U.S. ENVIRONMENTAL PROTECTION AGENCY
               NATIONAL EUTROPHICATION  SURVEY
                        WORKING PAPER SERIES
                                          REPORT
                                            ON
                                        FWTON LAKES
                                       PASSAIC COUNT/
                                         NEW JERSEY
                                        EPA REGION II
                                      WORKING PAPER No, 373
     CORVALLIS ENVIRONMENTAL RESEARCH LABORATORY - CORVALLIS, OREGON
                                 and
    ENVIRONMENTAL MONITORING & SUPPORT LABORATORY - LAS VEGAS, NEVADA
liTG.P.O. 699-440

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                                           REPORT
                                             ON
                                        POMPTON LAKES
                                       PASSAIC COUNTY
                                         NEW JERSEY
                                        EPA REGION II
                                     WORKING PAPER No,  373
          WITH THE COOPERATION OF THE
NEW JERSEY DEPARTMENT OF ENVIRONMENTAL PROTECTION
                     AND THE
            NEW JERSEY NATIONAL GUARD
                     MAY 1976

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CONTENTS
Page
Foreword ii
List of Study Lakes — State of New Jersey IV
Lake and Drainage Area Maps V, Vi
Sections
I. Conclusions 1
II. Lake and Drainage Basin Characteristics 4
III . Lake Water Quality Summary 6
IV. Nutrient Loadings 11
V. Literature Reviewed 17
VI. Appendices 18

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Ii
FOREWORD
The National Eutrophication Survey was Initiated in 1972 in
response to an Administration coiiuiiitment to investigate the nation-
wide threat of accelerated eutrophication to freshwater lakes and
reservoi rs.
OBJECTIVES
The Survey was designed to develop, in conjunction with state
environmental agencies, information on nutrient sources, concen-
trations, 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 nonpoint source pollution abatement in lake water-
sheds.
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
watershed 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 [ g303(e)], water quality criteria/standards review
[ 3O3(c)3, clean lakes [ 3l4(a,b)], and water quality monitoring
[ lO6 and §305(b)] activities mandated by the Federal Water
Pollution Control Act Amendments of 1972.

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iii
Beyond the single lake analysis, broader based correlations
between nutrient concentrations (and loading) and trophic condition
are being made to advance the rationale and data base for refine-
ment of nutrient water quality criteria for the Nation’s freshwater
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 the U.S. Environmental Protection
Agency and to augment plans implementation by the states.
ACKNOWLEDGMENTS
The staff of the National Eutrophication Survey (Office of
Research and Development, U.S. Environmental Protection Agency)
expresses sincere appreciation to the New Jersey Department of
Environmental Protection for professional involvement and to the
New Jersey National Guard for conducting the tributary sampling
phase of the Survey.
Douglas Clark, Chief of the Bureau of Water Quality Planning
and Management, Mr. Frank Takacs, New Jersey National Eutrophication
Survey Coordinator, Principal Environmental Specialist, and
Robert Kotch, Senior Environmental Engineer, 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 William R. Sharp, Former Chief of Staff, Major
General Wilfred G. Menard, Jr., Chief of Staff, and Project Officer
Colonel Herbert 0. Ruhlin, who directed the volunteer efforts of
the New Jersey National Guardsmen, are also gratefully acknowledged
for their assistance to the Survey.

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iv
NATIONAL EUTROPHICATION SURVEY
STUDY LAKES
STATE OF NEW JERSEY
LAKE NAME COUNTY
Budd Lake Morris
Duhernal Lake Middlesex
Farrington Lake Middlesex
Greenwood Lake Passaic, N.J.;
Orange, N.Y.
Lake Hopatcong Morris, Sussex
Lake Musconetcong Morris, Sussex
Oradell Reservoir Bergen
Paulinskill Lake Sussex
Pinecliff Lake Passaic
Pompton Lakes Passaic
Spruce Run Reservoir Hunterdon
Union Lake Cumberland
Wanaque Reservoir Passaic

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POMPTON
LAKES
\
Hoppers
Lake
Tributary Sampling Site’
Lake Sampling Site
Sewage Treatment Facility
I 12 Km
2Mi.
New Jersey
Location
Point

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vi
New Jersey
New York
Location
LAKES
Tributary Sampling Site
Lake Sampling Site
Sewage Treatment Facility
Drainage Area Boundary
Central
“ Valley
POM PTON

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POMPTON LAKES, NEW JERSEY
STORET NO. 3410
I. CONCLUSIONS
A. Trophic Condition:
Based on Survey data and field observations, Pompton
Lakes is considered eutrophic. The lake is characterized
by high concentrations of total phosphorus, low Secchi
disc transparency and high potential for primary pro-
duction as measured by algal assay control yield. Survey
limnologists reported abundant aquatic macrophytes.
Chlorophyll a values ranged from a low in the spring of
5.4 pg/l to a high of 58.9 pg/i in the fall.
The lake has a record of occasional herbicide appli-
cations in the past. Ketelle and Uttormark (1971) recom-
mended partial dredging and the removal of nutrient sources
for the rehabilitation of Pompton Lakes.
B. Rate-Limiting Nutrient:
Algal assay results indicate that Pompton Lakes is
limited by available phosphorus. Spikes with phosphorus,
or phosphorus and nitrogen simultaneously resulted in
increased assay yields.

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2
The ratio of mean total available inorganic nitrogen
to mean orthophosphorus (N/P) further substantiates these
results.
C. Nutrient Controllability:
1. Point Sources -
The mean annual phosphorus contribution from
known point sources was estimated to be 28.5% of the
total load reaching Pompton Lakes during the sampling
year. However, the mean annual nutrient exports for
the Ramapo River (Section 0, page 16) were substantially
higher than what would be expected for this area. It
is likely that point sources above the lake in New York
significantly contribute to the phosphorus loading of
Pompton Lakes (page 14).
The present loading of 47.89 g P/m 2 /yr is about
13 times greater than the loading proposed by Vollen-
weider (Vollenweider and Dillon, 1974) as “dangerous”
(eutrophic). It should be noted that the applicability
of Vollenweider’s model is doubtful for lakes with such
short hydraulic retention times. Nevertheless, the above
loading is excessive and reduction of non-point phosphorus
loading as well as all point sources would be required to
substantially improve the water quality of Pompton Lakes.

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3
2. Nonpoint Sources —
The mean annual phosphorus load from nonpoint
sources was estimated to be 71.5% of the total load
reaching Pompton Lakes. Measured tributaries
accounted for 71.2%, and ungaged tributaries
accounted for 0.3%. The Ramapo River was estimated
to contribute 70.5% of this measured load; however,
as discussed, this high background loading is
probably due to the contributions of unmeasured
point sources upstream.

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4
II. LAKE AND DRAINAGE BASIN CHARACTERISTICS
Lake and drainage basin characteristics are itemized
below. Lake surface area and mean depth were provided by
the State of New Jersey; tributary flow data were provided
by the New Jersey District Office of the U.S. Geological
Survey (USGS). Outlet drainage area includes the lake
surface area. Mean hydraulic retention time was obtained
by dividing the lake volume by the mean flow of the outlet.
Precipitation values are estimated by methods as outlined in
National Eutrophication Survey (NES) Working Paper No. 175.
A table of metric/English conversions is included as
Appendix A.
A. Lake Morphometry:
1. Surface area: 0.83 km 2 .
2. Mean depth: 1.8 meters.
3. Maximum depth: 5.8 meters.
4. Volume: 1.494 x 106 m 3 .
5. Mean hydraulic retention time: 2.0 days.

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5
B. Tributary and Outlet (see Appendix B for flow data):
1. Tributaries -
Drainage Mean flow
Name area(km 2 ) ( m 3 /sec )
A(2) Ramapo River 388.5 7.96
B(l) Unnamed Stream 10.8 0.14
C(l) Unnamed Stream 4.6 0.05
Minor tributaries and
immediate drainage - 9.6 0.13
Totals 413.5 8.28
2. Outlet - A(l) Ramapo River 414.4 7.83
C. Precipitation:
1. Year of sampling: 122.9 cm.
2. Mean annual: 156.4 cm.

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6
III. LAKE WATER QUALITY SUMMARY
Pompton Lakes 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 two stations on the lake and
from a number of depths at each station (see maps, pages v
and vi). During each visit, depth-integrated samples were
collected from each station for chlorophyll a analysis and
phytoplankton identification and enumeration. During the
first visit, an 18.9-liter depth-integrated sample was coni-
posited for algal assays. Maximum depths sampled were
3.7 meters at Station 1 and 1.5 meters at Station 2. For a
more detailed explanation of NES methods, see NES Working
Paper No. 175.
The results obtained are presented in full in Appendix C
and are summarized in III A for waters at the surface and
at the maximum depth for each site. Results of the phyto-
plankton counts and chlorophyll a determinations are included
in III B. Results of the limiting nutrient study are
presented in III C.

