer x 5.711 = Ibs/square mile
-------
APPENDIX B
LAKE RANKINGS
-------
LAKES RANKED BY INDEX NOS.
HANK LAKE CODE LAKE NAME
i 4224
2 4220
3 4222
4 4228
5 4227
6 4223
7 3641
8 4229
9 4221
10 4219
11 4204
12 4226
13 4213
14 4216
15 4225
16 4201
17 4207
LAKE NAOMI
BELTZVILLE DAM
HARVEY'S LAKE
STILLWATER LAKE
POCONO LAKE
INDIAN LAKE
ALLEGHENY RESERVOIR
LAKE WALLENPAUPACK
CANADOHTA LAKE
BEAVER RUN RESERVOIR
CONNEAUT LAKE
PINCHOT LAKE
PYMATUNING RESERVOIR
SHENANGO RIVER RESERVOIR
ONTELAUNEE DAM
BLANCHARD RESERVOIR
GREENLANE 0AM
INDEX NO
445
423
413
401
389
388
385
371
369
360
307
256
206
157
101
85
53
-------
PERCENT OF LAKES (rflTH HIGHER VALUES (NUMBER OF LAKES WITH HIGHER VALUES)
LAKE
CODE LAKE NAME
3641 ALLEGHENY RESERVOIR
4201 BLANCHARD RESERVOIR
4204 CONNEAUT LAKE
4207 GREENLANE DAM
4213 PITHATUNING RESERVOIR
4216 SHENANGO RIVER RESERVOIR
4219 BEAVER RUN RESERVOIR
4220 BELTZVILLE 0AM
4221 CANADOHTA LAKE
4222 HARVEYtS LAKE
4223 INDIAN LAKE
4224 LAKE NAOMI
4225 ONTELAUNEE 0AM
4226 PINCHOT LAKE
4227 POCONO LAKE
4228 STILLWATEH LAKE
4229 LAKE WALLENPAUPACK
MEDIAN
TOTAL P
56
13
44
6
0
19
94
88
50
63
100
81
25
31
38
72
72
( 9)
( 2)
< 7)
< I)
( 0)
( 3)
t 15)
< 14)
< 8)
( 10)
( 16)
( 13)
( 4)
( 5)
( 6>
< 11)
( ID
MEDIAN
INORG N
38
13
63
6
72
44
19
25
97
81
31
88
0
56
97
72
50
< 6)
( 2)
( 10)
( 1)
( 11)
( 7)
( 3)
( 4)
( 15)
( 13)
( 5)
( 14)
( 0)
( 9)
< IS)
( 11)
( 8)
500-
MEAN SEC
63 (
25 (
69 (
19 <
6 (
13 (
88 (
94 (
56 (
100 (
75 <
44 (
0 (
31 (
50 (
38 t
81 (
10)
4)
11)
3)
1)
2)
14)
IS)
9)
16)
12)
7)
0)
5)
8)
6)
13)
MEAN
. CHLORA
100 (
31 (
56 (
13 <
0 (
6 t
81 <
94 (
19 (
63 (
75 (
69 (
44 (
38 (
88 (
25 (
SO (
16)
5)
9)
2)
0)
U
13)
IS)
3)
10)
12)
11)
7)
6)
14)
4)
8)
15-
MIN 00
69
3
34
3
100
47
19
34
59
47
19
88
19
81
75
94
59
( 11)
( 0)
( 5)
( 0)
( 16)
( 7)
( 2)
( 5)
( 9)
( 7)
( 2)
t 14)
( 2)
< 13)
< 12)
< 15)
( 9)
MEDIAN
OISS P
59 (
0 1
41 1
6 1
28 1
28 <
59 <
88 (
88 1
59 (
88 4
75 1
13 (
19 1
41 I
100 <
59 <
1 8)
i 0)
t 6)
I 1)
• V
[ 4)
i 8)
: 13)
: 13)
8)
; 13)
; 12)
; 2)
I 3)
[ 6)
: 16)
: 8)
INDEX
NO
385
85
307
53
206
157
. 360
423
369
413
388
445
101
'256
389
401
371
-------
LAKE DATA TO BE USEU IN RANKINGS
LAKE
CODE LAKE NAME
3641 ALLEGHENY RESERVOIR
4201 BLANCHARO RESERVOIR
4204 CONNEAUT LAKE
4207 GttEENLANE UAM
^213 PYMATUNING RESEHVOIR
4216 SHENANGO RIVER RESERVOIR
4219 BEAVER RUN RESEHVOIR
4220 BELTZVILLE DAM
4221 CANAOOHTA LAKE
4222 HARVEY'S LAKE
4223 INDIAN LAKE
4224 LAKE NAOMI
4225 ONTELAUNEE 0AM
4226 PINCHOT LAKE
4227 POCONO LAKE
4228 STILLWATER LAKE
4229 LAKE WALLENPAJPACK
MEDIAN
TOTAL P
0.016
0.064
0.023
0.066
0.070
0.058
0.009
0.010
0.020
0.015
0.003
0.014
0.040
0.027
0.024
0.015
0*015
MEDIAN
INOKG N
0.380
1.300
0.1H5
1.475
0.180
0.340
0.835
0.815
0.130
0.160
0.520
