U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
SACANUAGA RESERVOIR
FULTON AND SARATOGA COUNTIES
NEW YORK
EPA REGION II
WORKING PAPER No, 167
PACIFIC NORTHWEST ENVIRONMENTAL RESEARCH LABORATORY
An Associate Laboratory of the
NATIONAL ENVIRONMENTAL RESEARCH CENTER - CORVALLIS, OREGON
and
NATIONAL ENVIRONMENTAL RESEARCH CENTER - LAS VEGAS, NEVADA
-------
REPORT
ON
SACANDAGA RESERVOIR
FULTON AND SARATOGA COUNTIES
NEW YORK
EPA REGION II
WORKING PAPER No, 167
WITH THE COOPERATION OF THE
NEW YORK STATE DEPARTMENT OF ENVIRONMENTAL CONSERVATION
AND THE
NEW YORK NATIONAL GUARD
NOVEMBER, 1974
-------
CONTENTS
Page
Foreword i i
List of New York Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 3
III. Lake Water Quality Summary 5
IV. Nutrient Loadings 9
V. Literature Reviewed 15
VI. Appendices 16
-------
n
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 [§314(a,b)],
and water quality monitoring [§106 and §305(b)] activities mandated
by the Federal Water Pollution Control Act Amendments of 1972.
-------
iii
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, multivariate 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 New York Department of
Environmental Conservation for professional involvement and to
the New York National Guard for conducting the tributary sampling
phase of the Survey.
Henry L. Diamond, Commissioner of the New York Department of
Environmental Conservation, and Leo J. Hetling, Director, and
Italo G. Carcich, Senior Sanitary Engineer, Environmental Quality
Research, Department of Environmental Conservation, provided
invaluable lake documentation and counsel during the Survey.
Major General John C. Baker, the Adjutant General of New York,
and Project Officer Lieutenant Colonel Fred Peters, who directed
the volunteer efforts of the New York National Guardsmen, are also
gratefully acknowledged for their assistance to the Survey.
-------
IV
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF NEW YORK
LAKE NAME
Allegheny Reservoir
Black
Canandaigua
Cannonsville
Carry Falls
Cassadaga
Cayuga
Champlain
Chautauqua
Conesus
Cross
Goodyear
Huntington
Keuka
Long
Lower St. Regis
Otter
Owasco
Raquette Pond
Round
Sacandaga Res.
Saratoga
Schroon
Seneca
Swan
Swinging Bridge Res.
COUNTY
Cattaraugas, NY; McLean,
Warren, PA
St. Lawrence
Ontario
Delaware
St. Lawrence
Chautauqua
Seneca, Tompkins
Clinton, Essex, NY; Addison,
Chittenden, Franklin, VT
Chautauqua
Livingston
Cayuga, Onondaga
Otsego
Sullivan
Ontario
Hamilton
Franklin
Cayuga
Cayuga
Franklin
Saratoga
Fulton, Saratoga
Saratoga
Essex, Warren
Seneca, Schyler, Yates
Sullivan
Sullivan
-------
SACANDAGA RESERVOIR
® Tributary Sampling Site
x Lake Sampling Site
^ Sewage Treatment Facility
j Direct Drainage Area Boundary
& Indirect Drainage Area Boundary
9 I ? 3 A 5M1.
Scale
43* 10—
74*00'
-------
SACANDAGA RESERVOIR
STORET NO. 3632
CONCLUSIONS
A. Trophic Condition:
Survey data show that Sacandaga Reservoir is mesotrophic.
Of the 26 New York lakes sampled in the fall of 1972, when all
were essentially well-mixed, three had less mean total phos-
phorus, seven had less mean inorganic nitrogen, and one had
less mean dissolved phosphorus. For all data, five of the New
York lakes had less mean chlorophyll a^ and only four had greater
Secchi disc transparency.
Survey limnologists noted that the water was very clear on
all sampling occasions, and no algal blooms were observed.
B. Rate-Limiting Nutrient:
There was a significant loss in nutrients between the time
the sample was collected and the assay was begun; therefore, the
results are considered unreliable. However, the low level of
mean dissolved phosphorus observed (0.004 mg/1) indicates that
the potential primary productivity would have been low at that
time.
The lake data indicate that phosphorus was the limiting
nutrient at the time the assay was collected as well as the
other sampling dates (all N/P ratios were greater than 39/1,
and phosphorus limitation would be expected).
-------
C. Nutrient Controllability:
1. Point sources—During the sampling year, Sacandaga
Reservoir received a total phosphorus load at a rate less than
that proposed by Vollenweider (in press) as "permissible", i.e.,
an oligotrophic rate (see page 13). The contribution from point
sources was about 3% of the total load.
Phosphorus removal at the point sources would not be expected
to appreciably change the trophic condition of the reservoir, but
would provide additional protection for the existing trophic con-
dition.
2. Non-point sources—During the sampling year, the mean
total annual non-point phosphorus export was greatest from the
Sacandaga River; however, the export rate of this river was less
than other streams sampled (see page 13). The phosphorus export
rate (156 Ibs/mi2/yr) and the export N/P ratio (28/1) of the
Kennyetto Creek may be indicative of a point source(s) or cultural
practices that result in nutrient inputs to this drainage.
-------
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
A. Lake Morphometry :
1. Surface area: 30,146 acres.
2. Mean depth: 24.9 feet.
3. Maximum depth: 50.2 feet.
4. Volume: 750,635 acre/feet.
5. Mean hydraulic retention time: 166 days.
B. Tributary and Outlet:
{See Appendix A for flow data)
1. Tributaries -
Name Drainage area* Mean flow*
Sacandaga River 525.0 mi? 1,149.4 cfs
Unnamed Creek (A-l) 4.1 mi« 9.0 cfs
Hunters Creek 6.6 mi~ 14.4 cfs
Batcheller Creek 6.8 mi« 14.8 cfs
Beecher Creek 11.5 mi 25.2 cfs
West Stony Brook 88.0 mi^ 192.6 cfs
East Stoney Brook 95.4 mi« 208.8 cfs
Sand Creek 16.1 mi ~ 35.3 cfs
Paul Creek 20.5 mi ~ 44.9 cfs
Daly Creek 27.2 mip 59.6 cfs
Kenyetto Creek 36.8 mi 80.5 cfs
Minor tributaries & 2
immediate drainage - 158.9 mi 451.4 cfs
Totals 996.9 mi2 2,285.9 cfs
2. Outlet -
Sacandaga River 1,044.0 mi2** 2,285.9 cfs
fWood, 1974.
* Drainage areas are accurate within ±5%, except for small basins (±10%);
mean daily flows are accurate within ±5 and 25%; and normalized mean
monthly flows are accurate within ±15%.