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o N NO. OF SAMPLES
MAXIMUM DEPTH SAMPLED AT EACH SITE
S NO. OF SITES SAMPLED ON THIS DATE
POMPTON LAKES
STORET CODE 3410
PHYSICAL AND CHEMICAL CHARACTERISTICS
PARAMETER N°
I 4/17/73 I
2
RANGE MEDIAN
MAX
DEPTH
RANGE
(METERS)
N•
( 7/22/73 )
5 °° = 2
RANGE MEDIAN
MAX
DEPTH
RANGE
(METERS)
N°
I 10/ 2/73 I
S••° = 2
RANGE MEDIAN
MAX
DEPTH
RANGE
(METERS)
TEMPERATURE (DEG CENT)
0.—I.S H DEPTH 4
MAX DEPTH°• 2
12.6— 12.8 12.7
12.5— 12.6 12.5
0.0— 1.2
0.9— 3.4
4
2
21.0— 22.1 21.7
21.0— 21.3 21.1
0.0— 1.5
1.5— 3.7
3
2
18.3— 18.8 18.6
17.9— 18.6 18.2
0.0— 1.5
0.0— 2.7
DISSOLVED OXYGEN (MC,/L)
0.-I.5 N DEPTH 2
MAX DEPTH°° 2
10.0— 11.1 10.5
10.0— 11.0 10.5
0.9- 1.2
0.9— 3.4
2
2
,.8— 7.2 6.5
3.2— 7.2 5.2
1.5— 1.S
1.5— 3.7
2
2
13.2— 14.’. 13.8
10.0— 13.2 11.6
0.0— 1.5
0.0— 2.7
CONDUCTIVITY (UMHOS)
0.—I.S M DEPTH 4
MAX DEPTH°° 2
180.— 190. 190.
190.— 198. 194.
0.0— 1.2
0.9— 3.4
4
2
178.— 182. 179.
178.— 198. 188.
0.0— 1.5
1.5— 3.7
3
2
580.— 625. 600.
600.— 625. 613.
0.0— 1.5
0.0— 2.7
PH (STANDARD UNITS)
0.—I.5 H DEPTH 4
MAX DEPTH°• 2
7.1— 7.4 7.2
7.3— 7.4 7.3
0.0— 1.2
0.9— 3.4
4
2
7.0— 7.2 7.1
7.0— 7.2 7.1
0.0— 1.5
1.5— 3.7
3
2
8.8— 9.2 8.9
8.2— 8.8 8.5
0.0— 1.5
0.0— 2.7
TOTAL ALKALINITY (MG/LI
0.—I.5 N DEPTH 4
MAX DEPTH•e 2
34.— 37. 37.
36.— 37. 37.
0.0— 1.2
0.9— 3.4
4
2
48.— 49. 49.
48.— 58. 53.
0.0— 1.5
1.5— 3.7
3
2
69.— 76. 71.
76.— 77. 77.
0.0— 1.5
0.0— 2.7
TOTAL P (MG/I)
0.—1.5 N DEPTH 4
MAX DEPTH°U 2
0.054—0.060 0.056
0.040—0.061, 0.050
0.0— 1.2
0.9— 3.4
4
2
0.101—0.135 0.112
0.135—0.142 0.138
0.0— 1.5
1.5— 3.7
3
2
0.058—0.101 0.070
0.073—0.101 0.087
0.0— 1.5
0.0— 2.7
DISSOLVED ORTHO P (MG/I)
0.—1.5 H DEPTH 4
MAX DEPTH°• 2
0.027—0.038 0.032
0.01 9 —0.03b 0.027
0.0— 1.2
0.9— 3.4
4
2
0.032—0.040 0.038
0.029—0.038 0.033
0.0— 1.5
1.5— 3.7
3
2
0.006—0.015 0.008
0.006—0.01 0.010
0.0— 1.5
0.0— 2.7
N02 .N03 (MG/LI
0.-I.5 H DEPTH 4
MAX DEPTH•° 2
0.460—0.500 0.495
0.490—0.Soo 0.495
0.0— 1.2
0.9— 3,4
4
2
0.670—0.630 0.670
0.510—0.670 0.590
0.0— 1.5
1.5— 3.7
3
2
0.700—0.900 0.720
0.790—0.900 0.645
0.0— 1.5
0.0— 2.7
AMMONIA (HG/LI
0.-I.5 N DEPTH 4
MAX DEPTH°• 2
0.ObO—0.090 0.070
0.060—0.070 0.065
0.0— 1.2
0.9- 3.4
4
2
0.160—0.220 0.200
0.160—0.470 0.3)5
0.0— 1.5
1.5— 3.7
3
2
0.040—0,040 0.040
0.040—0.240 0.140
0.0— 1.5
0.0— 2.7
KJELOAHL N (MG/LI
0.—I.5 N DEPTH 4
MAX DEPTH°° 2
0.300—0.400 0.400
0.300—0.400 0.350
0.0— 1.2
0.9— 3.4
4
2
0.600—0.900 0.700
0.700—0.900 0.800
0.0— 1.5
1.5— 3.7
3
2
0.300—0.600 0.300
0.600—0.600 0.600
0.0— 1.5
0.0— 2.7
SECCPII DISC (METERS)
2
1.1— 1.5 1.3

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8
B. Biological Characteristics:
1. Phytoplankton
Algal
Sampling Dominant Units
Date Genera per ml
04/17/73 1. Navicula 1,577
2. Melosira 681
3. Stephanodiscus 430
4. Asterionella 203
5. Flagellates 167
Other genera 347
Total 3,405
07/22/73 1. Melosira 829
2. Aphanizomenon 609
3. Navicula 463
4. Flagellates 317
5. Fragilaria 171
Other genera 389
Total 2,778
10/02/73 1. Flagellates 14,505
2. Melosira 6,484
3. Cyclotella 1,003
4. Stephanodiscus 535
5. Coelastrum 267
Other genera 468
Total 23,262

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9
Station
Number
1
2
1
2
1
2
Maximum yield
( mg/l-dry wt. )
8.5
11.8
24.1
9.7
2. Chlorophyll a -
Sampling
Date
04/1 7/73
07/22/73
10/02/73
Chlorophyll a
(ijg/i)
5.4
12.1
9.2
9.5
58.9
43.1
C. Limiting Nutrient Study:
1. Autoclaved, filtered, and nutrient spiked -
Ortho P Inorganic N
Spike (mg/i ) Conc.(mg/l) Conc.(mg/1)
Control 0.020 0.325
0.05 P 0.070 0.325
0.05 P + 1.0 N 0.070 1.325
1.00 N 0.020 1.325
2. Discussion -
The control yield of the assay alga, Selenastrum
capricornutum , indicates that the potential for primary
productivity was high in Pompton Lakes at the time of
sampling. The lake was phosphorus limited at that time
as indicated by the increased yield of the assay alga in
response to an addition of orthophosphorus. Spikes with
phosphorus and nitrogen simultaneously resulted in a
maximum yield.

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10
The N/P ratio of 18/1 in the spring lake chemical data further
indicates phosphorus limitation. At all other sampling times the
N/P ratio was 25/1 or greater, and phosphorus limitation also would
be expected.

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11
IV. NUTRIENT LOADINGS
(See Appendix 0 for data)
For the determination of nutrient loadings, the New
Jersey National Guard collected monthly near-surface grab
samples from each of the tributary sites indicated on the
maps (pages v and vi), except for the high runoff month
of March when two samples were collected. Sampling was
begun in July 1973, and was completed in June 1974.
Through an interagency agreement, stream flow estimates
for the year of sampling and a “normalized” or average year
were provided by the New Jersey District Office of the USGS
for the tributary sites nearest the lake.
In this report, nutrient loads for sampled tributaries
were determined by using a modification of the USGS computer
program for calculating stream loadings. Nutrient loads
indicated for tributaries are those measured minus known
point source loads, if any.
Nutrient loadings for unsampled “minor tributaries and
in’uiiediate drainage” (“ZZ” of USGS) were estimated by using
the mean annual concentrationsin Unnamed Stream at
Station B(1) and mean annual ZZ flow.

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12
The operators of the Ramapo College, Prime Equities,
Blue Hills, Regency Park Apts., Skyview, Oakwood Knolls,
Pompton Lakes Nursing-Convalescent, Holiday Inn (Fairlawn),
Manito School (Oakland), Indian Hills High School, Swiss
Chalet, Apex Co., Okonite Co., Nu-Car Carriers Inc.,
Hamiltonian Fidelity, Society Hills, U.S. Army Housing
Area, Chan’s Hawaiian Restaurant, and TriCorner Realty
wastewater treatment plants provided monthly effluent
samples and corresponding flow data. Nutrient loads for
the city of Suffern wastewater treatment plant were estimated
at 1.134 kg P and 3.401 kg N/capita/year.
Eleven other New York point sources exist which are
known to impact the Ramapo River Basin area. These include
Queen of Apostle College, Intercoast Development, Zukerman’s
Apartments, and Highland Telephone Co., all in the city of
Monroe; Motel on the Mountain in Hilburn; the Ramapo-Sloatsburg
plant in Sloatsburg; Tuxedo Village, Tuxedo Mt. View Apart-
ments, and Tuxedo Park Sewage Treatment Plant, all in Tuxedo;
the Indian Hill Plant and New York University Apartments,
both at Sterling Forest Lake. These sources did not partici-
pate in the Survey so are not included in the nutrient budget
on pages 14-15. It is expected, however, that the unusually
high background loading for the Ramapo River is due, at least
in part, to unmeasured contributions from these sources.