0.135
2.150
0.245
0.130
0.1 80
0.250
500-
KEAN SEC
414.250
453.143
402.000
460.222
467.750
•463.555
384,833
362.444
436.000
338.000
400.222
443.333
470.667
453.000
438. BOO
449.000
394.583
MEAN
CHLORA
3.700
15.187
7.S67
24.011
56.333
26.800
5.183
4.856
19.167
5.967
5.211
5.533
11.783
13.950
4.980
18.233
9.617
15-
MIN DO
13.800
14.900
14.600
14.900
7.700
14.500
14.800
14.600
14.100
14.500
14.800
8.000
14.800
11.500
13.200
7.900
14.100
MEDIAN
DISS P
0.006
0.046
0.0.07
0.020
0.008
0.008
0.006
0.005
0.005
0.006
0.005
O.OOS
0.011
0.008
0.007
0.004
0.006
-------
APPENDIX C
TRIBUTARY FLOW DATA
-------
LAKE CODE 4229
TRIdUTARr FLO* INFORMATION FOH PENNSYLVANIA
WALLtNPAUPACX
1/27/75
TOTAL DRAINAGE AKEA OF LAKt(SO KM)
SUB-OKA IMAGE
TRIBUTARY AHEA(SO KMI
590.5
4229A1
4229A2
422961
4229C1
4229D1
4229E1
4229F1
4229G1
4229H1
4229ZZ
S90.5
391.1
12.4
10.6
3.B
40.4
21.2
4.4
7.1
9U.4
NOrtMALIiEO FLOWS (CMS)-
JAN
11.78
4.59
0.27
0.17
O.Q6
0.4U
0.26
0.03
0.07
5.83
FtB
11.04
5.32
0.31
0.19
0.07
0.57
0.37
0.04
0.09
4.ua
MAR
13.31
9.34
0.59
0.31
0.15
1.13
0.99
0.17
U.31
0.31
APR
14.78
9.91
0.62
0.34
0.16
1.19
1.08
0.20
0.37
0.91
MAY
10.34
6.23
0.37
0.22
0.06
0.68
0.48
0.06
0.12
2.10
JUN
9.12
3.40
0.19
0.13
0.04
0.34
0.17
0.02
0.03
4.81
JUL
8. 13
2.61
0.14
0.10
0.02
0.23
0.11
0.01
0.02
4.90
AUG
8.41
2.36
0.13
0.09
0.02
0.21
0.09
0.01
0.02
5.47
SEP
8.07
1.98
0.11
0.08
0.02
0.17
0.07
0.00
0.01
5.64
OCT
7.93
2.55
0.14
0.10
0.02
0.23
0.10
0.01
0.02
4.76
MOV
7.96
4.39
0.2S
0.16
0.05
0.45
0.27
0.03
0.06
2.29
DEC
9.37
5.38
0.31
0.19
0.07
0.57
0.37
0.04
0.09
2.35
MEAN
10.01
4.83
0.29
0.17
0.06
0.52
0.36
0.05
0.10
3.62
SUMMARY
TOTAL
SUM UF
DRAINAGE
AHEA OF
LAKE =
SUB-DRAINAGE AREAS =
590.5
589.4
TOTAL FLO*
TOTAL FLO*
IN =
OUT =
120.23
120.23
MEAN MONTHLY FLOWS AND DAILY FLOKS(CHS)
TRIBUTARY MONTH YEAH MEAN FLOW DAY
4229A2
S
6
7
8
9
10
11
12
1
2
3
5
6
7
a
<*
10
11
12
1
2
3
t.
73
73
73
73
73
73
73
73
74
74
74
73
73
73
73
73
73
73
V3
7t
74
74
74
14. -*7
22.71
23.28
15.43
4.08
6.60
0.05
1,5.12
27.44
24.92
21.01
9.b3
10.76
5.95
3.40
1.93
1.78
2.b3
12.16
8.76
5.95
7.65
10.76
19
now DAY
B.21
FLOW DAY
FLOW
19
9
23
19
17
22
25
22
20
17
15
19
9
23
20
22.34
26.96
23.90
lb.99
3.68
0.03
1.9U
1.8?
1.42
2.5S
7.6b
7.93
4.Hi
17.56
6.bl
-------
LAKE CODE 4229
THItHJTAHY FLO* 1NFOKMATION FOK PENNSYLVANIA
LAKE WALLENPAUPACK
1/27/75
MEAN MONTHLY FLOSS AND OAILY FLOhS(CHS)
TRJ9UTAHV MONTH YtAH MEAN FLO* DAY
4229B1
4229C1
4229D1
4229E1
5
6
7
e
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
5
6
7
8
9
10
11
12
1
2
3
4
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
0.59
1). 68
0.37
0.20
0.10
0.09
0.16
0.82
0.57
0.37
0.48
0.71
0.31
0.37
0.21
0.13
0.07
0.07
0.11
0.42
0.31
0.21
0.27
0.37
0.15
0.16 '
0.08
0.04
0.02
0.01 .
