U.S. ENVIRONMENTAL PROTECTION AGENCY
NATIONAL EUTROPHICATION SURVEY
WORKING PAPER SERIES
REPORT
ON
MOOSEHEAD LAKE
PISCATAQUIS AND SOMERSET COUNTIES
MAINE
EPA REGION I
WORKING PAPER No, 2
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
MOOSEHEAD LAKE
PISCATAQUIS AND SOMERSET COUNTIES
MAINE
EPA REGION I
WORKING PAPER No, 2
WITH THE COOPERATION OF THE
MAINE DEPARTMENT OF ENVIRONMENTAL PROTECTION
AND THE
MAINE NATIONAL GUARD
MAY, 1974
-------
1
CONTENTS
Page
Foreword II
List of Maine Study Lakes iv
Lake and Drainage Area Map v
Sections
I. Conclusions 1
II. Introduction 3
III. Lake and Drainage Basin Characteristics 4
IV. Lake Water Quality Summary 6
V. Nutrient Loadings 12
VI. Literature Reviewed 17
VII. Appendices 18
-------
11
FOREWORD
The National Eutrophication Survey was initiated in 1972 as a
research project in response to an Administration commitment to
investigate the nationwide 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 fresh water 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 APPROACFI
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, in fact, 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
This report documents the first stage of evaluation of lake and
watershed data collected from the study lake and its drainage basin.
It is formatted to provide state environmental agencies with specific
information for basin planning [ 3O3(e)], water quality criteria!
standards review [ 3O3(c)], clean lakes [ 5314(a,b)], and water quality
monitoring [ g106 and §305(b)] activities mandated by the Federal Water
Pollution Control Act Amendments of 1972.
-------
ut
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic
conditton 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.
AC KNOWLEDGMENT
The staff of the National Eutrophication Survey (Office of
Research & Development, U. S. Environmental Protection Agency)
expresses sincere appreciation to the Maine Department of
Environmental Protection for professional involvement and to the
Maine National Guard for conduct of the tributary sampling phase
of the Survey.
William R. Adams, Commissioner of the Department of Environmental
Protection, and William P. Hinckley and Matthew Scott of the Division
of Lakes and Biological Studies, provided invaluable lake documentation
and counsel during the course of the study.
Major General Edwin W. Heywood (Retired), then the Adjutant
General of Maine, and Project Officer Lieutenant Colonel Earl B. Adams
who directed the volunteer efforts of the forty-one participating Maine
National Guardsmen are also gratefully acknowledged for their assistance
to the Survey.
-------
iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF MAINE
LAKE NAME COUNTY
Moosehead Lake Piscataquis, Somerset
Estes Lake York
Long Lake Cumberl and
Bay of Naples & Sebago Lake Cumberland
Rangeley Lake Franklin
Long Lake Aroostook
Mattawamkeag Lake Aroostook
Sebasticook Lake Penobscot
-------
MOOSEHEAD LAKE
...—......_..—Direct Drainage Area Boundary
® Tributary Sampling Site
x lake Sampling Site
2 345
-------
MOOSEHEAD LAKE
STORET NO. 2309
I. CONCLUSIONS
A. Trophic Condition:
High water clarity and dissolved oxygen values observed in
association with low nutrient levels and chlorophyll a concen-
trations are indicative of an oligotrophic condition In
Moosehead Lake. This conclusion is corroborated by personnel
of the Maine Department of Environmental Protection and the
Department of Inland Fisheries and Game.
B. Rate-Limiting Nutrient:
Algal assay results and nutrient concentration ratios
observed in lake waters Indicate Moosehead Lake was phosphorus
limited when sampled. However, nutrient spiked subsample
growth yields suggest nitrogen limitation would occur with an
approximate two fold increase In orthophospProrus concentration
(to about l6 ig/l, assuming constant inorganic nitrogen levels).
C. Nutrient Sources; Controllability:
1. Point Sources — Other than septic tank seepage, there
are no known point source discharges to the Moosehead Lake
drainage basin. However, a grant has been awarded recently to
the Moosehead Sanitary District for construction of a collection
system and tertiary treatment plant to serve the villages of
Greenville and Greenville Junction. Although plant effluent
will be discharged to the lake, the required combination of high
treatment and phosphorus removal should not compromise Moosehead
Lake water quality.
-------
2
2. Non-Point Sources - Over 99% of calculated phosphorus
and nitrogen loadings can be attributed to non-point sources.
The Moose River, draining approximately 63% of the total lake
watershed, contributes 40.1% of the total phosphorus and 43.1%
of total nitrogen. Notwithstanding the percentages attributable
to this and other areal sources, comparison of observed phos-
phorus loading rates with the Vollenweider model indicate no
apparent threat to present lake trophic condition.
-------
3
II. INTRODUCTION
Moosehead Lake is the largest lake in the State of Maine and is the
headwater of the Kennebec River. The watershed is predominantly forested.
The lake level is controlled for hydroelectric storage by the Kennebec
Water Power Company; other industrial uses include pulpwood storage and
transport. The lake is not used as a municipal water supply; however, some
shoreline camps and dwellings use the lake as a source of water.
Moosehead Lake has been famous for salmon and trout fishing since the
middle of the 19th century; reportedly, no other Maine lake studied provides
a better habitat for salmon, brook trout, and lake trout. Other recreational
uses include aesthetics, boating, and swimming, although low water tempera-
tures are said to discourage whole-body contact recreation.
-------
4
LAKE AND DRAINAGE BASIN CHARACTERISTICS
Lake Morphometry:
1. Surface area: 74,890 acres
2. Mean depth: 54 feet
3. Maximum depth: 246 feet
4. Volume: 4,043,760 acre/ft
5. Mean hydraulic retention time: 3 years
B. Tributary and Outlet:
(See Appendix A for flow data)
1. Tributaries* -
* Mean flows based on the period October 1, 1961 - September 30, 1971
± Drainage areas are accurate within ±1% and mean annual flows within ±5%.
III.
A.
Name
Moose River
Drainage
areat
Mean
1,104.6
flowt
cfs
720.0
mi 2
Tomhegan Stream
23.7
mi 2
39.4
cfs
.
Roach River
69.6
.2
mi
116.6
cfs
Lily Bay Brook
13.4
mi 2
26.8
cfs
Mud Brook
4.6
mi 2
7.9
cfs
Beaver Creek
9.0
mi 2
14.7
cfs
Unnamed Brook (J-1)
7.3
mi 2
14.0
cfs
Squaw Brook
7.0
.2
mi
13.0
cfs
Upper Squaw Brook
5.8
mi 2
9.4
cfs
Minor tributaries &
289.0
nh 2
522.0
cfs
immediate drainage
Totals
-
1,149.4
nii 2
1 ,868.4 cfs
-------
5
Name Drainage area Mean flowt
2. Outlet -
Kennebec River (East Outlet) 1,266.4 m1 2 * 1,804.1 cfs
West Outlet 1,266.4 mi 2 * 64.2 cfs
Totals 1,266.4 mi 2 1,868.3 cfs
C. Precipitation**:
1. Year of sampling: 56.0 inches
2. Mean annual: 43.3 inches
*Includes area of lake
**See Working Paper No. 1, “Survey Methods.”
See preceding page
-------
6
IV. LAKE WATER QUALITY SUMMARY
Moosehead Lake 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 seven
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 or
less to surface depending on station depth) sample was composited from
the seven stations for phytoplankton identification and enumeration;
and during the last visit, three five—gallon depth—integrated samples
were composited from three groups of stations (1 ,2, and 3; 4 and 5; and
6 and 7) for algal assays. Also, each time depth-integrated samples
were collected at the stations for chlorophyll a analyses. Maximum
depths sampled were 11 feet at station 1, 9 feet at station 2, 39 feet
at station 3, 8 feet at station 4, 17 feet at station 5, 13 feet at
station 6, and 100 feet at station 7.