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‘3
A Waste Sources -
Known municipal -
Population Me n Flow Receiving
Name Served* Treatment ( m Id x iO ) Water
Ramapo College 3,500 Activated sludge 0 181 Ramapo River
(Wayne)
Prime Equities 1,225 Activated sludge 0 057 Ramapo River
(Mahwah)
Blue Hills 105 Activated sludge 0 067 Ramapo River
(Mahwah)
Regency Park 363 Activated sludge 0 070 Ramapo River
Apts (Mahwah) /
Skyview (Oakland) 300 Activated sludge 0 082 Ramapo River
Oakwood Knolls 240 Activated sludge 0 392 Ramapo River
(Oakland)
Pompton Lakes 70 Sand filter 0 016 Ramapo River
Nursi ng-Convalescent
Holiday Inn 200 Activated sludge 0 048 Ramapo River
(Fairlawn)
Manito School 108 Activated sludge 0 016 Ramapo River
(Oakland)
Indian Hills High 1,100 Activated sludge 0 053 Ramapo River
School (Wycuoff)
Swiss Chalet 65 Trickling filter 0 023 Ramapo River
(Ramsey)
Apex Corporation 83 Sand filter 0 034 Ramapo River
(Mahwah)
Okonite Company 149 Activated sludge 0 011 Ramapo River
(Ramsey)
Nu-Car Carriers Inc 8 Activated sludge 0 006 Ramapo River
Hamiltonian Fidelity 500 Activated sludge 0 110 Masoniuro Brook!
(Mahwah) Ramapo
Society Hills 56 Activated sludge 0 021 Oarlington Brook !
(Mahwah) Ramapo River
U S Army Housing 150 Trickling filter 0 105 Ramapo River
Area
Chans Hawaiien 900 to 1,000 Activated sludge 0 037 Ramapo River
Restaurant
TriCorner Realt ) 9-store Sand filter 0 003 Ramapo River
compl ex**
Suffern Sewage 8,273 Trickling filter 1 131 Ramapo River
Treatment Plant***
Treatment plant questionnaire information
**Small 5tores, each operated by owner
***US [ PA, 1971 Population shown is 1970 census, flow estimate is based on 0 3785 m 3 !capi ta/day

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14
B Annual Total Phosphorus Loading - Average Year
Inputs -
of
Source kg P/yr total
a Tributaries (nonpoint load) -
A(2) Rarnapo River 28,000 70 5
B(l) Unnamed Stream 140 0 4
C(l) Unnamed Stream 135 0 3
b Minor tributaries and irmiediate 135 0 3
drainage (nonpoint load) -
c Known municipal STPs -
Ramapo College 130 0 3
Prime Equities 65 0 2
Blue Hills 115 0 3
Regency Park Apts 90 0 2
Skyview 180 0 5
Oakewood Knolls 550 1 4
Pompton Lakes Nursing-Convalescent 20 0 1
Holiday Inn 175 0 4
Manito School 10 <0 1
Indian Hills High School 115 0 3
Swiss Chalet 130 0 3
Apex Corporation 70 0 2
Okonite Company 5 <0 1
Nu-Car Carriers Inc 5 <0 1
Hamiltonian Fidelity 150 0 4
Society Hills 50 0 1
Suffern 9,380 23 6
U S Army Housing Area 50 0 1
Chans Hawaiian Restaurant 20 0 1
TriCorner Realty 5 <0 1
d Septic tanks* — 5 <0 1
e Known industrial — none
f Direct precipitat,on** - 15 <01
Totals 39,745 100 0
2. Output - A(1) Ramapo River 16,100
3 Met annual P accumulation 23,645
*Estlmate based on 22 lakeside residences
**Estimated (see NES Working Paper No 175)

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15
C. Annual Total Nitrogen Loading - Average Year
Inputs -
S of
Source kg N/yr total
a. Tributaries (nonpoint load) -
A(2) Ramapo River 431 .620 89 4
B(l) Unnamed Stream 5,380 1.1
C(l) Unnamed Stream 4,040 0.8
b Minor tributaries and ime’diate 5,255 1.1
drainage (nonpoint load) -
c Known municipal SIPs -
Ramapo College 990 0 2
Prime Equities 355 0.1
Blue Hills 275 0 1
Regency Park Apts. 410 0 1
Skyview 330 0.1
Oakwood Knolls 2,335 0.5
Pompton Lakes Nursing-Convalescent 105 <0.1
Holiday Inn 220 0 1
Manito School 55 <0.1
Indian Hills High School 575 0 1
Swiss Chalet 150 <0.1
Apex Corporation 185 <0 1
Okonite Company 55 <0.1
Nu-Car Carriers Inc 30 <0 1
Hamiltonian Fidelity 880 0 2
Society Hills 170 <0 1
Suffern 28,135 5 8
U S Army Housing Area 190 <0 1
Chans Hawaiian Restaurant 75 <0 1
TriCorner Realty 40 <0 1
d. Septic tanks* - 235 0 1
e Known industrial - none
f Direct preclpltatlon** - 895 0 2
Totals 482,985 100 0
2 Output - A(l) Ramapo River 327,150
3 Net annual N accumulation - 155,835
*Estimate based on 22 lakeside residences
**Estimated (see NES Working Paper No 175)

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16
D. Mean Annual Non-point Nutrient Export by Subdrainage Area:
Tributary kg P/km 2 /yr kg NJkm 2 /yr
A 2) Ramapo River* 72 1,110
B 1) Unnamed Stream 13 498
C(l) Unnamed Stream 29 878
E. Yearly Loads:
In the following table, the existing phosphorus loadings
are compared to those proposed by Vollenweider (Vollenweider
and Dillon, 1974). Essentially, his “dangerous” loading is
one at which the receiving water would become eutrophic or
remain eutrophic; his “permissible” loading is that which
would result in the receiving water remaining oligotrophic
or becoming oligotrophic if morphometry permitted. A rneso-
trophic loading 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 Yearly
Phosphorus Loading
(g/m 2 /yr)
Estimated loading for Pompton Lakes 47.89
Vollenweider’s “dangerous” or eutrophic loading 3.60
Vollenweider’s “permissible” or oligotrophic loading 1.80
* The background levels for the stream are probably inflated by unsampled
point sources upstream (see page 12).

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17
V. LITERATURE REVIEWED
Ketelle, J. M. and P. D. Uttormark. 1971. Problem Lakes
in the United States. U.S. Environmental Protection
Agency Project #16010 EHR. University of Wisconsin,
Madison, Wisconsin.
U.S. Environmental Protection Agency. 1971. Inventory of
Wastewater Treatment Facilities. Office of Media Pro-
grams, Office of Water Programs, Washington, D.C.
________ 1975. National Eutrophication Survey Methods
1973-1976. Working Paper No. 175. Environmental Monitoring
and Support Laboratory, Las Vegas, Nevada and Corvallis
Environmental Research Laboratory, Corvallis, Oregon.
Vollenweider, R. A., and P. J. Dillon, 1974. The application of
the phosphorus loading concept to eutrophication research.
Natl. Res. Council of Canada Pubi. No. 13690, Canada Centre
for Inland Waters, Burlington, Ontario.

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VI. APPENDICES
APPENDIX A
CONVERSION FACTORS

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CONVERSION FA(;TORS
Hectares x 2.471 = acres
Kilometers x 0.6214 = miles
Meters x 3.281 = feet
Cubic meters x 8.107 x lO = 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 = lbs/square mile

-------
APPENDIX B
TRIBUTARY FLOW DATA

-------
TRIBUTARY FLOW INFORMATION FOR NEW JERSEY 06/04/76
LAKE CODE 3410 POMPTON LAKE
TOTAL DRAINAGE AREA OF LAKE (SO KM) 414.4
SUB—DRAINAGE NORMALIZED FLOIS(CMS)
TRIBUTARY AREA(SO KM) JAN FEB MAR APP MAY JUN JUL AUG SEP OCT NOV DEC MEAN
3410A 1 414.4 8.81 9.60 15.80 14.16 8.95 5.13 3.74 4.19 4.13 4.05 7.14 8.38 7.83
3410A2 388.5 9.29 9.54 16.06 14.19 8.27 4.90 3.51 4.02 4.05 5.35 7.42 9.09 7.96
341081 10.8 0.167 0.170 0.258 0.212 0.147 0.088 0.068 0.074 0.071 0.085 0.147 0.170 0.138
3410C1 4.6 0.057 0.057 0.099 0.079 0.048 0.025 0.018 0.019 0.018 0.024 0.048 0.057 0.046
3410ZZ 10.4 0.161 0.164 0.249 0.207 0.142 0.085 0.065 0.071 0.068 0.082 0.142 0.164 0.133
SUMMARY
TOTAL DRAINAGE AREA OF LAKE = 414e4 TOTAL FLOW IN 99•49
SUM OF SUB—DRAINAGE AREAS — 414.3 TOTAL FLOW OUT 94.07
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
3410A1 7 73 9.628 21 15.036
8 73 2.381 26 1.246
9 73 1.631 29 1.104
10 73 1.999
11 73 2.237 4 2.718
12 73 23.758 8 2.520
1 74 13.309 26 17.103
2 74 9.656 23 19.227
3 74 12.714 9 10.534 23 21.917
4 74 18.944 21 13.875
5 74 9.316 12 12.629
6 74 5.239 22 6.428
3410A2 7 73 7.872 21 11.129
8 73 1.668 26 0.850
9 73 1.249 29 0.821
10 73 1.923
11 73 2.005 4 2.294
12 73 25.995 8 4.814
1 74 13.026 26 16.509
2 74 9.599 23 19.255
3 74 12.997 9 11.044 23 20.756
4 74 17.868 21 11.950
5 74 8.523 12 12.488
6 74 5.295 22 5.267