** Includes area of lake.
-------
C. Precipitation*:
1. Year of sampling: 46.2 inches
2. Mean annual: 41.9 inches.
* See Working Paper No. 1, "Survey Methods",
-------
III. LAKE WATER QUALITY SUMMARY
Sacandaga Reservoir was sampled three times during the open-water
season of 1972 by means of a pontoon-equipped Huey helicopter. Each
time, samples for physical and chemical parameters were collected from
three stations on the lake and from a number of depths at each station
(see map, page v). During each visit, a single depth-integrated (15
feet to surface) sample was composited from the three stations for phyto-
plankton identification and enumeration; and during the last visit, a
single five-gallon depth-integrated sample was composited for algal assays.
Also each time, a depth-integrated sample was collected from each of the
stations for chlorophyll ^analysis. The maximum depths sampled were 31
feet at station 1, 35 feet at station 2, and 36 feet at station 3.
The results obtained are presented in full in Appendix B, and the
data for the fall sampling period, when the lake was essentially well-
inixed, are summarized below. Note, however, the Secchi disc summary
is based on all values.
For differences in the various parameters at the other sampling
times, refer to Appendix B.
-------
A. Physical and chemical characteristics:
Parameter Minimum
Temperature (Cent.) 12.9
Dissolved oxygen (mg/1) 8.6
Conductivity (ymhos) 50
pH (units) 6.9
Alkalinity (mg/1) 10
Total P (mg/1) 0.007
Dissolved P (mg/1) 0.002
N0? + NO- (mg/1) 0.080
Ammonia pg/1) 0.030
FALL VALUES
(10/10/72)
Mean Median
Maximum
14.2
9.0
50
7.0
10
0.009
0.004
0.106
0.069
14.0
9.2
50
7.0
10
0.009
0.004
0.110
0.050
15.2
9.4
50
7.2
12
0.012
0.007
0.130
0.120
ALL VALUES
Secchi disc (inches) 114
139
139
196
-------
B. Biological characteristics:
1. Phytoplankton -
Sampling
Date
05/18/72
07/31/72
10/10/72
Domi nant
Genera
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
1.
2.
3.
4.
5.
Dinobryon
Flagellates
Phacus
Cryptomonas
Synedra
Other genera
Total
Lyngbya
Fragilaria
Dinobryon
Polycystis
Peridim'um
Other genera
Total
Stichococcus
Dinobryon
Flagellates
Fragilaria
Anabaena
Other genera
Number
per ml
1
2,306
6,506
Total
6,080
-------
Sampling
Date
05/18/72
07/31/72
10/10/72
Station
Number
01
02
01
02
03
01
02
03
8
2. Chlorophyll a^ -
(Because of instrumentation problems during the 1972 sampling,
the following values may be in error by plus or minus 20 percent.)
Chlorophyll a^
(ug/1)
3.0
1.6
4.6
8.1
1.9
7.2
7.0
5.4
C. Limiting Nutrient Study:
There was a significant loss in nutrients in the assay sample
from the time the sample was collected and the beginning of the
assay; therefore, the results are considered unreliable. However,
the low level of mean dissolved phosphorus measured in the reser-
voir in October (0.004 mg/1) indicates that the potential primary
productivity would have been low at that time.
The lake data indicate that phosphorus was the limiting
nutrient at the time the assay sample was collected as well
as the other sampling dates (N/P ratios were greater than 39/1,
and phosphorus limitation would be expected).
-------
IV. NUTRIENT LOADINGS
(See Appendix C for data)
For the determination of nutrient loadings, the New York National
Guard collected monthly near-surface grab samples from each of the tribu-
tary sites indicated on the map (page v)» except for the high runoff
months of April and May when two samples were collected. Sampling was
begun in November, 1972, and was completed in October, 1972.
Through an interagency agreement, stream flow estimates for the year
of sampling and a "normalized" or average year were provided by the New
York District Office of the U.S. Geological Survey for the tributary sites
nearest the lake.
In this report, nutrient loads for sampled tributaries were determined
by using a modification of a U.S. Geological Survey computer program for
calculating stream loadings*. Nutrient loadings for unsampled "minor
tributaries and immediate drainage" ("ZZ" of U.S.G.S.) were estimated by
2
using the means of the nutrient loads, in Ibs/mi /year, at stations C-l,
p
p_l, E-l, H-l, and K-l and multiplying the means by the ZZ area in mi .
Nutrient loads from Sacandaga Park were estimated at 2.5 Ibs P and
7.5 Ibs N/capita/year.
Working Paper No. 1.
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A. Waste Sources:
1. Known municipal -
Pop.
Name
Sacandaga
Park
500
10
Served* Treatment
Mean Receiving
Flow (mgd) Water
Imhoff tank 0.050** Sacandaga Reservoir
2. Known industrial - None
* Anonymous, 1971.
** Estimated at 100 gal/capita/day.
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11
Annual Total Phosphorus Loading - Average Year:
1. Inputs -
Ibs P/ % of
Source y_r total
a. Tributaries (non-point load) -
Sacandaga River 17,750 36.8
Unnamed Creek (A-l) 160 0.3
Hunters Creek 410 0.9
Batcheller Creek 330 0.7
Beecher Creek 460 1.0
West Stoney Brook 3,470 7.2
East Stoney Brook 4,870 10.1
Sand Creek 590 1.2
Paul Creek 800 1.7
Daly Creek 980 2.0
Kennyetto Creek 5,740 11.9
b. Minor tributaries & immediate
drainage (non-point load) - 6,390 13.2
c. Known municipal -
Sacandaga Park 1,250 2.6
d. Septic tanks* - 330 0.7
e. Known industrial - None
f. Direct precipitation** - 4,700 9.7
Total 48,230 100.0
2. Outputs -
Lake outlet - Sacandaga River 35,450
3. Net annual P accumulation - 12,780 pounds
* Estimate based on 526 shoreline dwellings; see Working Paper No. 1
** See Working Paper No. 1.
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12
C. Annual Total Nitrogen Loading - Average Year:
1. Inputs -
Ibs N/ % of
Source y_r total
a. Tributaries (non-point load) -
Sacandaga River 1,818,100 48.8
Unnamed Creek (A-l) 9,100 0.3
Hunters Creek 14,500 0.4
Batcheller Creek 24,140 0.6
Beecher Creek 42,900 1.2
West Stoney Brook 293,880 7.9
East Stoney Brook 291,570 7.8
Sand Creek 55,800 1.5
Paul Creek 85,040 2.3
Daly Creek 79,580 2.1
Kennyetto Creek 165,100 4.4
b. Minor tributaries & immediate
drainage (non-point load) - 540,640 14.5
c. Known municipal -
Sacandaga Park 3,750 0.1
d. Septic tanks* - 12,360 0.3
e. Known industrial - None
f. Direct precipitation** - 290,430 7.8
Total 3,726,890 100.0
2. Outputs -
Lake outlet - Sacandaga River 3,840,480
3. Net annual N loss - 113,590 pounds
* Estimate based on 526 shoreline dwellings; see Working Paper No. 1
** See Working Paper No. 1.
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13
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary Ibs P/mi2/yr Ibs N/mi2/yr
Sacandaga River 34 3,463
Unnamed Creek (A-l) 39 2,219
Hunters Creek 62 2,197
Batcheller Creek 49 3,550
Beecher Creek 40 3,730
West Stoney Brook 39 3,340
East Stoney Brook 51 3,056
Sand Creek 37 3,466
Paul Creek 39 4,148
Daly Creek 36 2,926
Kennyetto Creek 156 4,486
-------
14
E. Yearly Loading Rates:
In the following table, the existing phosphorus loading
rates are compared to those proposed by Vollenweider (in press).