0.03
0.22
0.14
0.08
0.11
0.19
1.13
1.33
0.65
0.34
0.16 *
0.15
0.28
1.56
1.05
0.65
0.88
1.33
19
17
22
25
22
20
17
IS
19
9
23
20
19
17
22
25
22
20
17
15
19
9
23
20
19
17
22
25
22
20
17
15
19
9
23
20
19
17
22
25
22
20
17
15
19
9
23
23
FLOW DAY
1.16
0.21
0.15
0.10
0.10
U.07
0.14
0.45
(1.51
0.28
1.19
0.40
0.57
0.14
0.10
0.07
0.07
0.05
U.10
0.27
0.26
0.18
0.59
0.24
0.34
U.04
0.03
0.02
0.02
0.01
0.02
0.11
0.12
U.06
0.37
0.09
2.35
0.34
0.25
0.16
0.16
0,11
0.23
0.76
O.B2
0.48
2.46
0.74
FLOW PAY
FLOW
-------
LAKE CODE 4229
THIdUTAKY fLOW INFORMATION FOK PENNSYLVANIA
LAKE WALLtlNPAUPAC*
1/27/75
MEAN MONTHLY FLOWS ANU DAILY
TRIBUTARY MONTH YEAR ME.AN FLOW
4229F1
422961
4229H1
4229ZZ
7
8
9
10
11
12
1
3
4
5
6
7
K
9
10
11
12
1
2
3
5
6
7
6
9
10
11
12
1
2
3
5
6
7
8
9
10
11
12
1
2
3
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
73
73
73
73
73
73
73
73
74
74
74
74
DAY
0.99
1.2S
0.45
0.17
0.06
0.06
0.13
1.56
0.91
0.45
0.6S
1.27
0.17
0.24
0.06
0.1S
0.00
0.00
0.01
0.34
0.15
0.06
0.10
0.24
0.31
0.42
0.11
0.03
O.Ul
0.01
0.02
0.57
0.28
0.12
0.20
0.42
0.42
0.71
3.54
2.44
1.59
2.07
3.06
2.66
3.06
1,59
O.dfl
0.4tt
19
17
£2
25
22
20
17
15
19
9
23
20
19
17
£2
25
22
20
17
15
19
9
23
20
19
17
22
25
22
20
17
15
19
9
23
2o
19
17
22
2b
22
20
17
15
19
'•)
23
20
FLO* DAY
2.7B
0.19
0.12
0.06
0.06
0.04
U.10
0.68
0.74
0.31
2.97
0.54
0.74
0.02
0.01
0.00
0.00
0.00
U.Ol
0.10
0.12
U.U3
0.76
O.OB
1.19
0.0*
0.02
0.01
0.01
0.00
0.02
0.20
0.32
O.O/
1.30
U.15
0.34
0.62
2.04
2.15
1.25
5.44
I, It
5.21
O.BS
J.beS
FLO* DAV
FLOW
-------
APPENDIX D
PHYSICAL and CHEMICAL DATA
-------
STORET RETRIEVAL DATE 75/01/27
41 21 12.0 075 11 15.0
LAKE KALLENPAUPACK
42127 PENNSYLVANIA
DATE
FROM
TO
73/04/12
73/07/23
73/10/03
00010
TIME DEPTH WATER
OF TEMP
DAY FEET
13
13
13
13
13
13
11
11
11
11
11
12
12
12
12
12
45
45
45
45
45
45
10
10
10
10
10
50
50
50
50
50
0000
0006
0015
0025
0035
0049
0000
0005
0015
0025
0040
0000
0012
0025
0035
0045
CENT
6.9
6.8
6.8
6.7
6.7
6.7
25.0
24.7
22.7
16.3
11.1
18.3
16.0
17.6
12.4
10.8
00300
00
MG/L
12.0
12.0
12.0
11.9
11.9
8.2
7.2
3.6
0.9
9.0
9.4
6.4
0.0
0.0
11EPALES
00300
00
MG/L
12.0
12.0
12.0
11.9
11.9
8.2
7.2
3.6
0.9
9.0
9.4
6.4
0.0
0.0
00077
THANSP
SECCHI
INCHES
60
180
124
00094
CNOUCTVY
FIELD
MICROHHO
65
65
65
65
65
65
53
54
52
47
46
48
49
48
64
68
3
00400
PH
SU
8.70
8.80
8.80
8.80
8.70
8.70
6.80
6.60
6.30
5.90
5.90
6.90
6.80
6.50
6.40
6.50
00410
T ALK
CAC03
MG/L
14
14
15
14
15
12
13
15
15
16
21
15
14
14
22
25
2111202
0044
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.030
0.030
0.050
0.060
0.060
0.030
0.130
0.270
0.080
0.040
0.100
0.770
1.370
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.300
0.200
0.200
0.200
0.300
0.200
0.300
0.300
0.300
0.400
0.500
0.800
0.600
0.500
1.200
2.000
00630
KI02&N03
N-TOTAL
MG/L
0.200
0.210
0.200
0.200
0.210
0.220
O.OSO
0.050
0.050
0.160
0.160
0.030
0.020
0.020
0.020
0.040
00671
PHOS-DI5
ORTHO
MG/L P
0.006
0.016
0.007
0.005
0.006
0.008
0.006
0.005
0.005
0.010
0.019
0.008
0.005
0.004
0.112
0.174
DATE
FROM
TO
73/04/12
73/07/23
73/10/03
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
13
13
13
13
13
13
11
11
11
11
11
12
12
12
12
12
45
45
45
45
45
45
10
10
10
10
10
50
50
50
50
50
0000
0006
0015
0025
0035
0049
0000
0005
0015
0025
0040
0000
0012
0025
0035
0045
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
.012
.014
.012
.011
.012
.014
.010
.011
.013
.016
.037
.024
.019
.020
.140
.3 JO
UG/L
8.5
6.4
11.6
-------
STORE! RETRIEVAL DATE 75/01/27
422902
41 25 40.0 075 12 45.0