-------
TRIBUTARY FLOW iNFORMATION FOR NEW JERSEY 06/04/76
LAKE CODE 3410 POMPTON LAKE
MEAN MONTHLY FLOWS AND DAILY FLOWS(CMS)
TRIBUTARY MONTH YEAR MEAN FLOW DAY FLOW DAY FLOW DAY FLOW
3410B1 7 73 0.113 21 0.127
8 73 0.034 26 0.020
9 73 0.020 29 0.020
10 73 0.045
11 73 0.045 4 0.045
12 73 0.283 8 0.096
1 74 0.170 26 0.232
2 74 0.156 23 0.340
3 74 0.224 9 0.184 23 0.311
4 74 0.261 21 0.184
5 74 0.167 12 0.263
6 74 0.082 22 0.079
3410C1 7 73 0.345 21 0.396
8 73 0.016 26 0.014
9 73 0.014 29 0.007
10 73 0.017
11 73 0.017 4 0.017
12 73 0.116 8 0.027
1 74 0.068 26 0.085
2 74 0.051 23 0.147
3 74 0.082 9 0.065 23 0.122
4 74 0.099 21 0.065
5 74 0.057 12 0.102
6 74 0.022 22 0.021
3410 1Z 7 73 0.110 21 0.122
8 73 0.034 26 0.020
9 73 0.020 29 0.020
10 73 0.045
11 73 0.045 4 0.045
12 73 0.275 8 0.093
1 74 0.164 26 0.224
2 74 0.150 23 0.340
3 74 0.218 9 0.176 23 0.311
4 74 0.252 21 0.176
5 74 0.16! 12 0.255
6 74 0.079 22 0.076

-------
APPENDIX C
PHYSICAL AND CHEMICAL DATA

-------
STORET RETRIEVAL DATE 76/06/04
341001
40 59 45.0 074 16 33.0 3
POsIPTON LAKES
34031 NEW JERSEY
013391
11EPALES 2111202
0015 FEET DEPTH CLASS 00
00010 00300 00077 00094 00400 00410 00610 00625 00630 00671
DATE TIME DEPTH WATER DO TRANSP CNDUCTVY PH T ALK NH3—N TOT KJEL N02&N03 PHOS—DIS
FROM OF TEMP SECCHI FIELD CACO3 TOTAL N N—TOTAL ORTHO
TO DAY FEET CENT MG/L INCHES MICRONHO SU HG/I MG/I HG/I HG/I P4G/L P
73/04/17 10 00 0000 12.8 60 190 7.10 36 0.090 0.300 0.460 0.029
10 00 0004 12.8 11.1 180 7.20 34 0.070 0.400 0.500 0.027
10 00 0011 12.5 11.0 198 7.30 36 0.070 0.300 0.500 0.019
73/07/22 11 50 0000 22.1 24 182 7.10 49 0.220 0e900 0.680 0.038
11 50 0005 21.5 5.8 178 7.00 49 0.220 0.600 0.670 0.032
11 50 0012 21.3 3.2 198 7.00 58 0.470 0.900 0.510 0.029
73/10/02 13 05 0000 18.8 38 580 9.20 69 0.040 0.300 0.720 0.008
13 05 0005 18.3 14.4 600 8.90 71 0.040 0.300 0.700 0.006
13 05 0009 17.9 10.0 600 8.20 77 0.240 0.600 0.790 0.006
00665 32217
DATE TIME DEPTH PHOS—TOT CHLRPHYL
FROM OF A
TO DAY FEET MG/L P UGh
73/04/17 10 00 0000 0.054 5.4
10 00 0004 0.054
10 00 0011 0.040
73/07/22 11 50 0000 0.108 9.2
11 50 0005 0.101
11 50 0012 0.142
73/10/02 13 05 0000 0.058 58.9
13 05 0005 0.070
13 05 0009 0.073

-------
STORET RETRIEVAL DATE 76/06/04
341002
41 00 27.0 074 16 29.0 3
POMPTON LAKES
34031 NEW JERSEY
013391
1 1EPALES
0005 FEET
2111202
DEPTH CLASS 00
73/04/17 10 30 0000
10 30 0003
73/07/22 12 15 0000
12 15 0005
73/10/02 13 20 0000
00665 32217
PP$OS-TOT CHLRPHYL
A
MG/L P UGh
0.059
0.060
0.116
0.135
0.101
DATE
TIME
DEPTH
FROM
OF
TO
DAY
FEET
73/04/17
10 30
10 30
0000
0003
73/07/22
12 15
12 15
0000
0005
73/10/02
13 20
0000
DATE
TIME
DEPTH
FROM
OF
TO
DAY
FEET
00010
00300
00077
00094
00400
00410
00610
00625
00630
00671
WATER
DO
TRANSP
CNDUCTVY
PH
T
ALK
NH3—N
TOT KJEL
N021N03
PHOS—DIS
TEMP
SECCHI
FIELD
CACO3
TOTAL
N
N—TOTAL
ORTHO
CENT
MG/L
INCHES
MICROMNO
SO
MG/L
MG/I
MG/L
MG/ I
MG/ I P
12.7
45
190
7.30
37
0.070
0.400
0.500
0.038
12.6
10.0
190
7.40
37
0.060
0.400
0.490
0.036
21.9
20
180
7.20
48
0.180
0.700
0.670
0.040
21.0
7.2
178
7.20
48
0.160
0.700
0.670
0.038
12.1
9.5
43.1

-------
APPENDIX D
TRIBUTARY AND WASTEWATER
TREATMENT PLANT DATA

-------
STORET RETRIEVAL DATE 76/06/04
3410A1
40 59 33.0 074 16 47.0 4
RA iAPO RI ER
34 7.5 POMPTON PLAI
0/POMPTON LAKE
2NDRY RD 3ROG N OF
I 1EPALES
0000 FEET DEPTH
013391
US 202 JCT
2111204
CLASS 00
00630
00625
00610
00671
00665
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3—N
PHOS—DIS
PHOS—TOT
FROM
OF
N—TOTAL
N
TOTAL
OI THO
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L i-
MG/L P
73/07/21
08
45
0.430
0.970
0.132
0.009
0.075
73/08/26
09
00
0.430
1.470
0.129
0.015
0.050
73/09/29
09
00
0.680
1.470
0.160
0.011
0.067
73/11/04
09
00
0.700
1.000
0.168
0.039
0.085
73/12/08
09
00
0.570
0.400
0.088
0.044
0.095
74/01/26
09
30
0.616
0.500
0.095
0.020
0.030
74/02/23
09
00
0.756
0.700
0.110
0.020
0.065
74/03/O
09
00
0.600
0.400
0.035
0.020
0.065
74/03/23
08
20
0.420
0.400
0.045
0.010
0.050
74/04/21
08
30
0.540
0.500
0.050
0.017
0.025
74/05/12
09
00
0.560
0.800
0.080
0.035
0.085
74/06/22
09
00
0.520
0.700
0.080
0.020
0.100

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STORET RETRIEVAL DATE 76/06/04
3410A2
41 01 00.0 074 15 43.0 4
RAMAPO RIVER
34 7.5 WANAQUE
1/POMPTON LAt(E 013391
2NDRY RD BRL)G N OF OAKLAND
I1EPALES 2111204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT P JEL NM3N PHOSDIS PHOSTOT
FROM OF N—TOTAL N TOTAL ORTHO
10 DAY FEET MG/L MG/L MG/L MG/L P HG/L P
73/07/21 09 10 0.750 1.380 0.390 0.063 0.200
73/08/26 09 10 1.040 3.570 0.088 0.042 0.082
73/09/29 09 15 1.480 0.880 0.160 0.078 0.105
73/11/04 09 15 0.870 0.450 0.105 0.069 0.090
73/12/08 09 15 0.580 0.500 0.088 0.040 0.080
09 25 2.100 0.300 0.032 0.005K 0.045
74/01/26 09 55 0.650 0.300 0.125 0.040 0.045
74/02/23 09 15 0.660 0.700 0.165 0.100 0.195
74/03/09 09 10 0.610 0.400 0.095 0.065 0.125
74/03/23 08 40 0.528 0.800 0.230 0.720 0.800
74/04/21 08 45 0.450 2.000 0.065 0.022 0.030
74/06/22 09 15 0.860 0.800 0.110 0.050 0.105
K VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
341081
40 5 40.0 07g. 16 30.0 4
UNNAMED STREAM
34 7.5 POMPTON PLAI
T/POMPTON LAKE 013391
US 202 6I DG IN POMPTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
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 M&/L MG/L MG/L M6/L P MG/L P
73/07/21 09 05 0.310 0.710 0.058 0.024 0.067
73/08/26 09 05 1.140 1.100 0.052 0.031 0.035
73/09/29 09 05 0.520 1.570 0.320 0.017 0.020
73/11/04 09 00 0.390 0.450 0.072 0.013 0.020
73/12/08 09 05 0.440 0.600 0.040 0.008 0.035
74/01/26 09 40 0.640 0.400 0.030 0.010 0.010
74/02/23 09 00 0.630 0.600 0.050 0.010 0.030
74/03/09 09 05 0.800 0.300 0.030 0.010 0.050
74/03/23 08 30 0.560 0.500 0.025 0.005 0.030
74/04/21 08 35 0.504 0.200 0.085 0.015 0.030
74/05/12 09 05 0.410 1.900 0.065 0.015 0.040
74/06/22 09 05 0.312 0.400 0.030 0.015 0.030