It should be noted that the Survey Secchi disc values are con-
sistently less than those observed by the Maine Department of
Environmental Protection. Such variations could be attributed to
fluctuations in cloud cover or sun angle (ambient light conditions),
observer technique, water surface disturbance, or may, in fact, be the
result of short-term water clarity differences.
The results obtained are presented in full in Appendix B; and the data
for the fall sampling period, when the lake was essentially well-mixed, are
-------
7
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:
FALL VALUES
(10/01/72)
Parameter Minimum Mean Median Maximum
Temperature (Cent.) 12.6 13.7 13.8 14.1
Dissolved oxygen (mg/i) 9.0 9.3 9.2 12.4
Conductivity (pnihos) 50 50 50 50
pH (units) 6.6 6.7 6.7 7.0
Alkalinity (mg/i) 10 10 10 10
Total P (mg/i) 0.006 0.009 0.009 0.013
Dissolved P (mg/i) 0.005 0.007 0.007 0.009
NO + NO (mg/i) 0.080 0.137 0.140 0.150
Am onia ?mg/l) 0.030 0.045 0.040 0.080
ALL VALUES
Secchi disc (inches) 90 149 144 264
B. Biological characteristics:
1. Phytoplankton -
Sampling Dominant Number
Date Genera per ml
06/05/72 1. Dinobryon 49
2. Synedra 30
3. Cryptomonas 22
4. Asterionella 20
5. Peridinium 10
Other genera 37
Total
1 68
-------
8
Sampling Dominant Number
Date Genera per ml
08/09/72 1. Dinobryon 197
2. Cycioteila 51
3. Merismopedia 45
4. Polycystis 34
5. Fragilaria 34
Other genera 124
Total 485
10/01/72 1. Fragilaria 2,387
2. Cyclotella 1,382
3. Melosira 1,005
4. Anabaena 477
5. Aphanothece 402
Other genera 1,558
Total 7,211
2. Chlorophyll a -
(Because of instrumentation problems during the 1972 sampling,
the following values may be in error by plus or minus 20 percent.)
Sampling Station Chlorophyll a
Date Number ( pg/i )
06/05/72 01 1.2
02 0.6
03 0.6
04 1.2
05 1.1
06 1.2
07 1.0
08/09/72 01 2.8
02 3.3
03 2.0
04 2.2
05 2.0
06 1.2
07 1.2
-------
9
2. Autoclaved, filtered, and nutrient
tions 4 and 5) -
spiked (composite - sta-
Spike (mg/i )
Control
0.006 p
0.012 P
0.024 P
0.060 p
0.060 p + 10.0 N
10.0 N
Ortho P
Conc. (mg/i )
0.010
0.016
0.022
0.034
0.070
0.070
0.010
Inorganic N
Conc. (mg/i )
0.099
0.099
0.099
0.099
0.099
10 .099
1 0 .099
Maximum yield
( mg/i-dry wt. )
0.8
1.7
1.7
1 .8
1 .8
34.9
1.0
Sampling
Date
10/01/72
Station
Number
01
02
03
04
05
06
07
Chlorophyll
(pg/i)
a
1.7
1.5
1.3
-
1.1
1.1
1.3
C.
Limiting Nutrient Study:
1. Autoclaved, filtered,
tions 1,2, and 3) -
and nutrient
spiked
(composite - sta-
Ortho P Inorganic N Maximum yield
Conc.O! J]j Conc. (mg/l) (mg/l-dry wt.)
Spike (mg/i)
Control
0.001
0.149
0.3
0.006 P
0.007
0.149
0.7
0.012 p
0.013
0.149
2.8
0.024 p
0.025
0.149
2.9
0.060 P
0.061
0.149
2.7
0.060 p +
10.0
N
0.061
10.149
26.2
-------
10
3. Autoclaved, filtered, and nutrient spiked (composite - sta-
tions 6 and 7) -
Ortho P Inorganic N Maximum yield
Spike (mg/i) Conc. (mg/i) Conc. (mg/i) ( mgfl-dry wt. )
Control 0.004 0.122 0.3
0.006 P 0.010 0.122 0.8
0.012 P 0.0.6 0.122 1.8
0.024 P 0.028 0.122 1.6
0.060 P 0.064 0.122 1.9
0.060 P + 10.0 N 0.064 10.122 27.8
10.0 N 0.004 10.122 0.2
4. Discussion -
The three control yields of the assay alga, Selenastrum
capricornutum , indicate the potential primary productivity of
Moosehead Lake was relatively low at the time the samples were
collected. Also, in each assay, the increased yield result-
ing from the first orthophosphorus spike shows that Moosehead
Lake was phosphorus limited. At ortho-P concentrations higher
than about 0.013 to 0.016 mg/i, yields did not change signifi-
cantly until nitrogen was also added which indicates the lake
would become nitrogen limited if ortho-P concentrations in
the lake were increased to about 0.016 mg/i (note that the
addition of only nitrogen produced yields not significantly
different than the control yields).
The minor differences in yields in the three assays are
due to differences in the initial (control) concentrations
-------
11
of phosphorus which may have resulted from the autoclaving
of the samples, sample storage or actual differences
between the sampling sites.’
Lak data indicate that Moosehead Lake was phosphorus
limited at the other sampling times as well (nitrogen to
phosphorus ratios exceeded 25 to 1; i.e., phosphorus
limitation would be expected).
D. Trophic Condition
Survey data indicate that Moosehead Lake is oligotrophic.
Nutrient and chlorophyll a concentrations were very low and
Secchl disc transparencies were exceptional, even though perhaps
in error (see page 6). No depression of oxygen below saturation
was noted at any depth to 53 feet) except for the August sample
at station 3, at the 15-foot level, which was recorded as 7.4 mg/i
(82% of saturation). This is probably an analytical or recording
error, however, since samples collected at the same time above
(at 4 feet) and below (at 25 feet) were both oxygen-saturated.
-------
12
V. NUTRIENT LOADINGS*
(See Appendix B for data)
For the determination of nutrient loadings, from September 1972,
through August 1973, the Maine National Guard collected monthly near-
surface grab samples from the tributary sites indicated on the map
(page v), except for the high runoff months of April and May when two
samples per month were collected. Stream flow estimates were provided
by the Maine District Office of the U. S. Geological Survey through an
interagency agreement.