Essentially, his "dangerous" rate is the rate at which the
receiving waters would become eutrophic or remain eutrophic;
his "permissible" rate is that which would result in the
receiving water remaining oligotrophic or becoming oligo-
trophic if morphometry permitted. A mesotrophic rate would
be considered one between "dangerous" and "permissible".
Total Phosphorus Total Nitrogen
Units
Ibs/acre/yr
grams/mvyr
Total
1.6
0.18
Accumulated
0.4
0.04
Total
123.6
13.9
Accumulated
loss*
Vollenweider loading rates for phosphorus
(g/m /yr) based on mean depth and mean
hydraulic retention time of Sacandaga Reservoir:
"Dangerous" (eutrophic rate) 0.80
"Permissible" (oligotrophic rate) 0.40
* There was an apparent loss of nitrogen during the sampling year. This may
have been due to nitrogen fixation in the lake, solubilization of previously
sedimented nitrogen, recharge with nitrogen-rich ground water, unknown and
unsampled point sources discharging directly to the lake, or underestimation
of the nitrogen loads from Sacandaga Park. Whatever the cause, a similar
nitrogen loss has occurred at Shagawa Lake, Minnesota, which has been inten-
sively studied by EPA's National Eutrophication Research and Lake Restora-
tion Branch.
-------
15
V. LITERATURE REVIEWED
Anonymous, 1971. Inventory of municipal waste facilities. Publ.
No. OWP-1, Vol. 2, EPA, Washington, D.C.
Vollenweider, Richard A., (in press). Input-output models. Schweiz.
A. Hydrol.
Wood, Lindsey W., 1974. Personal communication (morphometry data).
NY Dept. of Health, Albany.
-------
VII. APPENDICES
APPENDIX A
TRIBUTARY FLOW DATA
-------
LAKE CODE 363?
TRIBUTARY FLOW INFORMATION FOP NEW YORK
GREAT SACANOAGA LAKE
11/26/74
TOTAL DRAINAGE AREA OF LAKF 1044.00
SUB-DRAINAGE
TRIBUTARY AREA
JAN
FF.R
MAR
APR
MAY
NORMALIZED FLOWS
JUM JUL AUG
SEP
OCT
NOV
DEC
MEAN
3632A1
3632B1
3632C1
363201
3632E1
3632F1
363261
3632G3
3632H1
3632J1
3632K1
3632L1
3632ZZ
4.10
6.60
6.77
11.50
88.00
95.40
525.00
1044.00
16.10
20.50
27.20
36. SO
?06.03
7.05
11.30
11.60
19.80
151.00
164. 00
903.00
1790.00
27.70
35.20
46. HO
63.30
354.00
5.81
9.36
9.60
16.30
125.00
135.00
745.00
1480.00
22. SO
29.10
38.60
52.20
29?. 00
13.10
21.00
21.60
36.60
280.00
304.00
1670.00
3330.00
51.30
65.30
66.60
117.00
656.00
30.70
49.50
50. BO
86.20
660.00
715.00
3940.00
7830.00
121.00
154.00
204.00
276.00
1550.00
14.40
23.10
23.70
40.30
308.00
334.00
1840.00
3660.00
56.40
71.80
95.30
129.00
722.00
6. OH
9.79
10.00
17.10
131.00
142.00
779.00
1550.00
23.90
30.40
40.40
54.60
306.00
3.60
5.80
5.95
10.10
77.40
83.80
461.00
917.00
14.20
18.00
23.90
32.30
181.00
2.01
3.23
3.32
5.63
43.10
46.70
257.00
511.00
7.88
10.00
13.30
18.00
101.00
2.78
4.48
4.60
7.81
59.80
64.80
357.00
709.00
10.90
13.90
18.50
25.00
140.00
5.26
8.47
8.69
14.80
113.00
122.00
674.00
1340.00
20.70
26.30
34.90
47.20
264.00
8.82
14.20
14.60
24.70
189.00
205.00
1130.00
2250.00
34.60
44.10
58.50
79.20
443.00
8.21
13.20
13.60
23.00
176.00
191.00
1050.00
2090.00
32.20
41.10
54.50
73.70
413.00
8.98
14.44
14.82
25.17
192.60
208.75
1149.44
2285.99
35.27
44.69
59.55
80.55
451.42
SUMMARY
TOTAL DRAINAGE AREA OF LAKE =
SUM OF SUB-DRAINAGE AREAS =
1044.00
1044.00
TOTAL FLOW IN = 27455.75
TOTAL FLOW OUT = 27457.00
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAW MEAN FLOW DAY
3632A1
FLOW DAY
FLOW DAY
FLOW
363281
11
12
1
?
3
4
5
6
7
B
9
10
11
12
1
2
3
4
5
6
7
B
9
10
72
72
73
73
73
73
73
73
73
73
73
73
72
72
73
73
73
73
73
73
73
73
73
73
18.20
10. ?0
14.7!)
9.6«
35.80
25.40
19.10
6.52
3.29
1.23
2.27
2.1ft
?9.20
16.40
23.50
15.60
41.30
41.00
30.60
10.50
5.30
1.97
3.66
3.48
5
3
6
3
3
7
6
•>
7
4
8
6
5
3
6
3
3
7
h
2
7
4
fl
6
9.05
7.22
9.05
21.40
2.60
20.60
5.65
7.20
2.35
1.75
1.66
1.68
10.80
8.58
10.80
2^.40
3.06
26.00
8.00
7.60
0.76
1.55
1.30
1.48
21
20
21
20
12.00
26.30
16.00
32.50
-------
coot
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIHJTAWY MONTH YEAH
3632C1
363201
363?F1
3632M
11
1?
1
?
3
4
5
6
7
B
9
10
11
12
1
2
3
4
5
6
7
R
9
10
11
1?
1
?
3
4
5
6
7
n
9
10
11
l?
l
•>
3
4
5
f>
7
8
9
10
72
72
73
73
73
73
73
73
73
73
73
73
72
72
73
73
73
73
73
73
73
73
73
73
73
72
73
73
73
73
73
73
73
73
73
73
72
7?