LAKE WALLENPAUPACK
42127 PENNSYLVANIA
DATE
FROM
TO
73/04/12
73/07/23
73/10/03
TIME DEPTH
OF
DAY FEET
14 15 0000
14 15 0006
14 15 0015
14 15 0025
14 15 0038
11 45 0000
11 45 0015
11 45 0025
11 45 0037
13 25 0000
13 25 0010
13 25 0020
13 25 0030
00010
WATER
TEMP
CENT
6.6
6.8
6.6
6.7
6.7
25.2
23.4
18.2
11.3
17.9
17.6
17.5
17.1
11EPALES
00300
00
MG/L
12.0
12.0
11.9
11.9
7.8
3.8
0.9
8.6
8.0
7.0
2.8
00077
TRANSP
SECCH1
INCHES
60
180
85
00094
CNOUCTVY
FIELD
MICROMHO
65
65
68
65
65
54
53
46
48
49
49
48
53
3
00400
PH
SU
8.70
8.80
8.70
8.70
8.70
6.80
6.50
5.90
6.10
7.00
6.80
6.60
6.30
00410
T ALK
CAC03
HG/L
15
15
15
15
14
17
17
17
24
15
16
17
22
2111202
0041
00610
HH3-N
TOTAL
MG/L
0.050
0.030
0.030
0.030
0.030
0.070
0.060
0.160
0.310
0.060
0.070
o.oeo
0.300
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.300
0.300
0.200
0.200
0.200
0.400
0.400
0.400
0.800
0.800
0.600
0.600
0.800
00630
N02tN03
N-TOTAL
MG/L
a. 250
0.220
0.220
0.220
0.230
0.060
0.070
0.180
0.100
0.020
0.020
0.020
0.020
00671
PMOS-DIS
ORTMO
MG/L P
0.008
0.006
0.005
0.005
0.006
0.006
0.006
0.005
0.012
0.014
0.005
0.005
0.006
DATE
FROM
TO
73/04/12
73/07/23
73/10/03
00665 32217
TIME DEPTH PHOS-TOT CHLRPHYL
OF A
DAY FEET
14
14
14
14
14
11
11
11
11
13
13
13
13
15
15
15
IS
15
45
45
45
45
25
25
25
25
0000
0006
0015
002S
0038
0000
0015
0025
0037
0000
0010
0020
0030
MG/L P
0
0
U
0
0
0
0
0
0
0
0
0
0
.015
.012
.010
.011
.013
.011
.014
.013
.053
.025
.018
.017
.040
UG/L
9.1
6.0
10.1
-------
STORE! RETRIEVAL DATE 75/01/27
422903
41 24 07.0 075 15 10.0
LAKE WALLENPAUPACK
42127 PENNSYLVANIA
11EPALES
DATE
FHOM
TO
73/04/12
73/07/23
73/10/03
DATE
FROM
TO
73/04/12
73/07/23
73/10/03
TIME DEPTH
OF
DAY FEET
15 00 0000
15 00 0006
15 00 0015
15 00 0025
15 00 0037
13 40 0000
13 40 0015
13 40 0025
13 40 0033
13 55 0000
13 55 0010
13 55 0020
13 55 002S
TIHE DEPTH
OF
DAY FEET
15 00 0000
15 00 0006
15 00 0015
IS 00 0025
15 00 0037
13 40 0000
13 40 0015
13 40 0025
13 40 0033
13 55 0000
13 55 0010
13 55 0020
13 55 0028
00010
MATER
TEMP
CENT
7.5
7.4
7.4
7.4
7.2
24.9
23.4
17.0
12.7
18.1
17.7
17.6
16.3
00665
PHOS-TOT
HG/L P
0.013
0.013
0.013
0.012
0.010
0.012
0.014
0.015
0.023
0.025
0.021
0.021
0.046
00300
DO
MG/L
11.4
11.4
11.4
11.6
8.2
2.7
1.0
8.6
8.2
7.8
1.4
32217
CHLRPHYL
A
UG/L
6.5
9.1
14.9
00077 00094
TRANSP CNOUCTVY
SECCH1 FIELD
INCHES MICROMHO
60 68
68
68
68
68
192 48
4B
42
44
72 50
50
50
66
3
00400
PH
SU
8
8
8
8
8
6
6
6
6
6
6
6
6
.90
.80
.80
.80
.60
.80
.70
.00
.00
.50
.50
.40
.30
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
16
18
17
18
25
21
20
20
29
2111202
0037
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.030
0.030
0.060
0.080
0.200
0.270
0.080
0.070
0.070
0.460
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.400
0.300
0.200
0.200
0.300
0.400
0.200
0.300
0.600
0.900
0.700
0.600
1.100
00630
N02&N03
N-TOTAL
MG/L
0^250
0.250
0.260
0.250
0.260
O.OSO
0.080
0.200
0.120
0.040
0.020
0.020
0.020
00671
PHOS-DIS
ORTHO
MG/L P
0.006
0.006
0.007
0.005
0.005
0.007
0.007
0.007
0.014
0.008
0.004
0.002
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/01/27
422904
41 22 20.0 075 16 32.0
LAKE WALLENPAUPACK
43127 PENNSYLVANIA
DATE
FROM
TO
73/04/12
73/OV/23
73/10/03
TIME
OF
DAY
15 30
15 30
15 30
15 30
IS 30
14 10
14 10
14 10
14 10
14 20
14 20
14 20
DEPTH
FEET
0000
0006
0015
0022
0030
0000
0005
0015
0027
0000
0015
0025
00010
WATErt
TEMP
CENT
7.7
7.7
7.7
7.7
7.7
25.2
24.6
23.2
15. S
18.1
17.4
16.2
11 EP ALES
00300
DO
MG/L
n\
. 1
11.1
U5
*C
11.2
8Q
• T
8J.