In this report, tributary nutrient loads were calculated with mean
concentrations and mean flows. The loads for unsampled “minor tribu-
taries and immediate drainage” (“ZZ” of U.S.G.S.) were calculated using
mean ZZ flows and mean Tonihegan Stream concentrations at station 0-1.
There were no municipal or industrial point sources discharging to
the Moosehead Lake drainage system during the Survey sampling year.
A. Waste Sources:
1. Municipal — None known
2. Industrial - None known
B. Annual Total Phosphorus Loading - Average Year:
1. Inputs —
lbsP/ %of
Source yr total
a. Tributaries (non-point load) -
Moose River 21,740 40.1
Tomhegan Stream 1,160 2.1
Roach River 1,840 3.4
Lily Bay Brook 630 1.2
* Based on sampling frequency and variations in concentrations, single
tributary loadings for gaged sites are believed to be within ±16% of
the true value 67% of the time and within ±32% of the true value 95%
of the time.
-------
13
lbsP/ %of
Source yr total
a. Tributaries (non-point load)
Mud Brook 220 0.4
Beaver Creek 290 0.5
Unnamed Brook (J-l) 580 1.1
Squaw Brook 220 0.3
Upper Squaw Brook 200 0.3
b. Minor tributaries &
imediate drainage
(non-point load)*_ 15,410 28.4
c. Municipal STP’s -
None known
d. Septic tanks** - 300 0.6
e. Industrial -
None known - -
f. Direct Precipitation* - 11,700 21.6
Total 54,270 100.0
2. Outputs -
Kennebec River, Last Outlet 28,410 96.6
West Outlet 1,010 3.4
Total 29,420 100.0
3. Net annual P accumulation - 24,850 lbs
* Estimated; see Working Paper No. 1, “Survey Methods”.
** Estimated 900 dwellings around lake; 25% permanent residences.
-------
14
Source _______
a. Tributaries (non-point load) -
Moose River
Tomhegan Stream
Roach River
Lily Bay Brook
Mud Brook
Beaver Creek
Unnamed Brook (J.-1)
Squaw Brook
Upper Squaw Brook
b. Minor tributaries &
immediate drainage
(non-point load)* -
c. Municipal STP’s -
None known
d. Septic tanks** -
e. Industrial -
None known
f. Direct precipitation* -
Iota 1
2. Outputs -
Kennebec River, East Outlet 1 ,960,480
West Outlet 60,540
Total 2,021,020
3. Net annual N accumulation - 673,850 lbs.
C. Annual Total Nitrogen Loading - Average Year:
1 1. Inputs —
lbs NI
yr
1,161,210
40,800
112,940
33,450
12,470
15,110
28,000
8,320
8,460
% of
total
43.1
1.5
4.2
1.2
0.5
0.6
1 .0
0.3
0.6
540,430 20.1
11,320 0.4
722,360
2,694,870
26.8
100.0
97.0
3.0
100.0
* Estimated; see Working Paper No. 1, “Survey Methods”.
** Estimated 900 dwellings around lake; 25% permanent residences.
-------
15
0. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary lbs P/mi 2 /yr lbs N/mi 2 /yr
Moose River 30 1,613
Tomhegan Stream 49 1 ,722
Roach River 26 1,623
Lily Bay Brook 47 2,496
Mud Brook 48 2,711
Beaver Brook 32 1 ,679
Unnamed Brook (J-1) 79 3,836
Squaw Brook 29 1 ,189
Upper Squaw Brook 34 1 ,459
E. Yearly Loading Rates:
In the following table, the existing phosphorus loading
rates are compared to those proposed by Vollenweider (1973).
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 oligotrophic
if morphometry permitted. A mesotrophic rate would be considered
one between “dangerous” and “permissible”.
Total Phosphorus Total Nitrogen
Units Total Accumulated Total Accumulated
lbs/acr /yr 0.7 0.3 36.0 9.0
grams/rn /yr 0.08 0.03 4.0 1.0
Vollenweider loading rates for phosphorus (g/m 2 /yr) based on mean
depth and mean hydraulic retention time for Moosehead Lake:
“Dangerous” (eutrophic rate) 0.46
“Permissible” (oligotrophic rate) 0.23
-------
16
E. Controllability of Nutrients:
1 . Discussion —
During the sampling year, it is estimated that less than
1% of the phosphorus load to Moosehead Lake was contributed
by point sources (septic tanks), and it is noted that the an-
nual total phosphorus loading rate was well below the “per-
missible” (oligotrophic) rate proposed by Vollenweider.
The impact of the Moosehead Sanitary District tertiary
treatment plant effluent on the overall trophic condition of
Moosehead Lake should be minimal; and, as long as the pro-
posed high level of 90+% phosphorus removal is maintained,
there should be little, if any, localized effect in the cove
receiving the effluent.
-------
17
VI. LITERATURE REVIEWED
Anonymous, 1953. Moosehead Lake survey report. Dept. of Inland
Fisheries & Game, Augusta.
Auclair, Roger P., 1972. Personal communication (physical, chemical,
and biological characteristics of Moosehead Lake). Dept. of In-
land Fisheries & Game, Greenville.
Johnson, Paul R., 1973. Personal communication (survey of Moosehead
Lake shoreline developments; present and planned sewage systems
in vicinity of lake; chemical and biological lake data). Dept.
of Inland Fisheries & Game, Greenville.
Scott, Matthew, 1974. Personal communication (trophic condition and
uses of Moosehead Lake). Dept. of Environmental Protection,
Augusta.
Vollenweider, Richard A., 1973. Input-output models. MS, Canada
Centre for Inland Waters, Burlington, Ontario.