73
73
73
73
73
73
73
73
73
73
HEAN FLOW DAY
FLOW DAY
FLOW (JAY
FLOW
30.00
16.90
?4.10
16. 00
42.50
4?. no
31.40
10.70
5.44
?.02
3.7ft
3.S7
50. SO
2fl.50
4i. 20
27.20
72.10
71.30
53.40
18.30
9.23
3.43
6.39
6.0«
389.00
216.00
314.00
209.00
551.00
546.00
408.00
140.00
70.70
26.30
48.90
46.40
4??. 00
237.00
341.00
2?5.00
598.00
502.00
443.00
152.00
76.60
2P.50
53.00
50.10
5
3
5
2
b
10
6
2
2
7
25
6
5
3
5
2
6
10
6
2
2
7
25
6
5
3
6
3
3
7
6
2
7
4
8
ft
5
3
6
3
3
7
6
2
7
a
8
6
?5.50
20.30
31.30
16.00
17.20
27.80
12.00
14.40
13.20
2.50
5.26
3.90
56.90
45.40
694.00"
35.50
3B.OO
40.00
17.40
21.20
19.60
4.20
7.30
5.30
278.00
222.00
276.00
65&.00
BO. 00
518.00
198.00
243. OJ
74.00
47.50
37.50
45.00
2?4.00
178.00
224.03
532.00
65.00
542.00
173.00
197.00
50.00
46.00
41.00
44.50
16
12
16
12
21
20
21
20
IB.40
25.00
27.60
37.40
360.00
604.00
350.00
675.00
-------
FLO.V INFOHMflTION FOR NEW YORK
1 1/26/74
LA«.E: cone
SACANDAG& L«KE
MEAN MONTHLY TLOtoS AMD DAILY FLOWS
TKI4UTASY MONTH YFAP
363PG3
36J2H1
3632J1
MEAN FLOW DAY
FLO* DAY
FLOW DAY
1 1
1?
1
3
4
5
7
7
cj
10
1 1
12
1
3
5
7
7
8
9
10
H
1?
1
2
3
4
5
7
7
R
9
10
1 1
12
1
3
4
5
7
7
8
10
7?
7?
73
73
73 ,
73
73
73
73
73
73
73
73
73
72
73
73
73
73
73
73
73
73
73
73
73
7?
72
73
73
73
73
73
73
73
73
73
73
73
72
72
73
73
73
73
73
73
73
73
73
73
73
2330.00
1300.90
1880.00
240.00
3P90.00
3260.00
835.00
421.00
4?1.00
157. CO
29?. 00
277.00
4630.00
2590.00
3720.00
2470.00
6560.00
6480.00
4850.00
1660.00
838.00
838.00
312.00
580.00
550.00
71.20
39. "0
57.60
38.00
101.00
100.03
74.80
25.60
13.00
13.00
4.81
0.91
8.50
90.80
51.00
73. ?0
48.50
129.00
127.00
95.20
32.60
16.40
16.40
6.10
11.40
10.00
5
3
6
3
3
7
6
2
7
7
4
8
6
5
3
5
2
6
10
6
2
2
2
7
25
6
5
3
5
2
6
10
6
?
2
2
7
25
6
5
3
5
2
6
10
f,
?
2
?
7
25
6
1740.00
1390.00
1740.00
4130.00
496. OD
3880.00 21
1220.00 20
1540.00
454.00
454.00
321 .OP
274.00
307.00
48.00
3040.00
4110.00
5000.00
4580.00
5480.00 16
127.00 12
4070.00
2480.00
2480.00
2550.00
2100.00
2060.00
80.00
64.00
98.00
54.50
53.50
68.00 16
29.20 12
26.00
33.00
33.00
4,?0
11.00
7. SO
136.00
10H.OO
167.00
93.00
92.00
80.00 16
30.00 12
37.40
33.50
33.50
2.?S
8.25
4.9b
2450.00
4790.00
4080.00
2010.00
46.40
63.00
50.40
72.00
-------
FLO«
FOR NFJd XOftK
11/26/74
coot
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY
3632K1
3632L1
3632ZZ
FLOW DAY
FLOW DAY
FLOW
11
12
1
2
3
4
5
6
7
7
B
9
10
11
12
1
2
3
4
5
6
7
7
«
9
10
11
12
1
?
3
A
5
6
7
7
3
9
10
72
72
73
73
73
73
73
73
73
73
73
73
73
72
72
73
73
73
73
73
73
73
73
73
73
73
72
72
73
73
73
73
73
73
73
73
73
73
73
120.00
67.60
97,30
64.30
170.00
169.00
126.00
43.30
21.80
21.80
8.11
15.10
14.30
163.90
91.40
132.00
87.00
230.00
228.00
171.00
58.50
29.50
29.50
11.00
20.40
19.40
9l?,00
512.00
736.00
487.00
1290.00
1280.00
957.00
328.00
165.00
165.00
61.60
114.00
108.00
5
3
5
2
6
10
6
2
2
2
7
25
6
5
3
5
3
3
7
6
•>
7
7
4
8
6
5
3
5
3
3
10
6
2
2
2
7
25
6
178.00
143.00
218.00
122.00
120.00
126.00
50.00
64.00
59.00
59.00
4.90
16.00
11.50
106.00
80.40
123.00
238.00
2.90
107.00
46.00
49.00
17.60
17.60
13.20
11.60
12.80
684.00
545.00
759.00
1040.00
326.00
1140.00
478.00
604.00
554.00
554.00
65,90
179.00
120.00
16
12
21
20
21
83.00
114.00
74.00
130.00
961.00
-------
APPENDIX B
PHYSICAL and CHEMICAL DATA
-------
STORE! RETRIEVAL DATE 74/11/26
363201
43 09 00.0 074 09 00.0
SACANDAG4 RESERVOIR
36 NEW YOPK
00010 00300 D0077 00094
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY
FROM OF TEMP SECCHI FIELD
TO DAY FEET CENT MG/L IMCHES MICROMHO
7P/05/18 10 20 0000 12.7 9.6 196 50
10 20 0010 7.5 11.7 SO
10 20 0030 7.1 9.4 50
72/07/31 08 45 0000 144 50K
08 45 0004 23.2 7.6 48
Ofl 45 0015 22.6 7.6 45
08 45 0022 18.2 5.0 40
08 45 0030 15.9 2.8 43
72/10/10 15 00 0000 120 50K
15 00 0004 13.8 9.2 50K
15 00 0015 13.3 9.4 50K
15 00 0022 13.2 9.2 50K
15 00 0031 12.9 9.2 50K
11EPALES
5
00400
PH
su
6.70
6.20
6.30
6.60
6.60
6.40
6.10
6.00
7.00
7.10
7.05
7. OS
7.00
00410
T AUK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
I OK
10K
10
2111202
0035
00630
N02S.N03
N-TOTAL
MG/L
0.430
0.450
0.470
0.210
0.210
0.200
0.220
0.200
0.090
0.090
0.110
0.100
0.120
FEET DEPTH
00610
NH3-N
TOTAL
MG/L
0.060
0.020
0.030
0.070
0.070
0.070
0.110
0.150
0.050
0.050
0.080
0.050
0.050
00665
PHOS-TOT
MG/L P
0.013
0.010
0.009
0.011
0.007
0.015
0.010
0.016
0.009
0.007
0.012
0.008
0.007
00666
PHOS-DIS
MG/L P
0.006
0.006
0.005
0.005
0.006
0.012
0.007
0.006
0.004
0.004
0.003
0.004
0.006
32217
DATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAV FEET ur,/L
72/05/18 10 20 0000 3.0J
72/07/31 08 45 0000 4.6J
72/10/10 15 00 0000 7.2J
K VALUE KNOWN TO rtf LKSS
TH»N INDICATED
J VALUF KNOWN TO H? I'M
-------
STORET RETRIEVAL DATE 74/11/26
363202
43 06 00.0 074 13 30.0
SACANDAGA RESERVOIR
36 NE* YORK
DATE TIME OEPTH
FROM OF
TO DAY FEET
72/OS/18 10 47 0000
10 47 0010
10 47 0035
7P/07/2H 11 50 0000
11 50 0027
72/07/31 07 55 0000
07 S5 0004
07 55 0015
07 55 0020
07 55 0024
72/10/10 14 30 0000
14 30 0004
14 30 0015
00010
•WATER
TEMP
CENT
13.4
9.6
7.1
16.3
22.4
22.3
21.6
20.1
14.0
00010
•WATER
TEMP
CENT
00300
DO
MG/L
00077
TRANSP
SECCHI
INCHES
00094
CNOUCTVY
FIELD
MICROMHO
00400
PH
su
10.0
11.5
10.?