• H
1Q
»9
8*6
7 A
.U
2.4
00077
TRANSP
SECCHI
INCHES
54
132
66
OOQ94
CNDUCTVY
FIELD
M1CROMHO
70
65
65
65
65
50
50
49
47
52
53
83
3
00400
PH
SU
P. 20
a. 90
a. 90
a, BO
8.80
6.90
7.00
6. 60
6.10
6.70
6.50
6.50
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
19
19
20
26
23
21
25
2111202
0031
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.030
0.020
0.020
0.050
0.050
0.030
0.220
0.070
0.100
0.830
FEET DEPTH
00625
TOT KJEL
N
MG/L
0.300
0.300
0.200
0.400
0.400
0.300
0.300
0.400
0.500
1.000
0.900
1.400
00630
N02&N03
N-TOTAL
MG/L
0.260
0.250
0.2SO
0.250
0.250
0.050
0.040
0.030
0.160
0.030
0.040
0.030
00671
PHOS-OIS
ORTMO
MG/L P
0.006
0.010
0.005
0.006
0.009
0*007
0.004
0.006
0.007
0.004
0.005
0.017
00665
DATE TIME DEPTH PHOS-TOT
FKOM OF
TO DAY FEET MG/L P
73/04/12 15 30 0000 C.017
15 30 0006 0.015
IS 30 0015 0.017
15 30 0022 0.017
15 30 0030 0.016
73/07/23 14 10 0000 0.012
14 10 0005 0.014
14 10 0015 0.019
14 10 0027 0.024
73/10/03 14 20 0000 0.022
14 20 0015 0.016
14 20 0025 0.042
32217
CHLRPHYL
A
UG/L
4.6
13.9
14.7
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
APPENDIX E
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
-------
STOWET KETRIEVAL DATE 75/02/03
4229A1
41 27 40.0 075 10 55.0
irfALLENPAUPACK CHEEK
42089 7.5 HAtfLEY
0/LAKE KALLENPAUPACK
US HWY 6 BWOG .5 MI N OF WILSONVILLE
11EPALES 211120H
4 0000 FEET DEPTH
DATE
FROM
TO
73/06/lb
73/07/22
73/08/27
73/»>9/21
73/10/22
73/11/30
73/12/26
74/01/21
74/03/12
74/03/23
74/04/23
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
16
10
Ib
15
12
11
16
16
13
09
10
15
20
00
35
00
00
30
00
30
30
MG/L
0
0
0
0
0
0
0
0
0
0
0
.089
.011
.010K
.012
.017
.076
.124
.168
.2U3
.224
.152
MG/L
1.
0.
0.
0.
0.
0.
1.
0.
0.
0.
0.
900
280
370
710
600
600
200
200
500
400
300
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL OHTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
066
154
020
052
063
032
036
024
035
020
010
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
005K
009
008
005K
023
008
016
012
010
010
010
MG/L P
O.Olb
0.010
O.Olb
0.015
0.030
0.012
0.035
O.U25
0.025
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/02/03
4229A2
41 It 02.0 075 19 14.0
WALLtNPAUPACK CKtEK
<*2 7.5 NEWFOUNDLAND
1/LAKt WALLENPAUPACK
AT bANK .3 MI E OF LEDGEDALE
11EPALES 2111204
4 0000 FEET
DATE
FWOM
TO
73/05/19
73/J6/U
7J/C7/22
73/06/25
73/09/22
73/10/20
73/11/30
73/12/23
7^/01/20
74/03/12
74/03/23
74/04/23
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
OAf FEET
15
11
15
14
10
14
10
14
15
16
11
09
55
15
01
04
30
20
30
20
35
55
30
00
MG/L
0.126
0.160
0.019
0.022
0.012
0.056
0.240
0.336
0.3bd
0.310
0.312
Q.I 68
MG/L
1.050
0.780
0.370
4.000
0.660
0.675
1.300
0.800
0.900
0.200
0.400
0.300
00610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL OKTHO
MG/L
0.030
0.044
0.189
0.126
0.019
O.l>b4
0.156
u.040
0.040
0.020
0.030
0.010
MG/L P
0.005K
0.006
0.009
0.010
0.006
0.005K
0.005K
0*008
0.008
0.005
0.005
(J.005K
MG/L P
0.020
0.027
0.02b
0.040
0.025
0.036
0.025
0.010
0.020
0.020
0.025
DEPTH
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STURET RETRIEVAL DATE 75/02/03
422961
41 23 14.0 07b 14 2b.O
MILL BROOK
42 7.5 HAn/LEY
T/LAKE. wALLLNPAUPACK
PA H*Y bO? bKOG .5 MI NW MT bAY AIRSTRIP
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/05/19
73/06/17
73/07/22
73/08/25
73/09/22
73/10/20
73/11/30
73/12/23
74/01/20
74/03/10
74/03/23
74/04/21
00630 00&2S
TIME DEPTH N02NN03 TOT KJEL
OF iM-TUTAL N
DAY FEET
17
10
14
14
09
16
10
15
IS
13
13
10
25
40
10
25
40
20
00
10
10
35
15
20
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.020
.OM4
.0*0
.090
,075
.010K
.040
.064
.064
.061
.044
.Otd
MG/L
0.
0.
0.
2.
1.
0.
0.
0.
0.
0.
0.
0.
140
770
340
900
320
200
700
600
100K
600
500
100
00610 00b71 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
11.
0.
0.
005K
015
176
150
115
ulB
028
032
016
031
030
005
MG/L
0.
0.
0.
u.
0.
0.
0.
0*
0.
0.
0.