-------
18
VII. APPENDICES
APPENDIX A
TRIBUTARY FLOW DATA
-------
IRItIUTANY FLOW INFORMATION FOR MAINE 6/25/74
LAKE CODE 2309 MOOSEHEAD LAKE
TOTAL DRAINAGE AREA OF LAKE 1246.00
SUB-DRAINAGE NORMALIZED FLOWS
TPIBIJTAPY AREA JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC MEAN
210941 1266.00 1658.00 1278.00 1817.00 2410.00 2820.00 2454.00 599.00 2533.00 2368.00 1831.00 2124.00 1906.00 1985.06
2309111 I?66.00 58.00 46.00 38.00 50.00 114.00 84.00 76.00 62.00 66.00 58.00 55.00 62.00 64.24
2109C1 720.00 1167.00 600.00 597.00 794.00 2845.00 1340.00 918.00 1101.00 1039.00 831.00 929.00 1035.00 1104.59
230901 23.70 19.00 14.00 25.00 127.00 107.00 32.00 16.00 13.00 14.00 24.00 46.00 35.00 39.37
?109E 1 69.60 143.00 102.00 79.00 156.00 208.00 136.00 81.00 37.00 78.00 149.00 106.00 123.00 116.59
2109F 1 11.40 11.00 9.10 19.00 105.00 57.00 18.00 9.50 7.10 9.70 19.00 35.00 23.00 26.85
2109 ,l 4.41 5.50 4.30 11.00 27.00 15.00 4.80 2.10 1.70 1.90 3.70 9.10 8.20 7.86
? 309M1 9.04 10.00 8.60 22.00 52.00 26.00 8.90 3.80 2.70 3.30 6.40 18.00 15.00 14.71
2109J 1 7.29 7.40 5.70 16.00 54.00 26.00 8.40 3.70 2.80 4.60 8.20 19.00 12.00 13.95
2109K1 6.96 8.20 5.90 12.00 41.00 33.00 10.00 4.60 3.80 4.00 7.30 14.00 12.00 12.99
2109L 1 5.83 7.60 5.50 12.00 27.00 23.00 7.00 3.00 2.50 2.30 4.00 9.00 9.20 9.35
21097? 404.00 174.00 313.00 620.00 1520.00 1313.00 509.00 188.00 123.00 125.00 201.00 525.00 451.00 521.93
SUMMARY
TOTAL DRAINAGE AREA OF LAKE = 1266.00 TOTAL FLOW IN = 22356.84
SUM OF SUB—DRAINAGE AREAS = 1266.43 TOTAL FLOW OUT 24567.00
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW OAY FLOW
230941 9 72 2255.00 16 1580.00
10 7? 1503.00 14 727.00
11 72 897.00 4 683.00
12 7’ 1542.00 10 896.00
1 71 1395.00 6 1160.00
2 73 2163.00 4 285.00
3 73 2573.00 3 3890.00
4 71 4500.00 7 5170.00 21 596.00
5 73 6911.00 5 7940.00 19 5190.00
6 73 2589.00 2 4300.00
7 73 3310.00 14 1740.00
8 73 1758.00 17 1370.00
230981 9 7? 20.00 16 20.00
ID 72 20.00 14 20.00
11 7? 40.00 4 36.00
I? 7? 40.00 10 40.00
1 73 50.00 6 50.00
2 73 40.00 4 45.00
3 73 35.00 3 35.00
4 73 40.00 7 35.00 21 45.00
5 73 65.00 5 40.00 19 75.00
6 73 75.00 2 75.00
7 73 70.00 14 70.00
11 71 60.00 17 60.00
-------
1P1BUTA, Y FLOW INFORMATION FOR MAINE
6/25/74
LAKE CODE 2309
MOOSENEAD LAKE
MEAN MONTMLY FLOWS AND OAILY FLOWS
TRIOUTARY MONTN YLAR MEAN FLOW DAY
9 7’ 232.00
10 72 1250.00
I I 72 1570.00
1? 72 1970.00
1 73 573.00
2 71 976.00
1 73 369.00
4 73 2380.00
5 73 3730.00
6 73 1570.00
7 73 1060.00
9 73 887.00
9 72 45.00
10 7? 36.00
II 72 92.00
72 55.00
73 32.00
2 73 46.00
3 74.00
4 73 159.00
5 73 154.00
5 73 42.00
7 73 90.00
8 73 130.00
9 7’ 112.00
10 7? 397.00
I l 72 247.00
12 7 167.00
73 159.00
7 73 218.00
3 73 485.00
4 71 114.00
5 73 449.00
6 73 87.00
7 73 339.00
8 73 275.00
9 7? 31.00
1 (3 72 79.00
I l 72 70.00
12 72 36.00
1 73 19.00
2 73 30.00
1 73 56.00
4 73 131.00
5 73 02.00
6 73 23.00
7 71 53.00
A 73 71.00
FLOW DAY FLOW DAY
16 232.00
14 1480.00
4 961.00
10 2550.00
6 533.00
4 970.00
3 533.00
284.00
5 7750.00
2 4300.00
14 985.00
17 970.00
16 21.00
14 28.00
4 79.00
10 76.00
6 22.00
4 132.00
3 17.00
7 89.00
5 137.00
2 192.00
14 47.00
17 60.00
16 87.00
14 386.00
4 230.00
10 194.00
6 134.00
4 423.00
3 301.00
7 11.00
5 423.00
2 151.00
14 278.00
17 219.00
16 15.00
I’ 22.00
4 60.00
10 50.00
6 13.00
4 86.00
3 13.00
7 73.00
5 73.00
2 44.00
14 25.00
17 43.00
FLOW
?10 C 1
I
210901
210 0c
21 602.00
19 5200.00
21 207.00
19 143.00
21 185.00
19 432.00
21 170.00
19 76.00
-------
TRIBUTARY FLOW INFORMATION FOR MAINE 6/25/74
LA F CODE 2309 HOOSEHEAD LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
230 9 F,1 9 72 6.10 16 2.90
10 72 5.60 14 4.30
11 72 18.00 4 15.00
12 72 13.00 10 18.00
1 73 9.30 6 6.40
2 73 14.00 4 40.00
3 73 32.00 3 7.40
4 73 34.00 7 19.00 21 44.00
5 73 27.00 5 20.00 19 20.00
6 73 6.20 2 12.00
7 73 12.00 14 5.60
B 73 17.00 17 10.00
2309H 1 9 72 11.00 16 5.20
10 72 9.70 14 7.50
11 72 36.00 4 31.00
12 72 24.00 10 33,00
1 73 17.00 6 12.00
7 73 28.00 4 81.00
3 73 65.00 3 15.00
4 73 65.00 7 36.00 21 84.00
5 73 37.00 5 33.00 19 34.00
6 73 12.00 2 23.00
7 73 21.00 14 9.90
8 73 27.00 17 16.00
2309J 1 9 72 14.00 16 6.60
10 72 12.00 14 9.20
ii 72 38.00 4 33.00
12 72 19.00 10 26.00
1 73 13.00 6 9.00
2 73 19.00 4 55.00
3 73 47.00 3 11.00
4 73 68.00 7 38.00 21 88.00
5 73 37.00 5 33.00 19 34.00
6 73 11.00 2 21.00
7 73 21.00 14 9.90
8 73 28.00 17 17.00
2309’( l 9 72 13.00 16 6.10
10 72 11.00 14 8.50
11 72 28.00 4 24.00
12 72 19.00 10 26.00