3.0
R.4
8.4
7.6
4.4
P.6
9.3
139
144
13?
120
50
50
50
50K
50K
50K
50K
50K
50K
50K
50K
50K
11EPALES
4
00400
PH
su
6.90
6.60
6.'0
6.60
6.60
6.50
6.50
6.50
6.40
7.20
7.15
7.10
00410
T ALK
CAC03
MG/L
10K
10*
10K
12
10
10K
10K
10K
20
11
12
10K
2111202
0042
00630
N02S.W3
N-TOTAL
MG/L
0.400
0.450
0.500
0.200
0.190
0.200
0.200
0.200
0.200
0.080
o.oeo
0.090
FEET DEPTH
00610
NH3-N
TOTAL
MG/L
0.030
0.030
0.050
0.160
0.060
0.060
0.060
0.060
0.190
0.040
0.030
0.040
00665
PHOS-TOT
MG/L P
0.009
0.009
0.008
0.009
0.013
0.010
0.010
0.011
0.021
0.009
0.011
0.010
00666
PHOS-D1S
MG/L P
0.005
0.004
0.003
0.007
0.008
0.009
0.009
0.006
0.012
0.004
0.005
0.007
3?217
DATE TIME DEPTH CHL"*PHYL
FHOM OF A
TO DAY FEET UG/L
72/05/1* 10 47 0000 1.6J
72/07/31 07 55 0000 8.1J
72/10/10 14 30 0000 7.0J
K V/ALUK KNOWN TO
THAN INDICATE}
J VALUE KNOrtN TO
-------
STORE! RETRIEVAL DATE 74/1l/?6
363203
43 20 00.0 074 00 00.0
SACANOAGA RESERVOIR
36035 NEW YORK
00010
DATE TIME DEPTH WATER
FROM OF TEMP
TO DAY FEET CENT
72/07/31 09
09
09
09
09
72/10/10 15
15
15
15
15
15 0000
15 0004
15 0015
15 0025
15 0036
35 0000
35 0004
35 0015
35 0032
35 0029
24.4
?3.8
17.0
13.9
15.2
15.1
15.0
14.9
00300 00077 00094
DO TRANSP CNDUCTVY
SECCHI FIELD
MG/L INCHES MICPOMHO
144 50K
7.2 50K
7.6 50K
2.8 50K
4.6 50K
114 50K
8.6 50K
8.6 50K
8.6 50K
P.2 50K
11EPALES
6
00400
PH
SU
6.70
6.60
6.40
6.10
6.00
7.10
7.00
6.95
6.95
6.95
00410
T ALK
CAC03
MG/L
10K
10K
10K
10K
10K
10K
10K
10K
10K
10K
2111202
0036
00630
N-TOTAL
MG/L
0.210
0.210
0.220
0.240
0.260
0.120
0.120
0.130
0.130
0.120
FEET DEPTH
00610
NH3-N
TOTAL
MG/L
0.060
0.060
0.070
0.130
0.180
0.100
0.100
0.100
0.120
0.090
00665
PHOS-TOT
MG/L P
0.010
0.008
0.007
0.009
0.011
0.010
0.009
0.007
0.009
0.008
00666
PHOS-DIS
MG/L P
0.007
0.005
0.005
0.007
0.010
0.005
0.006
0.003
0.003
0.002
3?217
DATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAY FEF.T UG/L
72/07/31 09 15 0000 1.9J
72/10/10 15 35 0000 5.4J
K VALUc KNO*N TO SF LESS
TH«VN iNOICATrU
J VALUT KNOWN TO 4t I'M ERROH
-------
APPENDIX C
TRIBUTARY DATA
-------
STORE! RETRIEVAL DATE 74/11/26
3*3241 LS3632A1
43 14 00.0 074 12 00.0
UNNAMED CREEK
36 7.5/NORTHVILLE
T/SACANDAGA RESERVOIR
GIFFORO VALLEY ROAU BRIDGE
11EPALES 2111204
A. 0000 FEET
DEPTH
DATE
FROM
TO
7?/ll/05
7?/12/03
73/01/06
73/02/03
7.3/03/03
73/04/07
73/04/21
73/05/06
73/05/20
73/06/0?
73/07/07
73/OB/04
73/09/08
73/10/06
00630 006?5
TIME DEPTH NO?^N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
13
13
13
11
13
13
12
11
16
10
10
13
05
35
45
45
45
50
35
30
?5
15
15
00
15
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
034
064
147
105
099
05?
0?1
04?
0?3
015
033
640
410
029
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
1.
0.
300
150
250
120
460
115
540
?40
520
230
380
470
400
00610 00671 00665
MH3-M PHOS-OIS PHOS-TOT
TOTAL OPTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0,
0.
060
014
034
063
OS6
033
027
039
026
008
013
033
?52
063
MO/L
n.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
G.
0.
0.