0.
p
006
01<*
017
018
013
009
012
008
008
007
OU5
005
MG/L t>
0.010
0.025
0.020
0.0 JO
0.020
0.030
U.02U
0.010
0.015
0.020
0.015
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
RETRIEVAL DATE 75/02/03
4229C1
41 21 30.0 075 16 15.0
KLEINHANb ChiEtK
42 7.b NEWFOUNDLAND
r/LAKE WALLEUHAUPACK
HA HWY 507 dROG 1.5 MI E OF PALMYRA
2111204
0000 FEtT DEPTH
DATE
FrtOM
TO
/j/u5/iy
73/06/17
73/07/22
73/Od/25
73/09/22
73/10/20
73/11/30
73/12/23
74/01/20
74/03/10
7^/03/23
7^/0^/21
01/630 00625
TIME DEPTH N02kN03 TOT KJEL
OF N-TOTAL N
DAY FE£T
17
10
14
14
10
16
0V
15
15
13
13
10
15
50
20
35
15
10
30
05
20
45
10
40
MG/L
0
0
0
0
0
0
0
0
0
0
0
0
.115
.099
.063
.075
.115
.015
.232
.176
.176
.160
.200
.124
MG/L
1.
3.
0.
0.
1.
J.
1.
0.
0.
0.
1.
0.
890
300
300
210
200
950
400
500
100K
500
100
400
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL ORTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0*
0.
044
120
160
037
054
019
023
020
016
030
106
020
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
p
OObK
ood
015
014
009
005K
012
003
OOSK
005K
005
005
MG/L P
0.120
0*020
O.U25
0.015
0*015
0.010
0.045
O.Olo
0.025
0.012
0.020
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOHET RETRIEVAL DATE 7b/02/U3
41 22 15.0 075 Is 10.0
UNNAMED CKEEK
42 7.5 NEWFOUNDLAND
T/LAKE *ALLENPAUPACK
PA HWY 5U7 BRDG IN PALMYKA
11EPALES 2111Z04
4 0000 FEET
DEPTH
DATE
FROM
ro
73/05/19
73/06/17
73/07/22
73/08/25
73/09/22
73/10/20
73/11/30
73/12/23
7W01/20
7^/03/10
7t/03/23
74/0<*/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N- 1'OTAL N
DAY FEET
17
11
14
It
10
16
09
14
15
13
12
10
05
15
25
48
30
00
00
55
30
55
50
35
MG/L
0
0
0
0
0
0
0
u
0
0
0
0
.2*0
.390
.200
.540
.680
.357
.850
.540
.560
.620
.590
.384
MG/L
0.
0.
0.
0.
1.
0.
1.
0.
0.
0.
0.
0.
320
540
500
165
400
550
200
BOO
100
700
500
250
00610 00671 00665
NH3-N PHOS-OIS PHOS-TOT
TOTAL OKTHO
MG/L
0.
0.
0.
0.
0.
U.
0.
0.
0.
0.
0.
0.
005K
013
075
013
048
009
028
032
016
025
030
010
MG/L P
0.005K
0.015
0.026
0.012
0.010
O.OU5K
0.008
0.008
0.005K
0.010
0.005
0.005K
MG/L P
0
0
0
0
0
U
0
0
0
0
0
.015
.025
.030
.015
.015
.035
.025
.015
.055
.015
.010
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/02/03
63008 tihfUG 1 Ml NE OF LE0GEDALE
11EPALES 211120**
4 0000 FEET DEPTH
DATE
FROM
TO
73/05/19
73/06/17
73/07/22
73/08/25
73/09/22
73/10/20
73/11/30
73/12/23
74/01/20
7W03/12
74/03/23
74/0*t/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAlT Ft£T
15
10
14
13
10
15
10
14
15
16
11
09
45
55
25
50
15
05
00
10
30
45
20
00
MG/L
0.048
0.133
0.160
0.154
0.200
0.013
0.320
0.300
0.340
0.176
0.156
0.044
MG/L
2.100
2.300
1.260
2.100
0.540
0.300
0.400
0.700
0.300
0.300
0.600
0.500
00610 00671 00665
NH3-N PHOS-OIS PhOS-TOT
TOTAL ORTHO
MG/L
0.054
0.084
0.075
0.088
0.018
0.011
0.016
0.038
0.020
0.025
0.025
0.010
MG/L P
0.009
0.013
0*029
0*014
0.007
0.005K
0.008
0.005K
0.005
0.005
0.005K
MG/L P
0.032
0.040
0.045
0.030
0.025
0.020
0.025
0.015
0.030
0.035
0.030
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STOkET HETRIEVAL DATE 75/02/03
4229FJ
41 25 40.0 0715 Ib 10.0
PUKOY CKEtK
42 7.5 LAKEVILLE
T/LAKE rtALLLNPAUPACK
KU 63009 BrtDG .8 MI SE OF LAKEVILLE
llEPALtS 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
73/05/19
73/06/17
73/07/22
73/08/25
73/0^/22
73/10/20
73/11/30
73/12/23
74/01/20
74/03/12
74/03/23
74/04/21
00630 00625
TIME DEPTH N026.N03 TOT KJEL
OF N-TOTAL N
DAY FEET
15
10
14
13
oy
14
09
14
15
16
10
10
20
35
10
21
40
50
50
00
20
35
10
30
MG/L
0
0
0
0
0
0
0
0
0
u
0
0
.060
.138
.110
.260
.190
.048
.192
.200
.208
.160
.160
.040
MG/L
3.