1 73 14.00 6 9.70
2 73 19.00 4 55.00
3 73 35.00 3 8.00
4 73 51.00 7 29.00 21 66.00
5 73 48.00 5 43.00 19 45.00
6 73 13.00 2 25.00
7 73 26.00 14 12.00
8 73 38.00 17 23.00
-------
TPIBtJTARY FLOW INFORMATION FOR MAINE 6/25/74
LA’cE CODE ?309 MOOSEHEAD LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
2309L1 9 72 7.40 16 3.50
10 72 6.10 14 4.70
11 72 18.00 4 15.00
1? 72 15.00 10 21.00
1 73 13.00 6 9.00
2 73 18.00 4 52.00
3 13 15.00 3 8.00
4 73 34.00 7 19.00 21 44.00
5 73 33.00 5 29.00 19 31.00
6 73 9.10 2 17.00
7 73 17.00 14 8.00
8 73 25.00 17 15.00
?1O9ZZ 9 7? 401.00
10 72 306.00
11 72 1040.00
1? 72 713.00
1 73 612.00
2 73 10?0.O0
3 73 1820.00
4 73 1900.00
5 73 1890.00
6 73 66?.00
7 73 1060.00
8 73 1230.00
-------
APPENDIX B
PHYSICAL AND CHEMICAL DATA
K - Value is less than indicated
J - Value known to be in error
-------
STORET RETRIEVAL DATE 74/06/25
DATE
FROM
TO
72/06/05
72/08/09
72/10/01
TIME DEPTH
OF
DAY FEET
09 12 0000
08 35 0000
10 05 0000
32217
C ML P PHYL
A
UG/L
I .2J
2.8J
1 • 7J
230901
45 27 48.0 069 35 48.0
MOOSEHEAD LAKE
23 MAINE
I 1EPALES
3
00010
00300
00077
00094
00400
00410
00630
00610
00665
00666
DATE
TIME DEPTH WATER
DO
TRANSP
CNDUCTVY
PH
1 ALK
N02&NO3
NH3—N
PHOS—TOT
PHOS—DIS
FROM
OF
TEMP
SECCHI
FIELD
CACO3
N—TOTAL
TOTAL
TO
DAY FEET
CENT
MG/L
INCHES
MICROMHO
SI)
MG/L
MG/L
MG/I
MG/I P
MG/L P
2111202
0011 FEET DEPTH
72/06/05
09
12
0000
8.2
12.0
120
10
7.00
10K
0.160
0.040
0.003
0.002
09
12
0010
8.2
11.2
10
6.80
10K
0.160
0.040
0.005
0.003
72/08/09
08
35
0000
144
50K
6.70
10
0.140
0.140
0.003
0.002K
08
35
0006
18.8
8.8
50K
6.70
11
0.060
0.060
0.002K
0.002K
08
35
0011
18.7
8.6
50K
6.70
10
0.150
0.070
0.002
0.002
72/10/01
10
05
0000
120
50K
6.60
10K
0.130
0.040
0.010
0.007
tO
Os
0004
12.7
9.4
50K
6.92
10K
0.130
0.040
0.009
0.006
10
05
0009
12.6
9.2
50K
7.00
10K
0.130
0.040
0.009
0.006
-------
STORET RETRIEVAL DATE 74/06/25
230902
45 28 24.0 069 36 06.0
MOOSEHEAD LAKE
23 MAINE
11EPALE S 2111202
3 0010 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH 1 AIK N021N03 NH3—N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 N—TOTAL TOTAL
TO DAY FEET CENT MG/L INCHES MICROMNO SU MG/L MG/I MG/I MG/I P MG/I P
72/06/05 10 40 0000 8.3 12.1 100 10 6.90 10K 0.170 0.020 0.002 0.002K
10 40 0009 7.7 12.3 10 6.80 10K 0.160 0.010 0.002 0.002K
72/08/09 09 00 0000 132 50K 6.80 10K 0.160 0.160 0.007 0.002
09 00 0004 18.7 9.0 50K 6.80 10 0.050 0.060 0.002K 0.002K
09 00 0009 18.6 9.0 50K 6.70 10 0.150 0.050 0.002K 0.002K
72/10/01 10 30 0000 102 50K 6.75 10K 0.140 0.070 0.010 0.008
10 30 0005 13.1 9.6 50K 6.85 10K 0.130 0.040 0.008 0.008
32217
DATE TIME DEPTH CHLRPHYI
FROM OF A
TO DAY FEET UG/L
72/06/OS 10 40 0000 0.6J
72/08/09 09 00 0000 3.3J
72/10/01 10 30 0000 1. SJ
-------
STORET RETRIEVAL DATE 14/06/25
230903
45 28 06.0 069 37 06.0
MOOSEHEAD LAKE
23 MAINE
I IEPALES 2111202
3 0011 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME OEPTH WATER DO TRANSP CNDUCTVY PH T ALK N02&N03 NH3-N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 N—TOTAL TOTAL
TO DAY FEET CENT WG/L INCHES MICROMHO SU MG/L MG/L MG/I MG/L P MG/I P
72/06/05 11 00 0000 8.0 11.9 144 10 6.90 10K 0.170 0.030 0.002 0.002
11 00 0010 7.8 12.0 10 6.90 10K 0.160 0.040 0.002 0.002K
72/08/09 09 25 0000 182 50K 6.80 10K 0.160 0.110 0.002K 0.002K
09 25 0004 18.4 9.0 50K 6.80 10K 0.080 0.020 0.002K 0.002K
09 25 0015 18.2 7.4 50K 6.80 10K 0.070 0.030 0.002K 0.002K
09 25 0025 18.1 9.0 50K 6.80 10K 0.070 0.020 0.006 0.002
09 25 0035 13.4 9.4 50K 6.50 lOX 0.100 0.060 0.002 0.002K
09 25 0039 11.7 11.8 50K 6.50 lOic 0.030 0.030 0.005 0.002
72/10/01 10 50 0000 204 50K 6.15 10K 0.140 0.040 0.010 0.008
10 50 0004 9.2 50K 6.65 10K 0.130 0.030 0.009 0.006
10 50 0015 13.5 9.0 50K 6.70 10K 0.140 0.040 0.007 0.006
10 50 0022 13.5 9.2 50K 6.60 10K 0.140 0.040 0.007 0.007
10 50 0029 13.5 9.2 50K 6.90 10K 0.140 0.040 0.001 0.006
32217
DATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAY FEET UGh
72/06/05 Il 00 0000 0.6J
72/08/09 09 25 0000 2.0)
72/10/01 10 50 0000 1.3J
-------
STORET RETRIEVAL DATE 74/06/25
230904
45 41 00.0 069 45 54.0
MOOSEHEAD LAKE
23 MAINE
1 IEPALES 2111202
3 0011 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME DEPTH WATER DO TRANSP CNOUCTVY PH T ALK N02 NO3 P*43—N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 N—TOTAL TOTAL
TO DAY FEET CENT MG/L INCHES MICROMHO SU MG/I. MG/L MG/L MG/L P MG/L P
72/06/05 11 30 0000 14.3 10.9 90 10 6.80 10K 0.130 0.030 0.004 0.003
11 30 0010 14.3 10.9 10 6.90 10K 0.130 0.030 0.005 0.003