P
005K
005K
005*
005K
005K
005K
005K
005K
010
005K
005K
005K
006
005K
MG/L P
O.OOM
0.005K
0.005K
0.005K
O.OOSK
0.015
0.005K
0.01S
0.010
0.010
0.010
0.015
O.OR5
0.010
K VALUh K.-iOW I 10 -Jc
LR.5S TH-.N r
-------
STOPET »ETPIEVAL HATE 74/U/26
DATE TIME DEPTH NO?^M(n
FPOM OF rj-TOTAL
TO DAf FEET MG/L
0.05?
0.083
0.034
0.09*
0.140
0.044
0.048
0.065
0.032
C.035
C.042
0.115
0.154
0.033
72/11/05
72/12/03
71/01/06
73/02/01
73/03/03
73/04/07
71/04/21
73/05/06
71/05/20
71/06/02
71/07/07
73/08/04
73/09/0«
71/10/06
15 35
15 00
14 40
14 4S
12 40
15 05
14 40
14 00
13 10
17 10
11 10
11 25
12 00
43 14 00.0 074 10 00.0
HUNTERS CREEK
36 7.5/NOWTHVILLE
T/SACANOAGA RESERVOIR
r'IMGE RO NE OF NORTHVILLE
11£PALES 2111304
4 oooo FEET
DEPTH
00625
TOT KJEL
N
MG/L
O.*30
0.100K
0.140
0.15C
0.120
0.500
0.330
1.050
0.520
0.580
0.440
0.420
0.920
0.319
00610
NM3-N
TOTAL
MG/L
C.084
0.025
0.02B
0.02.°
0.042
0.010
O.C4B
0.054
0.072
0.030
0.026
0.02^
0.120
0.040
00671
PHOS-OIS
ORTHO
MO/L P
0.005K
0.005K
0.005K
O.OC5K
0.005K
0.005K
0.005K
0.005K
O.OO'S
0.005K
0.005K
0.005K
0.009
0.005K
00665
PHOS-TOT
MG/L P
0.00*
0.006
0.005K
0.010
0.015
0.01S
C.010
0.030
0.010
0.010
0.020
0.020
0.035
0.015
K VALUT
TO
-------
STORET RETRIEVAL DATE 74/11/26
3632C1 LS3632C1
43 12 30.0 074 05 00.0
BATCHELLE* CREEK
36 7.5/EOlAJHUKG
T/SACANOAGA RESERVOIR
MEO DUTY «D H^IDGE NEAW BATCHELLErtVlLLE
11EPALES 2111204
4 0000 FEET DEPTH
0063U 00625
DATE TIME DEPTH NO&N03 TOT KJEL
FROM OF rt-TOTAL N
TO DAY FEET
72/1 I/OS 11 03
7P/12/03 09 30
73/01/05 08 30
73/02/02 09 05
73/03/06 Oft 14
73/04/10 10 03
73/04/16 09 00
73/05/06 10 20
73/05/1? 19 10
73/06/0? 09 ?6
73/07/02 07 45
73/08/07 09 40
73/09/25 10 4«5
73/10/06
MG/L
0.076
0.120
0.168
0.230
0.260
0.147
0.132
0.074
0.054
0.230
0.07?
0.150
0.078
MG/L
0.150
0.100K
O.lflO
0.520
0.200
0.100K
2.500
0.4?0
2.300
0.460
0.540
3.360
0.930
0.600
00610 00671 00665
MH3-N PHOS-DIS PHOS-TOT
TOTAL OPTHO
MG/L
0.050
0.006
0.013
0.060
0.038
0.021
0.070
0.034
0.063
0.105
0.092
0.790
0.060
0.056
MG/L P
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.006
O.OOR
0.005K
0.005K
0.003
0.005K
MG/L P
0.009
0.006
0.005K
0.015
0.010
0.005K
0.005K
0.015
0.020
0.010
0.020
0.005K
0.015
0.020
TO
THAN liJOICATEO
-------
00630
DATE TIME OEPTH NO?>>.N03
FPOM OF KJ-TOTAL
TO HAY FEFT MG/L
7?/ll/OS 10 07
7?/l?/03 09 00
73/01/05 0«* 10
73/02/0? 09 ?5
73/03/06 Ofl 54
73/0^/lG
73/04/l^j 09 30
73/05/06 10 10
73/05/1? 19 ?5
73/06/0? 09 05
73/07/02 07 00
73/08/07 09 58
73/09/25 10 ?B
73/10/06
0.(
0.110
0.
G.
O.i
C.147
0.13?
0.074
0.046
O.i
o.;
0.0^0
0.147
0.07M
3632U1 LS363PD1
>3 13 30.0 074 Ob 30.0
36
7.5/FOIMMUKG
006P5
TOT KJEL
N
MG/L
O.'IO
0.110
o.?«o
0.5?0
0.130
0.150
?.BOO
l.HOO
1.760
0.560
0.460
0.660
O.?30
0.640
00610
NH3-N
TOTAL
MG/L
0.046
O.OOP
O.OP3
0.044
a. 039
0.063
0.06S
0.052
0.050
0.03^
0.154
0.315
O.OP9
n.05C
00671
PHOS-DIS
OPTHO
MG/L P
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.005K
0.009
0.005K
0.005K
0.005K
0.006
0.005K
LK,HT DUTY
11F.PALE3
4
00665
PHOS-TOT
MG/L P
0.011
0.006
0.005K
0.010
0.005K
0.005K
O.Olu
0.025
0.010
0.015
0.010
0.006
0.005*
0.010
HWJOGE IN
2111204
0000 FEET DEPTH
TO
-------
STDPET RETRIEVAL DATE 74/11/26
LS3632E1
4.1 15 00.0 074 13 30.0
WEST STONY CREEK
36 15/HAHWIS-iURG
T/SACANOAGA RESERVOIR
BPDG AT CONFLUENCE WITH SA CANDAGA RIVER
IIE^ALES 2111204
^ 0000 FEET DEPTH
DATE
FROM
TO
7?/l 1/05
7?/l?/03
73/01/06
73/02/03
73/03/03
73/04/07
73/04/21
73/05/06
73/05/20
73/06/0?