-------
STORET RETRIEVAL DATE 76/06/04
3410C1
41 00 18.0 074 17 00.0 4
UNNAMED STREAM
34 7.5 ANAUUE
T/POMPTON LAKE 013391
2NDRY RD 6RDG E EDGE OF LAKE IN POMPTON
11EPALES 2111204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N P, OS—DIS PHOS—TOT
FROM OF N—TOTAL N TOTAL ORTHO
TO DAY FEET MG/L MG/L MG/L HG/L P MG/L P
73/07/21 09 25 2.800 0.820 0.110 0.011 0.055
73/08/26 09 15 1.200 0.052 0.024 0.035
73/09/29 09 25 0.160 0.160 0.016 0.030
73/11/04 09 25 4.600 0.300 0.021 0.048 0.080
74/01/26 10 40 0.640 2.000 0.065 0.005K 0.010
74/02/23 09 25 0.940 0.200 0.040 0.005K 0.015
74/03/09 09 ?5 2.200 0.200 0.025 0.005 0.030
74/03/23 08 50 0.630 0.500 0.020 0.005 0.0 15
74/04/21 08 55 0.300 0.800 0.040 0.010 0.040
74/05/12 09 25 0.790 3.100 0.200 0.015 0.650
74/06/22 09 25 3.200 0.400 0.050 0.040 0.070
K VALUE KNOWN TO BE
LESS THAN INDICAIED

-------
STORET RETRIEVAL DATE 76/06/04
3410AA AS341OAA P003500
41 06 10.0 074 09 10.0 4
RAMAPO COLLEGE (WAYNE)
34 7.5 RAMSEY
T/POMPTON LAKES 013391
RAMAPO RIVER
I1EPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW-MOD
TO DAY FEET MG/L MG/L MG/L MG/I P MG/L P INST MOD MONTHLY
73/07/03 11 00
CP(T)— 7.800 8.200 0.015 1.150 1.200 0.035 0.033
73/07/03 16 00
73/08/01 08 00
CP(T)— 6.800 0.980 0.250 1.500 1.600 0.031 0.033
73/08/01 16 00
73/09/01 07 00
CP(T)— 7.600 1.100 0.294 0.029 0.030
73/09/01 16 00
73/10/01 07 30
CP(T)— 2.200 4.800 2.100 0.490 0.740 0.037 0.040
73/10/01 16 00
73/11/03 08 00
CP(T)— 2.100 13.500 4.500 0.720 1.050 0.040 0.042
73/11/03 16 00
73/12/31 08 00
CP(T)— 12.000 1.600 0.072 1.300 1.700 0.048 0.051
73/12/31 16 00
74/01/02 ii 00 10.100 0.500K 0.040K 1.440 1.500 0.054 0.048
74/01/29 08 00
CP(T)— 6.720 8.250 2.200 1.440 2.700 0.053 0.055
74/01/29 16 00
74/03/12 08 00
CP(T)— 5.040 10.000 0.540 0.750 1.300 0.063 0.061
74/03/12 16 00
74/04/15 08 00
CP(T)— 8.200 11.000 0.370 1.575 2.300 0.073 0.066
74/04/15 16 00
74/05/20 08 00
CP(T)— 8.700 16.000 0.760 2.600 3.400 0.068 0.065
74/05/20 16 00
K VALUE KNOWN TO E
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410A8 AS341OAB
41 06 10.0 074 09 15.0 4
Pt IME EQUITIES (MAHW H)
34 7.5 RAMSEY
T/POMPTON LAKES
RAMAPO RIVER
1 1EPALES
0000 FEET DEPTH
P001225
013391
2141204
CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3-N
P 1105—015
P1105-TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOw-MGD
TO
DAY
FEET
MG/L
MG/L
HG/L
MG/L P
P4G/L P
INST MGD
MONTHLY
73/10/01
08 (10
13.600
1.200
0.760
5.130
5.130
0.014
0.0 14
73/11/07
08 30
7.700
7.100
4.000
3.500
3.625
0.014
0.014
73/12/06
08 30
32.000
3.900
0.040K
3.895
4.000
0.016
0.016
74/01/13
08 30
22.000
1.0001<
0.040K
5.100
5.400
0.015
0.015
74/02/10
08 30
6.800
1.0001<
0.0401<
0.081
0.110
0.015
0.015
74/03/07
08 00
18.400
2.900
0.190
4.700
4.800
0.015
0.0 iS
74/04/10
07 00
14.400
1.0001<
0.050K
0.740
0. 330
0.015
0.015
74/05/05
08 30
7.600
1.000K
0.0501<
0.100
0.160
0.015
0.015
74/06/10
08 00
11.800
1.0001<
0.550
4.563
4.940
0.015
0.015
K VALUE KNOWN TO BE
LESS T 1AN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AC AS34 IOAC
41 06 10.0 074 09 15.0 4
bLUE HILLS (MAHWAH)
34 7.5 RAMSEY
T/POMPTON LAKES
RAMAPO RIVER
1 1EPALES
0000 FEET DEPTH
P000105
013391
2141204
CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT KJEL
Nr13-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLO —MGD
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/10/02
06
30
11.600
2.750
0.040K
2.735
2.740
0.014
0.014
73/11/07
07
30
15.400
0.500K
0.100
6.500
6.875
0.014
0.014
73/12/06
07
30
14.000
1.200
0.025
6.800
7.100
0.015
0.015
74/01/08
07
30
6.000
1.200
0.040K
2.800
3.000
0.018
0.018
74/02/09
08
15
6.600
1.000K
0.095
1.800
1.900
0.020
0.020
74/03/07
07
00
5.400
1.000K
0.050K
1.700
1.750
0.018
0.018
74/04/10
08
30
11.000
1.000K
0.050K
4.400
‘+.900
0.020
0.020
74/05/05
08
00
15. 100
1.250
0.110
6.800
7.200
0.019
0.019
74/06/10
06
30
7.400
1.000K
0.067
7.200
7.200
0.019
0.019
K VALUE KNOWN TO BE
LESS THAN INDICATEt)

-------
STORET RETRIEVAL DATE 76/06/04
3410AD AS341OAD p000363
41 06 10.0 074 09 15.0 4
REGENCY PA Pc APARTMENTS (MAHWAH)
34 7.5 RAMSEY
T/POMPTON LAKES 013391
RAMAPO RIVER
1 1EPALES
0000 FEET DEPTH
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
“J02&N03
TOT KJEL
NH3—N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO
DAY
FEET
P4G/L
MG/L
Mr,/L
HG/L P
MG/L P
INST MGD
MONTHLY
2141204
CLASS 00
73/10/02
08
30
16.800
0.960
0.086
2.800
2.800
0.018
0.018
73/11/07
08
00
12.400
0.160
0.160
2.715
4.900
0.018
0.018
73/12/05
08
30
21.200
0.100K
0.070
2.800
3.900
0.018
0.018
74/01/15
08
00
4.700
15.000
4.400
2.900
3.500
0.018
0.018
74/02/10
08
30
5.200
8.600
3.000
2.200
2.400
0.018
0.018
74/03/07
08
30
11.200
1.800
0.520
3.750
3.900
0.018
0.018
74/04/10
08
00
23.000
1.400
0.050K
2.300
2.400
0.018
0.018
74/05/05
09
00
8.900
1.000K
0.058
3.500
3.700
0.019
0.019
74/06/10
07
00
11.000
1.000K
0.050K
3.750
4.000
0.019
0.019
K VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
34 10AE AS341 OAE
41 02 20.0 074 14 25.0 4
SKYVIEW (OAKLAND)
34 7.5 RAMSEY
T/POMPTON LAKES
RAMAPO RIVER
11 EP ALES
0000 FEET DEPTH
P00 0300
013391
2141204
CLASS 00
DATE
TIMF
DEPTH
N02&N03
TOT KJEL
NH3—N
PHOS—DIS
PHOS-TOT
FLOW
CONDUIT
FROM
OF
N-TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGt)
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/06/27
10
10
10.700
0.110
0.034
6.500
7.480
0.019
0.022
73/08/01
14
30
4.200
A.046
3.400
4.100
0.017
0.022
73/08/31
11
30
4.600
0.110
3.000
3.100
0.019
0.021
73/10/05
14
30
14.000
7.330
0.092
7.325
7.350
0.015
0.020
73/11/05
10
30
16.200
0.580
0.185
6.950
7.500
0.019
0.022
73/12/11
11
00
11.400
0.650
0.046
4.500
4.500
0.019
0.022
74/02/27
10
00
8.600
2.000
1.000
5.750
7.600
0.022
0.023
74/03/25
11
00
9.700
1.000K
0.390
6.300
6.900
0.021
0.021
74/04/30
10
30
13.000
2.?o0
0.210
12.000
12.000
0.021
0.022
74/06/07
10
15
4.300
1.000K
0.001
2.250
2.400
0.022
0.023
74/07/18
13
00
5.880
0.200
2.400
2.000
2.000
0.020
0.021
K VALUE KNOWN TO BE
LESS T 1AN iNDICATED