72/08/09 17 45 0000 96 50K 6.70 10K 0.120 0.110 0.007 0.005
17 45 0004 20.2 9.0 50K 6.70 10K 0.010K 0.050 0.006 0.003
17 ‘.5 0008 18.6 9.0 50K 6.70 10K 0.100 0.010K 0.005 0,004
72/10/01 15 05 0000 96 ioic 0.080 0.040 0.009 0.007
15 05 0004 13.5 9.0 50K 6.80 10K 0.090 0.070 0.010 0.009
32217
DATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAY FEET UG/L
72/06/05 11 30 0000 1.2J
72/0ô/09 17 45 0000 2.2J
72/10/0 I 15 05 0000 1.1
-------
STORET RETRIEVAL DATE 74/06/25
230905
45 51 36.0 069 38 00.0
MOOSEHEAD LAKE
23 MAINE
IIEPALES 2111202
3 0019 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH T 61K N02&N03 NH3—N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 N—TOTAL TOTAL
TO DAY FEET CENT MG/I INCHES MICROMHO SU MG/I MG/L MG/L MG/L P MG/L P
72/06/05 12 05 0000 12.8 11.2 192 10 7.00 10K 0.160 0.030 0.002 0.002
12 05 0005 12.1 11.3 10 7.20 10K 0.150 0.020 0.002 0.002
12 05 0012 9.1 11.9 10 7.10 10K 0.150 0.010K 0.002 0.002
12 05 0017 8.2 12.0 10 7.10 10K 0.160 0.020 0.002 0.002
72/08/09 18 10 0000 96 50K 6.80 10K 0.160 0.010K 0.006 0.002
18 10 0004 19.1 13.0 50K 6.80 10K 0.140 0.010K 0.003 0.003
18 10 0015 19.1 9.0 50K 6.80 10K 0.060 0.oioic 0.006 0.004
72/10/01 14 35 0000 216 50K 6.70 10K 0.150 0.080 0.010 0.009
14 35 0004 14.1 12.4 50K 6.70 10K 0.150 0.040 0.006 0.005
14 35 0015 14.0 9.2 50K 6.70 10K 0.140 0.050 0.007 0.007
32217
DATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAY FEET UG/L
72/06/05 12 05 0000
72/08/09 18 10 0000 2.OJ
72/10/01 14 35 0000 1.1J
-------
APPENDIX C
TRIBUTARY and WASTEWATER
TREATMENT PLANT DATA
K - Value is less than indicated
J - Value known to be in error
-------
STORET RETRIEVAL DATE 74/06/25
2309A1 LS2309A1
45 35 00.0 069 43 30.0
KENNEBECK RIVER E OUTLET
23 15 MOOSEHEAD Lt(
0/MOOSEHEAD LAKE
ST HWY 15 BRDG W OF MOOSEHEAD
1IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS—DIS P 1105—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET M6/L MG/L MG/I MG/L P MG/L P
72/09/16 13 30 0.217 0.265 0.265 0.005K 0.006
72/10/14 13 00 0.150 0.250 0.063 0.005K 0.005K
72/11/04 11 50 0.130 0.440 0.025 0.005K 0.006
72/12/10 11 15 0.130 0.210 0.005K 0.005K 0.005K
73/01/06 11 45 0.132 0.160 0.013 0.005K 0.005K
73/02/04 10 15 0.138 0.130 0.033 0.005K 0.005K
73 O4/07 11 30 0.150 1.000 0.016 0.010 0.010
73/04/21 08 30 0.147 1.000 0.034 0.006 0.006
73/05/05 0.147 0.210 0.020 0.005K 0.005K
73/05/19 13 00 0.147 0.400 0.075 0.005K 0.009
73/06/02 09 25 0.132 0.500 0.025 0.006 0.017
73/07/14 09 35 0.126 0.180 0.016 0.005K 0.005K
73/08/17 10 50 0.100 0.600 0.063 0.009 0.025
-------
STORET RETRIEVAL DATE 74/06/25
230906
45 35 18.0 069 42 42.0
MOOSEHEAD LAKE
23 MAINE
1 IEPAL ES 2111202
3 0015 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH T ALK N02&N03 NH3—N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 N—TOTAL TOTAL
TO DAY FEET CENT MG/I INCHES MICROMHO SU MG/L MG/L MG/I MG/I P MG/I P
72/06/05 15 40 0000 12.6 11.7 186 20 7.05 lOX 0.160 0.020 0.003 0.002
15 40 0013 30.6 12.1 20 7.00 lOX 0.170 0.020 0.006 0.003
72/08/09 17 30 0000 144 50K 6.90 10K 0.180 0.170 0.005 0.003
17 30 0004 18.1 11.0 50K 6.80 10K 0.160 0.020 0.003 0.003
17 30 0009 18.1 13.0 50K 6.70 10K 0.120 0.030 0.005 0.003
72/10/01 U 25 0000 168 50K 6.70 10K 0.140 0.060 0.008 0.008
11 25 0004 13.6 9.0 50K 6.70 10K 0.140 0.030 0.008 0.007
11 25 0010 13.4 9.2 50K 6.70 10K 0.140 0.040 0.008 0.008
32217
DATE TIME DEPTH CHIRPHYL
FROM OF A
TO DAY FEET UG/L
72/06/05 15 40 0000 1.2J
72/08/09 17 30 0000 1.2 )
72/10/01 11 25 0000 1. IJ
-------
STORET RETRIEVAL DATE 74/06/25
230907
45 35 36.0 069 41 06.0
MOOSEHEAD LAKE
23 MAINE
I1EPALES 2111202
3 0100 FEET DEPTH
00010 00300 00077 00094 00400 00410 00630 00610 00665 00666
DATE TIME DEPTH WATER DO TRANSP CNDUCIVY PH 1 ALK N026N03 NH3—N PHOS—TOT PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO) N—TOTAL TOTAL
TO DAY FEET CENT MG/L INCHES MICROMHO SU MG/L MG/L MG/L MG/L P MG/L P
72/06/05 15 55 0000 10.2 11.7 200 15 7.00 10K 0.150 0.020 0.003 0.003
15 55 0015 8.7 11.7 20 7.05 10K 0.170 0.010 0.003 0.002
IS 55 0020 8.9
15 55 0025 8.4
15 55 0030 7.9
15 55 0035 7.1
IS 55 0040 6.5
IS 55 0045 6.1
15 55 0050 5.8
15 55 0055 5.6
15 55 0060 5.4
15 55 0080 5.0
IS 55 0090 5.0
15 55 0100 4.9 20 7.00 10K 0.170 0.020 0.004 0.002
72/08/09 16 50 0000 132 50K 6.80 10K 0.170 0.130 0.005 0.003
16 50 0004 18.3 8.8 50K 6.80 10K 0.150 0.010K 0.003 0.002
16 50 0015 19.3 8.8 50K 6.80 10K 0.110 0.010K 0.004 0.003