73/07/07
73/08/04
73/09/OR
73/10/06
TIME DEPTH
OF
DAY FEET
14 30
13 45
13 50
14 40
12 00
14 05
13 45
1? 45
11 35
if> no
10 ?5
10 10
13 00
00630
,NO?*»N03
N-TOTAL
MG/L
0.234
0.2BO
0.357
0.490
0.315
0.290
0.260
0.140
0.198
0.060
0.040
0.115
0.05fl
0.014
00625
TOT KJEL
M
MG/L
0.210
0.160
0.360
O.fiOO
0.690
0.300
0.960
2.100
0.310
0.270
0.3?5
0.960
0.2«0
00610
NH3-N
TOTAL
MG/L
0.054
0.010
0.017
0.095
0.021
0.038
0.040
0.032
0.100
0.012
0.018
0.006
0.063
0.034
00671
PHDS-niS
ORTHO
MG/L D
0.005K
0.005K
0.005K
0.006
0.005K
0.005K
0.009
C.005K
0.006
0.005K
0.005K
O.OOSK
0.005K
0.005K
00665
PhOS-TOT
MG/L P
0.007
0.007
0.005K
0.014
0.010
0.01G
0.010
0.010
0.010
0.005K
0.010
0.015
0.010
0.010
V-\LUP"
THAN
TO
-------
PETKIFV.M. DATE 74/U/P6
3
-------
STOWFT RETRIEVAL DATE 74/1l/?6
3&32G1 LS3632G1
43 15 30.0 074 14 00.0
5ACANOAGA t-'IVE^
36 15/MARPISRUrtG
I/SACANDAbA RESERVOIR
HWY BRIDGE DOWNSTREAM OF M HAMPTON STP
11EPALFS 2111204
4 oooo FEET DEPTH
DATE
FROM
TO
7?/l 1/05
7?/l?/03
73/01/06
73/02/03
73/03/03
73/04/07
73/04/?l
73/05/06
73/05/20
73/06/02
73/07/07
73/OS/04
73/09/OR
73/10/06
00630 00625
TIME DEPTH NO?*,N03 TOT KJEL
OF N-TOTAL N
DAY FEET
14
13
13
14
12
14
13
1?
11
16
10
10
12
45
55
50
03
05
07
50
55
50
31
35
?0
10
00610 00671 00665
NH3-N HHOS-DIS PHOS-TOT
TOTAL OPTHO
MG/L ^G/L MG/L
0
0
0
0
0
0
0
0
0
0
0
0
f)
u
.338
.430
.560
.500
.400
.450
.430
.300
.380
• ??0
.110
.llv)
.072
.0-»6
0.
0.
0.
0.
0.
0.
0.
1.
3.
0.
0.
0.
1.
0.
260
330
?90
HOO
330
350
400
100
400
690
300
330
150
300
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
058
019
0?6
1 89
042
010
018
069
115
015
019
017
036
03?
MG/L
3.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0 .
0.
P
005K
005K
005K
008
005K
005K
005K
005K
005K
005K
005K
005K
0.005K
0.
005K
MG/L P
O.GO-}
0.011
0.005K
0.015
0.010
0.005K
0.005K
0.005K
0.010
0.005K
0.010
0.010
0.010
0.005K
VaLUF KNOWN TO
THAN I
t LESS
-------
STORET RETRIEVAL DATE 74/1l/?6
00630
DATE TIME DEPTH N02&NO?
F«OM OF N-TOTAL
TO DAY FEET
72/11/05 15 40
7?/}?/03 14 05
73/01/06 14 00
73/02/03 14 15
73/03/03 12 ?0
73/04/07 14 35
73/04/21 14 05
73/05/06 13 15
73/05/20 1? 10
73/06/0? 17 00
73/07/07 11 00
73/08/04 10 40
73/09/Oh
73/10/06 1? 30
0.340
0.420
0.530
0.490
0.390
0.420
0.390
0.237
0.340
0.220
C.100
0.105
0.05?
0.096
3632G? L
»1 21 30.0 07*4 16 00.0
36 IS/LAKE PLi-IASANT
T/SACANOAGA KESE^VOlK
GAGING STA NEAR PUMPKIN HOLLOW
i if PALES 21 11204
A 0000 FEET OEPTH
0062S
TOT KJFL
N
*r,/L
o.??o
0.270
0.330
0.230
0.740
0.610
0.33^
0.450
0.970
0.850
0.390
0.240
0.550
0.350
00610
NH3-N
TOTAL
Mfi/L
0.050
0.017
0.017
0.02Q
0.110
0.063
0.012
0.031
0.046
0.031
0.023
O.OOSK
0.037
0.032
00671
PHOS-DIS
CW HO
MG/L P
O.OOSK
O.OOSK
O.OOSK
O.OOSK
0.005K
O.OOSK
0.005K
O.OOSK
O.OOSK
O.OOSK
O.OOSK
O.OOSK
O.OOSK
O.OOSK
00665
PHOS-TOT
MG/L P
0.010
O.OOSK
O.OOSK
0.010
O.OOSK
0.010
O.OOSK
O.OOSK
0.010
0.010
0.01S
0.010
0.010
0.010
TO >->'r
-------
STORE! RETRIEVAL DATE 74/11/26
3632G3 LS3632G3
43 19 00.0 073 55 30.0
SAC4NDAGA HW-tW
36 15/LK L'JZFRME
0/SACANDAGA PESEKVOIR
CONKLINGV/ILLE 0AM AT NORTH SHORE *n
11EPALES 2111204
4 0000 EEET DEPTH
DATE
FROM
TO
7P/11/05
7P/12/03
73/01/05
73/03/02
73/01/06
73/04/10
73/04/16
73/05/06
73/05/1?
73/06/02
73/07/02
7.V08/07
73/09/P5
73/10/06
00630 006P5
TIME DEPTH N02&N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
11
OQ
08
18
08
08
11
18
08
19
08
09
00
10
40
10
5ft
13
40
00
30
00
55
?0
?5
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
095
088
240
315
390
300
350
399
370
052
097
160
140
0*8
MG/L
0.
0.
0.
0.
0.
0.
?.
2.
0.
0.
0.
0.
0.
0.
210
200
290
340
?30
120
000
200
330
7?0
460
H80
440
580
00610 00671 00665
NH3-N PHOS-OTS PHOS-TOT
TOTAL OPTHO
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
n.
0.
0.
0.
060
P29
028
041
052
02?
054
071
074
019
075
?80
075
042
MG/L
0.
0.
0.
0.
0.
0.
0.
0.
P
005K
005K
OOSK
005K
005K
005K
005K
005K
0.005K
0.
0.
0.
0.
0.
005K
OOSK
005K
OOSK
009
MG/L P
O.OOH
O.OOSK
0.005K
0.005*
O.OOSK
0.005K
0.005K
0.010
O.OOSK
0.010
0.015
O.OOSK
0.010
0.020
V&LUF f'NOrfN! TO H*-l LESS
T He 1*4 IMOICtTHO
-------
STORET RETRIEVAL DATE T*/\
LS3b3?Hl
<»3 16 10.0 074 03 30.0
SANO CREEK
36
T/SACANDAGA
NCWTH SHO4E RD R^IDGE IN 4R ST HAY
11EPALFS 2111204
4 0000 FEET OEPTH
DATF
TO
7P/11/OS
7?/l?/03
73/01/05
73/0?/0?
73/03/Ot)
73/04/10
73/04/16
73/OS/06
73/05/1?
73/06/0?.
73/07/0?
