Document ID: EPA-HQ-OW-2012-0095-0018
Agency: epa
Document Type: Supporting & Related Material
Title: 
Posted Date: 2012-04-19T04:00Z

Surface Water Quality Standards

N. J. A. C.  7:9B

NEW JERSEY DEPARTMENT OF ENVIRONMENTAL PROTECTION

Environmental Planning and Science

January 2002

STATE OF NEW JERSEY

Jim McGreevey, Governor

DEPARTMENT OF ENVIRONMENTAL PROTECTION

Bradley Campbell, Commissioner

ENVIRONMENTAL PLANNING AND SCIENCE

Leslie McGeorge, Assistant Commissioner

SURFACE WATER QUALITY STANDARDS

Authority

N.J.S.A. 13:1D-1 et seq., 58:10A-1 et seq.,and 58:11A-1 et seq.

Effective Date

April 17, 1998

Amendments - January 22, 2002

Executive Order No. 66(1978) Expiration Date

Chapter 9B, Surface Water Quality Standards, expires on April 18, 2003

A copy of this document can be obtained by calling 609-984-0058

or by sending a written request to:

Environmental Planning and Science

Department of Environmental Protection

P.O. Box 418

Trenton, NJ 08625

Subchapter 1.SURFACE WATER QUALITY STANDARDS

TABLE OF CONTENTS

Section	Subject								Page

7:9B-1.1 	Scope of subchapter						1

7:9B-1.2 	Construction								1

7:9B-1.3 	Severability								1

7:9B-1.4 	Definitions								1

7:9B-1.5 	Statements of policy						11

7:9B-1.6 	Establishment of water quality-based effluent limitations	23

7:9B-1.7 	Waterway loadings in areawide water quality 			24

   management plans

7:9B-1.8 	Procedures for modifying water quality-based 			24

   effluent limitations for individual dischargers to 

   Category One waters

7:9B-1.9 	Procedures for modifying water quality-based effluent 		26

   limitations for individual dischargers to 

   Category Two waters.

7:9B-1.10 	Procedures for reclassifying specific segments for less	27

   restrictive uses

7:9B-1.11 	Procedures for reclassifying specific segments for more 	29

   restrictive uses

7:9B-1.12 	Designated uses of FW1, PL, FW2, SE1, SE2, SE3, 		30

   and SC waters

7:9B-1.13 	Designated uses of mainstem Delaware River 			31

   and Delaware Bay 

7:9B-1.14 	Surface water quality criteria					32

7:9B-1.15 	Surface water classifications for the waters of the 		56

   State of New Jersey

CHAPTER 9B  SURFACE WATER QUALITY STANDARDS

SUBCHAPTER 1.  SURFACE WATER QUALITY STANDARDS

7:9B-1.1  Scope of subchapter

Unless otherwise provided by rule or statute, this subchapter shall
constitute the rules of the Department of Environmental Protection
governing matters of policy with respect to the protection and
enhancement of surface water resources, class definitions and quality
criteria, use designation and quality criteria for the mainstem of the
Delaware River including the Delaware Bay, the classification of surface
waters of the State, procedures for establishing water quality-based
effluent limitations, modification of water quality-based effluent
limitations, procedures for reclassifying specific segments for less
restrictive uses and procedures for reclassifying specific segments for
more restrictive uses pursuant to N.J.S.A. 13:1D-1 et seq., the New
Jersey Water Pollution Control Act, N.J.S.A. 58:10A-1 et seq., and the
Water Quality Planning Act, N.J.S.A. 58:11A-1 et seq.

7:9B-1.2  Construction

This subchapter shall be liberally construed to permit the Department
and its various divisions to discharge their statutory functions.

7:9B-1.3  Severability

If any subchapter, section, subsection, provision, clause, or portion of
this chapter, or the application thereof to any person, is adjudged
unconstitutional or invalid by a court of competent jurisdiction, such
judgment shall be confined in its operation to the subchapter, section,
subsection, clause, portion, or application directly involved in the
controversy in which such judgment shall have been rendered and it shall
not affect or impair the remainder of this chapter or the application
thereof to other persons.

7:9B-1.4  Definitions

The following words and terms, when used in this subchapter, shall have
the following meanings, unless the context clearly indicates otherwise.