16 50 0022 18.1 9.0 50K 6.60 10K 0.180 0.020 0.004 0.004
16 50 0030 16.9 8.8 50K 6.60 10K 0.180 0.010K 0.005 0.004
16 50 0040 14.2 8.2 50K 6.40 10K 0.120 0.010 0.005 0.004
16 50 0051 12.2 8.8 50K 6.30 10K 0.090 0.040 0.096 0.005
72/10/01 15 25 0000 14.0 264 50K 6.70 10K 0.150 0.050 0.009 0.008
IS 25 0004 14.0 9.2 50K 6.70 10K 0.150 0.040 0.010 0.006
15 25 0015 14.0 9.1 50K 6.80 10K 0.150 0.040 0.012 0.006
IS 25 0020 14.0 9.2 50K 6.70 10K 0.150 0.040 0.013 0.006
15 25 0027 14.0 9.0 50K 6.70 10K 0.150 0.040 0.011 0.007
IS 25 0033 14.0 9.2 50K 6.80 10K 0.150 0.040 0.013 0.008
15 25 0040 13.7 9.0 50K 6.80
15 25 0046 13.9 9.0 50K 6.80
IS 25 0053 14.1 9.2 50K 6.70
32217
OATE TIME DEPTH CHLRPHYL
FROM OF A
TO DAY FEET UG/L
72/06/05 IS 55 0000 1.OJ
72/08/09 16 50 0000 1.2J
7?/I0/01 IS 25 0000 1.3J
-------
STORET RETRIEVAL DATE 74/06/25
2309B1 LS230981
45 39 00.0 069 44 30.0
WEST OUTLET
23 15 MOOSEHEAD LK
0/MOOSEHEAD LAKE
ST HWY 15 BROG S OF ROCKWOOD
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME D [ PT’-$ N02&N03 TOT KJEL NH3—N PHOS-DIS PHOS—TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO DAY FEET MG/I MG/L MG/L MG/L P MG/I P
7?/09/1(, 13 50 0.130 0.150 0.033 0.006 0.010
72110/14 13 30 0.130 0.250 0.046 0.005K 0.006
7/11/04 11 45 0.130 0.320 0.032 0.005K 0.007
72/12/10 11 30 0.126 0.220 0.005K 0.005K 0.005K
73/01/06 12 00 0.138 0.610 0.029 0.005K 0.006
73/02/04 10 22 0.154 0.150 0.019 0.005K 0.005K
73/03/03 12 40 0.180 0.500 0.043 0.005K 0.005K
73/04/07 11 40 0.160 0.420 0.030 0.005K 0.00 5K
73/04/21 11 30 0.138 0.S3 5 0.044 0.005K 0.010
73/05/05 0.130 0.210 0.011 0.00 5K 0.005K
73/05/19 13 30 0.120 0.300 0.046 0.006 0.006
73/06/02 09 35 0.115 0.350 0.024 0.006 0.010
73/07/14 09 45 0.085 0.290 0.027 0.009 0.0 12
73/08/17 11 02 0.088 0.880 0.026 0.00 0.010
-------
STORET RETRIEVAL DATE 74/06/25
2309C1 LS2309C1
45 41 00.0 069 46 03.0
MOOSE RIVER
23 15 BRASSUA LX
1/MOOSEHEAD LAKE
BROG OFF ST HWY 15 W OF ROCKW000
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH NO2 NO3 TOT KJEL NH3-N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L P46/L MG/I MG/I P MG/L P
72/09/16 14 00 0.079 0.275 0.032 0.005K 0.009
72/10/14 13 35 0.078 0.200 0.054 0.005K 0.008
72/11/04 11 30 0.062 0.560 0.069 0.005K 0.016
72/12/10 11 45 0.056 0.400 0.021 0.005K 0.011
73/04/07 11 45 0.220 0.580 0.058 0.00 5K 0.010
73/04/21 08 00 0.189 0.460 0.028 0.005K 0.010
73/05/05 0.140 0.310 0.018 0.005K 0.010
73/05/19 13 40 0.110 0.370 0.027 0.006 0.0 10
73/06/02 09 40 0.089 0.390 0.016 0.006 0.010
73/07/14 09 55 0.058 0.260 0.024 0.005K 0.00 5K
73/08/17 11 15 0,040 1.050 0.032 0.005K 0.010
-------
STORET RETRIEVAL DATE 74/06/25
230901 L 52309D 1
45 44 30.0 069 50 00.0
TOMMEGAN SIRE M
23 15 BRASSUA LAKE
T/MOOSEHEAD LAKE
BROG W OF TOMMEGAN
11EPALES 2111204
0000 FEET DEPTH
00630
00625
00610
00671
DATE
TIME
DEPTt4
N02&N03
TOT KJEL
Nr43—N
PHOS—DIS
PHOS-TOT
FROM
OF
N-TOTAL
N
TOTAL
ORTHO
TO
DAY
FEET
P4G/L
MG/L
P4G/L
MG/L P
MG/L P
72/09/16
14 20
0.0R2
0.650
0.154
0.015
0.018
72/10/14
13 50
0.056
0.400
0.063
0.005K
0.014
72/11/04
11 00
0.087
0.440
0.039
0 .005K
0.016
73/03/03
1? 20
0.140
0.220
0.030
0.005K
0.005K
73/05/05
0.025
0.340
0.029
0.005K
0.010
73/06/0?
10 00
0.015
0.520
0.020
0.006
0.015
73/07/14
10 15
0.026
0.540
0.022
0.005K
0.020
-------
STORET RETRIEVAL DATE 74/06/25
2309E1 LS2309E1
45 40 30.0 069 27 00.0
ROACH RIVER—OUTLET 1ST ROACH PON
23 15 1ST ROACH PON
T/MOOSEHEAD LAKE
BRDG AT KOKAJDO
11EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/I MG/L P MG/L P
72/09/16 11 Os 0.047 0.625 0.031 0.005K 0.007
72/10/14 11 15 0.095 0.950 0.077 0.005K 0.006
72/11/04 14 00 0.072 0.320 0.029 0.005K 0.007
72/12/10 10 15 0.072 0.150 0.009 0.005K 0.006
73/01/06 10 15 0.090 1.260 0.079 0.005K 0.005K
73/02/04 09 15 0.086 0.140 0.012 0.007 0.007
73/03/03 11 00 0.098 0.250 0.031 0.005K 0.005K
73/04/07 10 10 0.092 0.500 0.015 0.005K 0.005K
73/04/21 10 15 0.088 0.260 0.012 0.005K 0.005K
73/05/05 10 00 0.084 0.180 0.026 0.005K 0.005K
73/05/19 15 00 0.081 0.120 0.010 0.015
73/06/02 11 50 0.072 0.130 0.005K 0.005K 0.015
73/07/14 12 00 0.035 0.140 0.031 0.005K 0.005K
73/08/17 11 40 0.015 0.150 0.017 0.020 0.020
-------
STORET RETRIEVAL DATE 74/06/25
2309F1 LS2309F1
45 36 00.0 069 30 30.0
LILY BAY BROO’(
23 15 MOOSEHEAD LK
T/MOOSEHEAO LAKE
BPDG W SIDE OF LILY BAY
1 1EPALES
4
2111204
0000 FEET DEPTH
00630
00625
00610
00671
00665
DATE
TIME
DEPTH
N02F Pi03
TOT KJEL
N 43-N
PHOS—DIS
PHOS—TOT
FROM
OF
N-TOTAL
N
TOTAL
ORTHO
TO
DAY
FFET
MG/L
MG/L
MG/L