1.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
150
650
500
270
b60
900
700
600
300
300
600
300
00610 00671 00665
NH3-N KMOS-D1S PHOS-TOT
TOTAL OUTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
075
056
050
017
022
031
016
052
044
025
035
010
MG/L P
0
0
0
0
0
0
0
0
0
0
0
0
.008
.018
.025
.027
.011
.005K
.006
.008
.005K
.005
.010
.005
MG/L P
0.035
0.040
0.035
0.035
0.035
0.020
0.020
0.015
u.025
0.035
0.025
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORtT RETRIEVAL DATE 75/02/03
41 25 38.0 075 lb 3/.0
UNNAMED CkEEK
42 7.5 LAKtVlLLt
r/LAl\t. WALLENPAUPACK
«L> 63112 brtOG .8 MI b OF PA HWY 590
11EPALES 2111204
4 0000 F£ET DEPTH
DATE
FkOM
Tu
73/05/1^
73/06/17
73/07/22
73/08/25
73/OV/22
73/10/2U
73/11/30
73/12/2J
74/01/20
74/03/12
74/03/23
74/04/21
00630 00625
TIME DEPTH NU2&NOJ TOT KJEL
OF N-TOTAL N
DAY FEET
iS
10
13
13
09
14
09
13
15
16
10
10
10
25
52
10
20
35
20
49
15
20
00
20
MG/L
0
0
0
0
0
0
u
Ci
0
0
0
u
*
•
•
*
•
•
•
•
•
•
*
•
025
210
084
350
063
189
104
224
288
264
232
140
MG/L
2.360
1.900
3.360
2.800
9.350
2.100
1.450
0.400
1.100
0.500
0.400
O.bOO
U0610 00671 00665
NH3-N PHOS-DIS PHOS-TOT
TOTAL OftTHO
MG/L
0
0
I
7
4
0
u
0
0
0
0
0
.110
.840
.040
.900
.800
.399
.028
.056
.610
.060
.030
.145
MG/L
0.
LI.
0.
3.
1.
2.
0.
0.
0.
0.
0.
u.
p
040
600
470
100
700
800
008
024
460
100
055
055
MG/L P
O.U80
0.67U
0.550
3.800
2.400
2.900
0.240
0.045
O.S9o
i>.145
0.105
ii.055
-------
bTOhfET KETRIEVAL DATE 75/02/03
41 26 30.0 075 13 2d.O
SP1NNERBROOK
42 7.5 HAWLEf
T/LArtE tfALLENPAUPACK
«L> 63113 bh*UO .» Ml SE OF JCT H*Y 590
HEPALES 2111204
4 UOOO FEET DEPTH
DATE
FROM
TO
73/05/19
73/06/17
73/07/2?
73/08/2^
73/09/22
73/10/20
73/11/30
73/12/23
74/01/20
74/0 J/ 12
74/03/23
74/04/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
UAt FEET
14
10
13
12
09
14
09
13
15
16
09
10
45
10
39
55
00
20
00
32
00
10
45
00
MG/L
0
0
0
0
0
0
0
a
0
0
0
0
.021
.115
.2dO
.336
.094
.010K
.023
.056
.120
.052
• 044
.028
MG/L
1.
i).
0.
1.
2.
0.
0.
0.
0.
0.
2.
0.
900
980
265
540
200
200
300
700
500
200
000
200
00610 00671 00665
NH3-N PHOS-D1S PHOS-TOT
TOTAL ORTHO
MG/L
0*
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
u.
041
028
034
110
189
042
012
024
068
025
060
010
MG/L
0.
i>.
0.
a.
0.
0.
0.
0.
0.
0.
0.
0.
p
007
022
010
027
020
012
008
008
012
005
010
005
MG/L P
0.020
U.035
0.027
0.025
0.020
0.030
0.020
0.012
0.010
0.070
0.005
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/02/03
4229EA P04229EA P000400
41 26 27.1) 075 22 09.0
HIDEOUT PLANT (LAKE ARIELI
42089 7.5 LAKEV1LLE
T/LAKE WALLENPAUPECK
ArtlEL CREEK
11EPALES 214)204
4 0000 FEET DEPTH
DATE
FAOM
TO
73/07/10
CP(T>-
73/07/10
73/08/10
CP-
73/OB/10
73/09/14
CPITI-
73/09/14
73/10/10
CP1T)-
73/io/u
73/11/12
CP 1 T 1 -
73/11/12
73/12/14
CP 1 T 1 -
73/12/14
74/02/11
CPITI-
74/02/11
74/03/11
CHITI-
74/03/11
74/04/H
CP-
74/04/11
74/05/10
CP-
74/05/10
74/06/10
CPm-
74/06/10
74/07/11
CP(TI-
74/07/11
00630
TIME DEPTH N02iN03
OF N-TOTAL
DAY FEET MG/L
04
16
04
16
11
16
16
16
04
16
04
16
04
16
04
16
04
16
04
16
04
16
04
16
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
30
0
0
U
0
0
1
0
4
0
1
0
0
.2*0
.310
.660
.720
.880
.440
.720
.000
.360
.000
.680
.208
00625
TOT KJEL
N
MG/L
10
a
5
7
1
0
1
1
1
1
9
15
.000
.200
.100
.900
.100
.SOOK
.400
.OOOK
.OOOK
.200
.000
.000
00610 00671 00665 S0051 SOOS3
NH3-N PHOS-OIS PHOS-TOT FLOW CONDUIT
TOTAL URTHO HATE FLOW-MGD
MG/L MG/L P MG/L P INST MGO MONTHLY
3.150
1.100
0.920
1.760
0.140
0.058
0.7HO
d.040
0.410
0.400
7.400
0
0.050 0
0.072 0
T
0.160 0
0.067 0
0.1SO 0
0.040K 0
O.OSOtv 0
0
0.055 0
0.025 0
3.600 5
_,
.480
.135
.120
.200
.610
.740
.067
.120
.140
.065
.210
.500
0.022
0.027
0.014
0.040
0.023
0.106
0.057
0.083
0.092
0.075
0.042
0.040
0.031
0.035
0.026
0.010
0.026
0.053
0.055
0.068
0.097
0.062
0.069
0.060
K VALUE KNOWN TO tiE
LESS THAN INDICATED
-------
STUrtET KETHIEVAL DATE 75/03/03
422^XA AS4229XA P000060
41 fly 00.U 075 17 00.0
POCONO PLATEAU CHKISTIAN ASSOCIA
42 7.b BUCK MILL FA
T/LAM;
TAYLOW
HEPALES 2141204
4 0000 FEET DEPTH
DATE
FROM
TO
73/11/23
74/0 1/U<»
74/03/01
74/03/17
74/04/la
74/07/01
TIME DEPTH
OF
DAY
14
15
IS
16
20
18
FEET
00
00
30
30
30
00
00630
IMC2&N03
N-TOTAL
MG/L
0.050
0.960
0.360
0.240
O.lbO
0.200
00625
TOT KJEL
N
MG/L
0.500K
0.570
l.OUOK
l.OOOK
l.OOOK
l.OOOK
00610
NH3-N
TOTAL
MG/L
0.1-^7
0.040K
O.ObOK
0.230
0.050K
0.100
00671
PHOS-D1S
ORTHO
MG/L P
0.067
0.140
0.160
0.077
0.050K
0.090
00665
PHOS-TOT
50051
FLOw
KATE
MG/L
0.