-------
STORE! RETRIEVAL DATE 76/06/04
3410AF AS34 IQAF
41 02 20.0 074 1’. 25.0 4
OAKw000 KNOLLS (OAKLAND)
34 7.5 RAMSEY
T/POMPTON LAKES
RAMAPO RIVER
1 1EPALES
0000 FEET DEPTH
P000240
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3—N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
013391
2141204
CLASS 00
73/06/27
10
30
5.400
0.130K
0.019
2.940
3.300
0.009
0.012
73/08/01
14
00
2.940
0.370
0.011
4.200
4.700
0.012
0.009
73/08/31
11
00
0.170
2.940
3.000
0.012
0.012
73/10/05
1’.
00
1.300
3.000
0.056
6.950
6.950
0.010
0.012
73/11/05
11
00
1.700
0.750
0.038
‘..800
5.100
0.010
0.012
73/12/11
11
30
1.600
0.600
0.170
2.770
3.100
0.012
0.012
74/02/27
09
00
2.160
5.000
0.071
0.340
0.355
0.016
0.013
74/03/25
11
30
15.000
1,000K
0.070
3.400
3.900
1.000
1.000
74/04/30
11
00
5.000
1.700
0.150
2.900
3.900
0.020
0.018
74/06/07
11
00
2.170
1.000K
0.100K
0.128
0.128
0.018
0.019
74/07/18
11
00
20.000
1.000K
0.340
4.000
5.000
0.018
0.019
K VALUE KNOWN To BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AG SF341OAG P000070
41 00 57.0 074 16 10.0 4
POMPTON LAKES NURSING CONVALESCE
34 7.5 WANAQUE
T/POMPTON LAKES 013391
RAMAPO RIVER
IIEPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW—MOD
TO DAY FEET MG/L MG/L MG/L MG/L P MG/ I P INST MOD MONTHLY
73/07/04 09 00
CPT— 7.200 6.000 0.310 3.600 4.200 0.004 0.004
73/07/04 17 30
73/09/12 08 00
CP(T)— 21.000 1.100 0.105 2.400 2.630 0.004 0.004
73/09/12 16 00
73/10/03 08 00
CP T)— 16.000 2.900 0.091 2.405 2.500 0.004 0.004
73/10/03 15 30
73/11/07 09 00
CP(T)— 14.000 0.500K 0.058 1.800 3.900 0.004 0.004
73/11/07 16 00
73/12/04 09 30
CP(T)— 15.000 0.550 0.048 2.550 2.550 0.004 0.004
73/12/04 16 00
74/01/08 08 00
CP(T)— 4.600 6.800 0.170 3.520 4.200 0.004 0.004
74/01/08 15 00
74/02/10 08 00
CP(T)— 3.900 7.200 2.880 2.760 2.900 0.004 0.004
74/02/12 15 00
74/03/12 07 30
CP(T)— 4.400 6.400 1.400 3.300 3.400 0.004 0.004
74/03/12 15 00
74/04/10 08 00
CPU)— 10.400 1.000K 0.100 2.450 2.600 0.004 0.004
74/04/10 15 00
74/05/08 07 30
CP(T)— 6.100 19.000 0.660 3.700 5.700 0.004 0.004
76/05/08 18 00
74/06/12 08 00
CPU)— 37.800 7.000 2.100 4.100 4.400 0.004 0.004
74/06/12 15 00
74/07/14 09 00
CP(T)— 7.200 5.300 0.250 3.450 4.800 0.004 0.004
74/07/14 19 00
K VALUE KNOWN TO bE
LESS THAN INDICATED

-------
3410AH AS341OAH
41 04 10.0 074 08 12.0 4
HOLIDAY INN (FAIRLA N)
34 7.5 RAMSEY
T/POMPTON LAKES
RAMAPO RIVER
1 1EPALES
0000 FEET DEPTH
STORET RETRIEVAL DATE 76/06/04
P000 20 0
013391
2141204
CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE TIME
DEPTH
N02&N03
TOT KJEL
NH3-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM OF
N-TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/06/29 15 40
2.100
5.800
0.920
7.500
7.700
0.012
0.013
73/07/28 09 00
1.700
13.000
3.900
7.800
9.700
0.013
0.011
73/11/06 14 00
6.900
‘
2.350
0.098
4.900
5.100
0.013
0.013
73/12/08 10 00
5.800
15.500
3.200
14.700
16.500
0.013
0.013
74/03/02 09 00
15.200
1.600
0.500
7.400
9.700
0.013
0.013
74/04/27 09 00
2.400
3.700
0.480
12.500
14.000
0.013
0.013
74/05/11 09 00
6.160
1.200
0.200
9.200
9.400
0.013
0.013
74/08/04 11 00
4.800
12.000
1.550
6.800
7.300
0.013
0.013

-------
STORET RETRIEVAL DATE 76/06/04
3410AJ AS341OAJ
41 01 20.0 074 14 45.0 4
P4AN1TO SCHOOL (OAKLAND)
34 7.5 RAMSEY
T/POHPTON LAKES
AMAPO R1VE
I 1EPALES
0000 FEET DEPTH
P000108
013391
2141204
CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOw-MGO
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/06/27
17 00
0.670
0.100K
0.021
0.185
0.250
0.005
73/08/01
15 00
0.690
1.300
0.130
0.190
0.280
73/09/01
12 00
0.100K
0.510
0.537
0.0001
0.0002
73/10/02
17 00
3.000
21.500
12.600
0.100
0.500
0.004
0.005
73/11/06
08 00
1.050
0.100K
0.019
0.150
0.210
0.003
0.005
73/12/03
16 30
5.800
2.500
0.040K
3.360
4.100
0.005
0.004
74/01/04
12 00
2.320
0.500K
0.040K
0.130
0.147
0.005
0.005
74/03/02
11 00
1.360
0.600
0.050K
0.350
0.420
0.005
74/04/01
18 30
12.600
1.200
0.062
1.450
1.850
0.005
0.005
74/05/02
16 00
0.360
25.000
13.000
7.000
7.800
0.004
0.004
74/06/02
20 00
0.720
2.000
0.110
0.215
0.460
0.005
74/07/04
08 00
1.040
1.100
0.220
0.220
0.305
0.004
K VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AK AS3410AK P001100
41 01 20.0 074 14 45.0 4
INDIAN HILLS HIGH SCHOOLIWYcUOFF
34 7.5 RAMSEY
T/POMPTON LAKES 013391
RAMAPO RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME DEPTH
N02&N03
TOT KJEL
NH3-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTIlO
RATE
FLOW—MGO
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/06/29
10
00
CP(T)—
15.200
0.420
0.062
8.100
8.300
0.005
0.013
73/06/29
14
45
73/08/29
07
30’
CP(T)—
0.022
1.220
1.280
0.008
0.008
73/08/29
13
30
73/09/26
10
00
40.000
0.650
4.387
4.400
0.017
0.017
73/10/26
45.000
0.450
0.054
6.200
6.400
0.018
0.016
73/11/27
08
30
33.000
0.100K
0.097
5.300
5.300
0.017
0.017
73/12/21
23
00
14.000
0.630
0.480
6.200
6.800
0.018
0.015
74/01/25
14
00
25.200
1.300
0.680
7.200
7.200
0.018
0.017
74/02/26
07
30
CP(T)—
28.000
1.600
0.380
6.300
6.500
0.017
0.016
74/02/26
14
30
74/03/26
07
30
CPU)—
30.800
1.000K
0.670
4.600
4.700
0.016
0.016
74/03/26
13
30
74/04/26
08
30
CP(T)—
29.000
1.200
0.100
7.000
7.300
0.016
0.015
74/04/26
13
30
74/05/24
08
00
CP(T)—
26.000
1.000
0.110
7.200
7.800
0.01S
0.014
74/05/24
13
00
74/07/23
14
00
15.100
1.000K
0.180
2.400
2.500
0.004
0.004
ic VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AL TF34 IOAL P000065
41 03 15.0 07’. 12 48.0 4
SWISS CHALET (RAMSEY)
34 7.5 RAMSEY
T/POMPTON LAKE 013391
RAMAPO RIVER
I 1EPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL URTHO RATE FLOw—MGD
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST M jD MONTHLY
73/09/08 17 00 5.040 8.470 0.370 0.005 0.003
73/10/07 12 00 1.980 14.500 1.300 16.000 20.000 0.003 0.003
73/11/03 13 00 1.700 11.000 3.300 7.500 8.400 0.004 0.004
73/12/02 12 00 0.370 34.000 8.800 11.600 18.000 0.004 0.004
74/01/06 13 00 0.360 18.300 4.400 17.600 2 .000 0.005 0.005
74/02/02 14 30 0.240 15.000 6.000 13.200 15.000 0.005 0.004
74/03/02 14 00 0.360 23.000 8.900 16.000 19.000 0.005 0.005
74/03/30 13 30 0.160 22.000 8.300 15.000 21.000 0.006 0.006
74/05/01 17 00 0.160 18.000 2.300 13.000 17.000 0.010 0.010
74/06/01 13 00 0.240 24.000 6.900 10.500 13.500 0.009 0.009
74/06/30 13 00 0.720 19.000 7.300 11.000 12.800 0.009 0.009
74/08/0 1 13 00 2.080 6.600 0.180 6.600 9.700 0.010 0.009
74/08/3! 12 30 2.760 7.800 0.380 6.000 7.425 0.010 0.009