MG/L P
MG/L P
72/09/16
10 40
0.185
0.400
0.046
0.008
0.009
72/10/14
11 00
0.117
0.750
0.075
0.005K
0.OOS
72/11/04
15 50
0.120
0.330
0.026
0.005K
0.010
73/04/07
10 00
0.120
1.600
O.04R
0.005K
0.010
73/04/21
10 00
0.067
0.330
0.012
0.005K
0.010
73/05/05
08 40
0.130
0.160
0.OLQ
0.005K
0.010
73/05/19
0.072
0.460
0.021
0.007
0.015
73/06/02
11 40
0.087
0.400
0.120
0.008
0.020
73/07/14
11 45
0.126
0.200
0.016
0.00 5K
0.010
73/08/17
11 50
0.084
0.600
0.027
0.006
0.020
-------
STORET RETRIEVAL. DATE 74/06/25
2309G1 LS2309G1
45 34 30.0 069 32 00.0
MUO BROOK
23 15 MOOSEHEAD LK
T/MOOSEHEAD LAKE
BRDG SE CORNER OF MATHEWS COVE
1 IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P NG/L P
72/09/16 10 30 0.075 0.800 0.115 0.019 0.022
72/10/14 10 40 0.042 0.800 0.086 0.005K 0.015
72/11/04 13 50 0.056 0.780 0.110 0.005K 0.016
72/12/10 10 00 0.063 0.740 0.180 0.005K 0.010
73/04/07 09 50 0.044 0.410 0.023 0.005K 0.005K
73/04/21 12 00 0.025 1.000 0.044 0.006 0.010
73/05/05 08 30 0.014 0.330 0.056 0.005K 0.010
73/05/19 14 40 0.011 0.110 0.009 0.015
73/06/02 11 30 0.012 0.460 0.040 0.006 0.015
73/07/14 11 35 0.024 0.800 0.033 0.005K 0.015
73/08/17 12 05 0.010K 1.540 0.024 0.005K 0.020
-------
STORET RETRIEVAL DATE 14/06/25
2309’l l LS2309 1-41
45 32 00.0 069 33 00.0
BEAVER POND-OUTLET OF PRONG POND
23 15 MOOSEHEAD LK
T/MOOSEHEAO LAKE
B DG SE END OF BEAVER COVE
1 IEPALES 2)11204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH NO2 NO3 TOT KJEL NH3—N PHOS—DIS PHOS-TOT
FROM OF N—TOTAL N TOTAL OPTHO
TO DAY FEET MG/I MG/L MG/I MG/L P MG/L P
72/09/16 1? 20 0.032 0.425 0.063 0.005K 0.01’.
72/10/14 10 24 0.032 0.350 0.054 0.005K 0.010
72/11/04 13 30 0.022 0.460 0.040 0.005K 0.012
7?/12/10 09 50 0.029 0.370 0.005K 0.005K 0.008
73/01/06 09 30 0.052 0.380 0.005K 0.010
73/02/04 08 55 0.088 0.360 0.034 0.007 0.007
73/03/03 10 20 0.100 0.390 0.038 0.005K 0.005K
73/04/07 09 45 0.110 1.320 0.063 0.005K 0.015
73/04/21 09 00 0.100 0.750 0.024 0.005K 0.010
73/05/05 08 20 0.037 0.220 0.007 0.005K 0.010
73/05/19 14 10 0.018 0.060 0.007 0.010
73/06/02 ii 15 0.010K 0.410 0.050 0.006 0.015
73/07/1’ 11 25 0.010K 0.440 0.025 0.007 0.010
73/08/17 1? 05 0.010K 0.300 0.014 0.005K 0.010
-------
STORET RETRIEVAL DATE 74/06/25
2309J1 LS2309J1
45 27 30.0 069 37 30.0
NO NAME
23 15 GREENVILLE
T/MOOSEHEAD LAKE
ST HWY 15 BRDG IN GREENVILLE JCT
1 IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEI NH3-N PHOS—DIS PHOS—TOT
FROM OF N-TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P
72/09/16 12 50 0.088 0.650 0.086 0.009 0.021
72/10/14 12 40 0.039 1.050 0.063 0.005K 0.013
72/11/04 12 15 0.040 0.420 0.038 0.005K 0.009
73/04/07 10 45 0.063 0.920 0.026 0.005K 0.015
73/04/21 08 10 0.025 0.960 0.025 0.005K 0.010
73/05/05 10 30 0.027 0.220 0.011 0.005K 0.010
73/05/19 12 45 0.024 0.420 0.008 0.007 0.015
73/06/02 09 05 0.016 0.390 0.023 0.006 0.020
73/07/14 09 15 0.048 0.640 0.044 0.005K 0.015
73/08/17 10 15 0.033 0.132 0.032
-------
STORET RETRIEVAL D4TE 74/06/25
2309K1 LS2309K1
49 29 30.0 069 40 00.0
SQUAW BROOK
23 15 GREFNVILLE
T/MOOSEHEAD
ST HWY 15 BROG NW OF GREENVILLE JCT
1 IEPALES 2111204
4 0000 FEET DEPTH
00630 00625 006)0 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO DAY FFET MG/L MG/L Mr,/L MG/L P MG/L P
72/09/16 13 05 0.117 0.400 0.042 0.005K 0.006
72/10/14 1 45 0.039 0.200 0.048 0.005K 0.005K
72/11/04 12 10 0.059 0.310 0.035 0.005K 0.007
73/04/21 11 45 0.076 0.480 0.012 0.005K 0.010
73/05/OS 0.090 0.150 0.011 0.005K 0.005 1 <
73/05/19 13 00 0.061 0.12R 0.010 0.015
73/06/02 09 15 0.071 0.220 0.060 0.006 0.010
73/07/14 11 00 0.060 0.150 0.026 0.005K 0.005K
73/08/17 10 25 0.048 0.130 0.021 0.007 0.010
-------
STORET RETRIEVAL DATE 74/06/25
2309L1 LS2309L1
45 30 30.0 069 40 30.0
UPPER SQUAW BROOK
23 15 MOOSEHEAD LK
T/MOOSEHEAD LK
ST HWY 15 SE OF MT VIEW POND
1 1EPALES 2111204
4 0000 FEET DEPTH
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3-N PHOS—DIS PHOS—TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO DAY FEET HG/L MG/L HG/I MG/L P MG/L P
72/09/1f 13 20 0.094 0.450 0.110 0.008 0.016
72/11/04 12 10 0.032 0.440 0.058 0.005K 0.014
72/12/10 11 00 0.013 0.420 0.007 0.005K 0.006
73/04/07 11 20 0.096 0.440 0.069 0.005K 0.005K
73/04/21 08 30 0.069 1.100 0.054 0.005K 0.010
73/05/05 0.062 0.195 0.015 0.005K 0.010
73/05/19 13 15 0.010K 0.310 0.005K 0.005K 0.010
73/06/02 09 20 0.010K 0.140 0.019 0.006 0.015
73/07/14 09 25 0.010K 0.320 0.011 0.005K 0.010
73/08/17 10 23 0.010K 0.370 0.006 0.005K 0.015
------- |