0.
0.
0.
P
17U
110
050K
170
INST
0
0
0
0
0
0
MGO
.001
.001
.uOl
.002
.002
.002
S0053
CONDUIT
FLOw-MGD
MONTHLY
0.001
0.001
0.001
0.002
0.002
0.002
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/02/03
DATE
FROM
TO
73/07/Oh
CP-
73/07/06
73/08/17
73/0^/23
73/10/17
73/11/14
CPU)-
73/11/14
73/12/19
74/01/30
74/02/1^
74/U3/12
74/04/14
7^/05/05
74/06/13
7W07/20
TIME 1
OF
DAY 1
13 00
16 00
14 30
13 45
16 15
11 00
16 00
13 45
13 35
13 15
13 25
15 45
11 00
14 30
14 00
00630
DEPTH NU2NN03
N-TOTAL
FEET MG/L
0.076
0.110
0.440
0.230
a.180
lO.bOO
4229ZA AS<+229ZA P000300
41 25 38.0 075 IS 41.0
COVE HAVEN HONEYMOON RESORT
42 7.b LAKEVILLE
T/LAKE WALLENPAUPECK
UNNAMED iTRtAM
11EPALES 2141204
4 0000 FEET DEPTH
00625
TOT KJEL
N
MG/L
16.800
31.500
31.500
4.700
00610
NH3-N
TOTAL
MG/L
5.200
6.900
24.000
00671
PHOS-DIS
ORTHO
MG/L P
6.060
4.900
11.600
7.700
00665
PHOS-TOT
MG/L P
8.200
23.000
12.300
8.600
50051
FLOW
RATE
INST MGD
0.055
0.061
0.046
0.035
50053
CONDUIT
FLOW-MOD
MONTHLY
0.055
0.058
0.048
0.050
9.700
H.QOO
U.034
0.030
17.000 l.OOOK
0.520 5.800
2.900 10.000
2u.OOO
10.000
3.100
1.400 1
9.2BO
.500
.700
.700
.000
.OOOK
0.078
0.720
0.560
0.05U
0.150
0.210
3.100
0.100
9.400
6.400
10.100
9.700
11.000
9.500
8.250
3.150
9.600
9.500
11.500
10.000
12.000
9.700
8.250
3.450
0.020
0.038
U.034
0.024
0.019
0.029
O.U35
0.039
0.024
0.028
0.025
0.026
0.025
0.027
0.032
0.039
K VALUE KNOWN TO BE
LESS THAN INDICATED
-------
STORET RETRIEVAL DATE 75/02/03
422921 AS422921 P000536
41 27 15.0 075 10 5/.0
•/ALLtNPAUPECK ARtA HIGH SCHOOL
42127 7.5 HAwLEY
D/LAKE WALLENPAUPECK
LAKE rfALLENPAUPECK
11EPALES 2141204
4 0000 FEET DEPTH
DATE
FROM
TO
73/06/19
73/07/17
73/08/22
73/09/20
73/10/19
73/11/27
73/12/19
74/01/25
74/02/26
74/03/25
74/04/23
74/05/21
00630 00625
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
OAY FEET
10
09
12
10
09
09
09
09
08
12
09
09
00
00
00
00
00
30
30
00
30
45
00
30
MG/L
1.
2.
1.
4.
id.
14.
43.
42.
26.
6.
16.
6.
470
BOO
820
120
600
000
000
000
000
600
000
400
MG/L
0.
2.
3.
0.
2.
0.
4.
5.
2.
1.
1.
990
100
500
500K
500
500K
OOU
300
700
800
600
00610 00671 00665
NH3-N PHOS-DI5 PHOS-TOT
TOTAL ORTHO
MG/L
0.280
0.360
0.164
0.200
0.031
C.120
1.000
2.220
1.000
U.560
0.140
O.ObOK
MG/L P
0.850
0.750
2.720
1.700
1.540
4.300
5.900
9.400
5.550
1,950
3.800
3.900
50051 50053
FLOW CONDUIT
RATE FLOW-MGD
MG/L P 1NST MGD MONTHLY
0.890
0.970
3.100
1.700
2.700
4.400
6.400
9.400
6.VOO
2.300
4.100
4.400
0.006
0.002
0.002
0.005
0.006
0.005
0.005
0.006
0.006
0.006
0*006
0.007
0.007
0.002
0.003
0.006
0.005
0.006
0.006
0.006
0.006
0.006
0.006
0.006
K VALUE KNOWN TO BE
LESS THAN INDICATED
------- |