-------
STORET RETRIEVAL DATE 76/Ob/04
3410AN SF34 IOAN P000083
41 04 50.0 074 11 00.0 4
APEX CORP. (MAHWAH)
34 7.5 RAMSEY
T/POMPTON LAKE 013391
RAMAPO RIVER
1IEPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW—MGD
TO DAY FEET MG/L MG/L MG/I MG/L P MG/L P INST HGD MONTHLY
73/09/28 10 30
CP(T)— 0.880 2.800 0.083 1.600 3.750
73/09/28 16 00
73/11/01 10 00
CP(T)— 1.260 5.700 0.047 0.830 2.300
73/11/01 15 30
74/01/16 10 00
CPU)— 1.680 16.000 4.600 7.350 0.009
74/01/16 17 00
74/02/15 10 00
CP(T)— 0.360 13.000 4.100 2.650 4.600 0.009
74/02/15 14 00
74/03/15 09 00 0.320 11.000 0.610 1.250 3.850 0.009
74/04/15 10 00
CP(T)— 0.600 17.000 4.800 2.100 6.100 0.009
74/04/15 14 00

-------
STORET RETRIEVAL DATE 76/06/04
3410AP AS34 IOAP
41 04 38.0 074 08 30.0 4
OKONITE COMPANY (RAMSEY)
34 7.S RAMSEY
T/POMPTON LAKE
I AMPOO RIVER
1 1EPALES
0000 FEET DEPTH
P000149
013391
2141204
CLASS 00
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3-N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST M(,D
MONTHLY
74/02/21
10.100
1.000K
0.040K
1.280
1.400
74/03/06
13.600
1.700
3.390
3.600
3.700
74/04/17
9.400
1.000K
0.061
1.800
1.850
0.003
74/05/15
18.000
2.530
0.730
2.200
2.700
0.003
74/ Ob/04
7.500
1.900
0.050K
1.050
1.050
0.003
74/07/17
11.8 J0
0.300
5.900
1.050
1.150
0.003
74/08/14
12.000
1.300
0.050K
2.800
3.100
0.003
74/09/11
10.600
0.500K
0.050K
1.150
1.150
0.003
74/10/11
8.200
1.000K
0.025K
2.800
3.200
0.003
74/11/11
12.400
1.000K
0.086
1.350
1.350
0.003
74fl2/10
18.400
3.100
1.050
3.750
1.900
0.002
75/01/10
7.000
0.674
0.120
0.780
0.800
0.003
K IALUL KNOWN TO 13E
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AR AS34LOAR
41 04 25.0 074 11 49.0 4
CHAN’S HAWII RESTRAUNT
34 7.5 RAMSEY
T/POMPTON LAKE 013391
RAMPOO RIVER
1IEPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW—MGD
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST MGD MONTHLY
74/01/02 10 00 1.240 5.600 0.210 5.240 7.900 0.009
74/02/21 2.760 1.000K 0.040K 0.650 0.740 0.009
74/03/06 3.000 1.900 0.050 0.970 1.250 0.009
74/04/17 3.520 1.000K 0.050K 0.240 0.140 0.010
74/05/15 2.900 1.400 0.110 0.800 1.100 0.010
74/06/04 3.100 2.200 0.050K 0.495 0.630 0.010
74/07/17 4.000 2.700 0.130 0.930 2.600 0.010
74/08/14 1.560 5.300 0.050K 0.650 0.890 0.009
74/09/11 1.040 3.000 0.220 1.300 1.800 0.010
74/10/11 5.280 1.400 0.100 0.400 0.760 0.009
74/11/11 4.400 5.500 0.100 2.400 3.200 0.009
74/12/10 4.320 2.300 0.073 0.400 0.780 0.009
75/01/10 1.680 1.000K 0.050K 0.094 0.100K 0.010
K VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STORET RETRIEVAL DATE 76/06/04
3410AT AS341OAT
41 04 25.0 074 11 49.0 4
NO—CAR CA RIENS INCOkPOP ATE
34 7.5 RAMSEY
1/POMPTON LAKE
RAMPOO RiVER
1 1EPALES
0000 FEET DEPTH
P000008
013391
2141204
CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
NO2 NO3
TOT KJEL
NH3—N
PHOS—DIS
PHOS-TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGO
TO
DAY
FEET
P 1(,/L
MG/L
MG/L
MG/L P
MG/L P
INST MGO
MONTHLY
74/01/0?
10 30
10.900
0.500K
0.040K
1.240
1.250
0.001
74/02/21
9.240
4.500
4.500
1.360
1.450
0.001
74/03/06
13.000
2.800
1.800
1.450
1.550
0.001
74/04/17
11.800
1.000K
0.420
0.930
1.000
0.002
74/05/15
11.200
1.030K
0.050K
0.860
1.000
0.002
74/06/04
10.400
1.500
0.050K
0.875
0.875
0.002
74/07/17
24.000
1.000K
0.061
1.720
1.870
0.001
74/08/14
8.000
3.100
0.050K
0.530
0.580
0.001
74/09/11
11.000
0.500K
0.050K
0.940
0.970
0.001
74/10/11
16.000
1.000K
0.330
1.330
1.330
0.001
74/11/11
13.200
1.000K
0.050K
1.500
1.500
0.001
74/12/10
12.800
1.400
0.050K
1.050
1.400
0.001
75/01/10
1.840
1.000K
0.050K
0.300
0.310
0.001
K VALUE KNOWN TO BE
LESS THAN INDICATED

-------
STONET RETRIEVAL DATE 76/06/04
3410XA AS34 IOXA
41 05 50.0 074 08 15.0 4
HAMILTONIAN FIDELITY(MAHWAH)
34 7.5 RAMSEY
T/POMPTON LAKES
MASONICVS bROOK
1 IEPALES
0000 FEET DEPTH
2141204
CLASS 00
P00 0500
013391
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NPI3—N
PHOS—DIS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N—TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO
DAY
FEET
MG/L
MG/L
MG/L
MG/L P
MG/L P
INST MGD
MONTHLY
73/07/16
09 15
2.400
34.000
21.000
4.500
4.900
0.033
0.040
73/08/15
11 00
8.600
1.400
0.650
3.400
0.040
0.032
73/09/15
10 30
10.500
1.200
0.220
3.760
3.900
0.040
0.041
73/10/19
10 00
25.000
4.590
0.020
4.581
4.700
0.026
0.030
73/11/17
09 00
3.570
17.500
15.000
3.570
4.000
0.003
0.003
73/12/17
16 45
16.200
4.300
0.800
2.900
2.900
0.040
0.032
74/01/15
09 00
1.040
i • 000
0.540
2.500
2.900
0.033
0.031
74/02/15
boa
5.000
16.000
9.800
3.100
3.100
0.040
0.038
74/03/15
08 30
0.040
28.000
0.230
3.300
0.040
0.031
74/04/15
10 00
10.600
4.500
2.400
3.300
4.100
0.004
0.043
74/05/16
09 00
0.156
38.000
24.000
4.500
5.600
0.037
0.022
74/06/17
09 30
24.530
8.300
5.100
3.100
3.400
0.004
0.003
74/07/15
10 00
1.320
6.400
0.200
3.100
3.300

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STORET RETRIEVAL DATE 76/06/04
341 0Y4 AS341OYA P000056
41 04 20.0 074 10 50.0 4
SOCIETY HILLS (MAH AH)
34 7.5 RAMSEY
T/POMPTON LAKES 013391
DARLINGTON BROOK
I1LPALES 2141204
0000 FEET DEPTH CLASS 00
00630 00625 00610 00671 00665 50051 50053
DATE TIME DEPTH N02&N03 TOT KJEL NH3—N PHOS—DIS PHOS—TOT FLOW CONDUIT
FROM OF N—TOTAL N TOTAL ORTHO RATE FLOW—MGD
TO DAY FEET MG/L MG/L MG/L MG/L P MG/L P INST MGD MONTHLY
73/07/16 14 Ofl 21.000 0.230 0.126 3.720 3.825 0.006 0.006
73/08/17 17 00 16.200 0.100 4.000 0.006 0.005
73/09/16 14 00 27.200 0.500K 0.105 9.350 9.550 0.005 0.006
73/10/19 09 30 27.000 0.100K 0.017 12.600 15.700 0.005 0.006
73/11/17 08 45 4.100 24.000 1?.000 10.400 12.300 0.006 0.001
73/12/17 16 00 4.200 17.000 2.730 3.200 4.500 0.005 0.005
74/01/15 10 30 1.680 27.000 12.000 6.000 8.400 0.006 0.005
74/02/15 11 45 4.000 17.000 7.700 4.200 4.400 0.006 0.005
74/03/16 09 00 0.920 30.000 23.000 7.000 8.500 0.006 0.005
74/04/15 11 00 0.760 6.800 5.200 4.100 4.900 0.005 0.006
74/05/16 11 30 5.880 5.100 0.450 3.600 4.200 0.006 0.008
74/06/17 11 45 24.500 6.200 3.750 3.000 3.000 0.007 0.006
74/07/15 11 30 12.000 3.400 5.900 S.900 0.007 0.006
K VALUE KNOWN TO dE
LESS [ HAN INDICATEO