73/OP/07
73/09/?5
73/10/06
TIvE OFpT'
OF
OAY FEET
10
OR
07
ov
19
10
19
OB
19
OB
09
IS
10
SO
55
30
00
35
37
35
55
04
^ NO-->U!03 TOT KJFL
N-TOTAL M
MG/L
0
3
0
0
0
0
y
0
0
0
0
0
t)
,0
.1S6
.?73
.340
• 3^9
.37*
.147
. 1 3fl
.160
. 16H
.046
,04«
.16^
.140
.OBO
00610 00671 0066S
NM3-N PHOS-OI5 PHQS-TOT
TOTAL O^THO
MG/L MK/L
0.
0.
0.
i .
0.
0.
1.
0.
?.
0.
0.
0.
0.
0.
190
?10
180
P50
PQO
1BO
760
^80
ion
5RO
4^n
5^+0
?50
4?0
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
3 .
0.
017
014
017
OH3
05?
061
05?
023
100
Oil
066
?40
03P
033
MG/L P
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
OOSK
OOSK
005K
OOSK
OOSK
OOSK
OOSK
005K
OOSK
OOSK
OOSK
003
OOSK
005K
MG/L P
o.oo«
0.005K
0.010
0.045
0.0 OSR
O.OOSK
O.OOSK
O.OOSK
0.010
0.010
0.015
0.015
o.oio
0.010
V'iLUF <>IO*'J TO HI Lf"
TH/.M I
-------
STOWET RETRIEVAL DATE 74/11/26
3632J1 LS3632J1
43 18 30.0 074 00 00.0
PAUL CREEK
36 15/HA*RISbUrtG
T/SACANDAGA RESERVOIR
NOPTH SHORE RD BRIDGE IN DAY CFNTER
11EPALE5 3111204
4 0000 FEET DE°TH
DATE
F^OM
TO
72/11/05
7P/12/03
73/01/05
73/02/0?
73/03/06
73/04/10
73/04/16
73/05/06
73/05/1?
73/06/02
73/07/0?
73/08/07
73/09/25
73/10/06
00630 006?5
TIME DEPTH NO?^N03 TOT KJEL
OF N-TOTAL N
DAY FEET
10
07
07
10
19
09
10
09
19
OB
20
09
09
?3
30
30
10
50
30
15
45
45
47
15
00
45
MG/L
0
0
0
D
C
0
0
0
0
0
0
0
0
0
.097
.13?
.200
.240
.370
.140
.138
.056
.078
.050
.066
.210
.147
.080
MG/L
0.
0.
0.
0.
0.
0.
2.
1.
3.
1.
0.
1.
0.
0.
180
175
1RO
290
170
150
600
320
400
000
560
000
160
460
00610 00671 00665
NH3-N PHOS-niS PHOS-TOT
TOTAL ORTHO
MG/L MG/L
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
0.
044
010
020
030
034
017
066
027
?50
037
160
B40
019
02P
0.
0.
0.
0.
0.
0.
G.
0.
0.
0.
0.
0.
0.
0.
p
005K
005K
005K
005K
005K
005K
005K
005K
005K
005K
005K
016
005K
005K
MG/L P
0.007
0.005K
0.010
0.020
0.005K
O.OOSK
0.010
0.005K
0.010
0.010
0.010
0.020
0.005K
0.010
-------
RETRIEVAL DATE 74/11/26
DATE
TO
7P/I1/05
7?/|?/03
73/01/05
73/OP/O?
73/03/06
73/04/10
73/04/lh
73/05/Oc
73/C5/1?
73/06/0?
73/07/0?
73/08/07
73/OV25
73/10/06
00630
TI»-'F OEMTM NO?JwN03
OF H-TOTtL
OAY FEET MG/L
09 40
10 30
09 10
08 35
19 13
08 45
09 10
10 45
18 47
OH 15
19 10
G8 35
09 10
0.063
0.110
O.?00
0.231
(..315
0.310
0.350
0.054
0.058
U.040
0.036
C.081
0.140
O.Q80
3632K1 LS363?K1
43 17 00.0 07? 58 00.0
DALY CWEEK
i6 15/LK LUZFKNE
T/SACA%DA6A RESERVOIR
5 SHORE HO BRIDGE ^w OF OVERLOOK
2111214
0000 EEET DEPTH
C06?5
TOT KJEL
M
MG/L
0.280
O.^^O
0.370
f.?5ij
0.230
0.310
1 ,U00
1.150
1.000
o.?io
0.700
O.<*60
0.160
O.?70
00610
NH3-N
TOTAL
MG/L
0.044
0.02?
0.04*
0.050
0.060
0.03H
0.051
0.063
0.1 RO
0.006
0.176
0.147
0.031
0.03?
00671
Prios-nis
OPT-iO
MG/L P
0.005K
0.005K
O.OOSK,
O.OOSK
O.OOSK
O.OC5K
O.OOSK
O.OOSK
0.005K
O.OOSK
0.005K
0.005K
O.OOSK
0.005K
00665
PHOS-TOT
MG/L P
0.010
O.OOSK
O.OOSK
O.OOSK
0.005K
O.OOSK
O.OOSK
O.OOSK
0.010
0.010
0.020
0.010
0.015
0.010
TH;IN I
TO
LrSS
-------
RETRIEVAL OATE 74/1l/?6
3h32Ll
43 03 30.0 073 13 30.0
KE^iTTTO C«EE<<
36 7.5/RROAOALBIN
T/5ACANOAGA RESERVOIR
ST HWY 30 BRIDGE N OF BROADALBIN
11EPALES 2111204
4 0000 FEET DEPTH
DATE
FROM
TO
72/11/05
72/12/03
73/01/05
73/02/03
73/03/03
73/04/07
73/04/21
73/05/06
73/05/'0
73/06/02
73/07/07
73/08/0**
73/09/0^
73/10/06
TIMF DE°TH
OF
OAY FEF.T
16 20
15 30
15 25
13 30
13 50
16 05
15 15
14 20
14 00
15 45
11 55
13 35
0'
f^
01
(•>»
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
0,
c,
0,
-.30
*03
FAL
'L
,182
,?60
,320
.360
,450
.140
,210
.126
.110
.126
,290
.378
.320
.110
00625
TOT KJEL
M
MG/L
0.350
0.320
0.900
1.300
1.260
0.440
l.POO
0.460
1.100
0.4PO
0. 390
1.400
0.360
00610
NH3-N
TOTAL
MG/L
0.063
0.03?
0.044
0.13«
0.260
0.033
0.04R
0.073
0.019
0.034
0.025
0.015
O.OtfO
0.025
00671
PHOS-DIS
ORTHO
MG/L P
0.011
0.010
0.011
0.019
0.037
0.005K
0.017
0.008
0.006
0.010
0.009
0.012
0.016
0.011
00665
PHOS-TOT
MG/L P
0.054
0.029
0.033
0.070
0.065
0.025
0.035
0.015
0.027
0.035
0.035
0.035
U.04Q
0.030
KNOWN TO
THAN
------- |