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STORET RETRIEVAL DATE 76/06/04
3c.1 OZA TF34 IOZA P0001 50
41 04 25.0 074 11 49.0 4
US ARMY ,IOUSING AREA
34 7.5 RAMSEY
T/POMPTON LAKE 013391
STREAM LEADING TO RAMPOO RIVER
11EPALES 2141204
0000 FEET DEPTH CLASS 00
00630
00625
00610
00671
00665
50051
50053
DATE
TIME
DEPTH
N02&N03
TOT KJEL
NH3—N
PHOS—OLS
PHOS—TOT
FLOW
CONDUIT
FROM
OF
N-TOTAL
N
TOTAL
ORTHO
RATE
FLOW—MGD
TO
DAY
FEET
MG/L
MG/L
MG/I
MG/L P
MG/L P
INST MGD
MONTHLY
73/12/07
10
00
0.920
1.430
0.690
0.360
0.630
0.005
0.005
74/01/10
11
00
0.200
6.000
0.130
1.500
1.800
0.007
0.008
74/02/07
11
00
0.480
6.600
4.000
1.760
2.100
0.007
0.006
74/03/07
12
00
0.480
3.400
2.300
1.530
1.b50
- 0.010
0.0 10
74/04/09
0.280
5.300
3.225
0.900
0.985
0.010
0.010
74/05/07
10
00
0.440
14.000
5.900
2.850
3.600
0.010
0.010
74/06/10
10
00
0.200
8.300
4.300
2.000
2.400
0.010
0.010
74/07/08
0.600
8.600
3.800
1.075
1.350
0.010
0.010
74/08/08
12
00
0.320
2.000
0.450
0.700
0.930
0.010
0.010
74/09/10
0.320
0.500K
0.090
0.210
0.220
0.010
0.070
74/10/08
10
00
0.280
1.300
0.530
0.500
0.570
0.010
0.070
74/11/08
12
30
0.240
1.000K
0.050K
0.218
0.279
0.010
0.070
74/12/06
11
30
0.400
1.400
0.089
0.600
0.300
0.010
0.070
K VALUE KNOWN TO 8E
LESS THAN INDICATED

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STORET RETRIEVAL DATE 76/06/04
74/01/02 09 30
74/02/21
74/0 3/06
74/04/17
74/05/15
74/06/04
74/07/17
74/08/14
74/09/11
74/11/08
74/12/10
75/0 1/10
1.400
0.280
0.240
0.280
I) • 153
0.400
0.120
0.588
0.280
0.240
0.320
0.480
23.000
29. 000
32.000
37. 000
42.000
35. 000
30.000
25.000
27. 0 00
34 .000
31.000
1.600
1.280
3 • 400
4 • 400
4.750
4.700
3 • 600
3.30 0
2.20 0
2.200
4.000
3.150
3410Zb SF3410Z8
41 00 43.0 074 11 41.0 4
IPI—CORNER REALTY
34 7.5 RAMSEY
T/POMPTON LAKE 013391
PAULIS POND TO RAMPOO RIVE R
11EPALES 2141204
0000 FEET DEPTH CLASS 00
3.000
2.300
4.800
6.600
6.900
5.900
4.900
4.100
3.670
4.100
7.200
4.650
0.001
0.00 1
0.00 1
0.00 1
0.00 1
0.00 1
0.001
0.001
0.001
DATE
FROM
TO
TIME DEPTH
OF
DAY FEET
00630
NO2&N03
i-TOTAL
MG/L
00625
TOT KJEL
N
MG/L
00671
PpIOS-OIS
OPT HO
P4G/L P
00665 50051
PHOS—TOT FLOW
RATE
MG/L P INST MGD
50053
CONDUIT
FLOW—MGD
MONTHLY
00610
NH3—N
TOTAL
MG/L
12. 600
13. 000
16. 000
24. 000
22. 000
22. 000
15. 700
6.400
19. 000
21.000
16. 00 0

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APPENDIX E
PARAMETRIC RANKINGS OF LAKES
SAMPLED BY NES IN 1973
STATE OF NEW JERSEY

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LAKE DATA TO BE USED IN RANKINGS
LAKE
CODE
LAKE NAME
MEDIAN
TOTAL P
MEDIAN
INOR& N
500—
MEAN SEC
MEAN
Cp-4LORA
iS-
MIN DO
MEDIAN
UISS OrUHO P
3402
8UDD LAKE
0.082
0.205
474.000
48.500
7.400
0.012
3’.03
GREENwOOD LAKE
0.021
0.100
414.250
11.920
14.800
0.007
3406
ORADELL RESERVO1
0.055
0.990
462.500
22.267
13.600
0.00
3409
PINECLIFF LAKE
0.070
0.175
465.500
38.960
11.000
0.011
3410
POMPTON LAKES
0.071
0.795
463.167
23.033
11.800
0.029
3412
DUHERNAL LAKE
0.082
1.420
466.667
6.800
8.600
0.010
3413
FARRINGTON LAKE
0.055
0,770
462.000
8.283
14.4(0
0.012
3415
LAKE HOPATCONG
0.022
0.120
416.333
13.627
14.900
0.007
3417
LAKE MUSCONETCONG
0.036
0.140
436.000
11.067
6.000
0.010
3419
PAULINS KILL LAKE
0.133
0.950
460.500
7.017
9.000
0.065
3420
SPRUCE RUN RESERVOIR
0.020
0.470
428.667
15.333
15.000
0.007
3422
UNION LAKE
0.063
1.150
463.200
22.080
12.800
0.018
3423
WANAQUE RESERVOIM
0.014
0.120
355.333
7.111
14.800
0.005

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PERCENT OF LAKES wITii RIGHEP VALUES (NUMBER OF LAKES ITt-4 MIGHER VALUES)
LAKE
CODE
LAKE NAME
MEDIAN
TOTAL P
MEDIAN
INORG
N
500—
MEAN SEC
MEAN
CHLORA
15—
HIN Du
DISS
MEL)IAN
ORTHO P
INUEX
NO
3402
BUDO LAKE
12 (
1)
58 (
7)
0 (
0)
0 C
0)
92 C 11)
2
( 3)
191
3403
GREENwOOD LAKE
83 (
10)
100 C
12)
92 (
11)
58 C
7)
21 C 2)
83
C 9)
437
3406
ORADELL RESERVOIR
54 (
6)
17 C
2)
42 C
5)
25 C
3)
42 C 5)
67
( 8)
2’.7
3409
PINECLIFF LAKE
33 C
4)
67 (
8)
17 (
2)
8 C
1)
67 C 8)
42
C 5)
234
3410
POMPTON LAKES
25 C
3)
33 (
4)
33 C
4)
17 (
2)
58 C 7)
8
( 1)
174
3412
DUMERNAL LAKE
12 C
1)
0 (
0)
8 C
1)
100 C
12)
83 ( 10)
58
( 7)
261
3413
FARRINGTON LAKE
54 (
6)
42 C
5)
50 ( 6)
75 C
9)
33 C 4)
29
C 3)
283
3415
LAKE HOPATCONG
75 C
9)
87 C
10)
83 C 10)
50 (
6)
8 C 1)
83
C 9)
386
3417
LAKE MUSCUNETCONG
67 C
8)
75 C
9)
67 ( 8)
67 C
8)
100 C 12)
50
C 6)
426
3419
PAULINS KILL LAKE
0 (
0)
25 C
3)
58 ( 7)
92 C
11)
75 ( 9)
0
( 0)
250
3420
SPRUCE PUN RESERVOIR
92 (
11)
50 C
6)
75 C 9)
42 C
5)
0
C 0)
83
C 9)
342
3422
UNION LAKE
42 C
5)
8 (
1)
25 ( 3)
33 C
4)
50
C 6)
17
C 2)
175
3423 WANAQUE RESERVOIR
100 C 12) 87 ( 10) 100 C 12) 83 C 10) 21 ( 2) 100 C 12)
491

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LAKES RANKED BY INDEX NOS.
RANK LAKE CODE LAKE NAME INDEX NO
1 3423 WANAQUE RESERVOIR 491
2 3403 GREENWOOD LAKE 437
3 3417 LAKE MUSCONETCONG 426
4 3415 LAKE HOPATCOP4G 386
5 3420 SPRUCE RUN RESERVOIR 342
6 3413 FARRINGTON LAKE 283
7 3412 OUMERNAL LAKE 261
8 3419 PAULINS KILL LAKE 250
9 3406 ORADELL RESERVOIR 247
10 3409 PINECLIFT LAKE 234
11 3402 BUDD LAKE 191
12 3422 UNION LAKE 175
13 3410 POMPTON LAKES 174

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