"Acute toxicity" means a lethal or severe adverse sublethal effect (for
example, immobilization of daphnids) to an organism exposed to a toxic
substance for a relatively short period of time.  Acute toxicity is
measured by short-term bioassays, generally of 48 or 96 hour duration.

"Agricultural water supply" means water used for field crops, livestock,
horticulture, and silviculture.

"Ambient temperature" means the temperature of a waterbody beyond the
portion of the waterbody that is affected by the localized heated waste
discharge or discharge complex; or the temperature of a waterbody that
would exist without addition of heated discharges.

"Anadromous fish" means fish that spend most of their life in saline
waters and migrate to fresh waters to spawn.

"Aquatic substrata" means soil material and associated biota underlying
the water.

"Bioaccumulation" means the increase of the concentration of a substance
within the tissues of an organism, to levels in excess of that
substance's ambient environmental concentration, directly from the water
or through the ingestion of food (usually other organisms).

"Bioconcentration" means the net accumulation of a substance by an
aquatic organism, as a result of uptake directly from the ambient water,
through the gill membrane or other external body surfaces.

"Bioassay" means a toxicity test using aquatic organisms to determine
the concentration or amount of a toxic substance causing a specified
response in the test organisms under stated test conditions.

"Biota" means the animal and plant life of an ecosystem; flora and fauna
collectively.

"Calculable changes" means changes to water quality characteristics as
demonstrated by any acceptable mathematical, predictive method.

"C1" means Category One waters.

"C2" means Category Two waters.

"Category one waters" means those waters designated in the tables in
N.J.A.C. 7:9B-1.15(c) through (h), for purposes of implementing the
antidegradation policies set forth at N.J.A.C. 7:9B-1.5(d), for
protection from measurable changes in water quality characteristics
because of their clarity, color, scenic setting, other characteristics
of aesthetic value, exceptional ecological significance, exceptional
recreational significance, exceptional water supply significance, or
exceptional fisheries resource(s).  These waters may include, but are
not limited to:

1. Waters originating wholly within Federal, interstate, State, county,
or municipal parks, forests, fish and wildlife lands, and other special
holdings that have not been designated as FW1 at N.J.A.C. 7:9B-1.15(h)
Table 6;

2. Waters classified at N.J.A.C. 7:9B-1.15(c) through (g) as FW2 trout
production waters and their tributaries;

3. Surface waters classified in this subchapter as FW2 trout
maintenance or FW2 nontrout that are upstream of waters classified in
this subchapter as FW2 trout production;

4. Shellfish waters of exceptional resource value; or

5. Other waters and their tributaries that flow through, or border,
Federal, State, county, or municipal parks, forests, fish and wildlife
lands, and other special holdings.

"Category two waters" means those waters not designated as Outstanding
National Resource Waters or Category One at N.J.A.C. 7:9B-1.15 for
purposes of implementing the antidegradation policies set forth at
N.J.A.C. 7:9B-1.5(d).

"Chlorine produced oxidants" means the sum of free and combined chlorine
and bromine as measured by the methods approved under N.J.A.C. 7:18.  In
fresh waters the oxidants measured are comprised predominantly of
hypochlorous acid (HOCl), hypochlorite ion (OCl ADVANCE \u3 - ADVANCE
\d3 ), monochloramine and dichloramine.  In saline waters the oxidants
measured are comprised predominantly of the oxidants listed for fresh
waters plus hypobromous acid (HOBr), hypobromite ion (OBr ADVANCE \u3 -
ADVANCE \d3 ) and bromamines.

"Chronic toxicity" means death or other adverse impacts that affect the
growth, survival, or reproductive success of an organism or its progeny
after a relatively long exposure period to toxic substances.  Chronic
toxicity is measured using intermediate-term or long-term bioassays.

(Complete mix( means a twenty five percent (25%) or less variation in
concentration across the transect of the water body.

"Criteria" means those elements of the Surface Water Quality Standards,
expressed as constituent concentrations, levels, or narrative
statements, representing a quality of water that supports a particular
use.  When the criteria are met, water quality will generally protect
the designated use.

"Department" means the New Jersey Department of Environmental
Protection.

"Designated use" means those surface water or ground water uses, both
existing and potential, that have been established by the Department for
waters of the State.

"Diadromous fish" means fish that spend most of their life in one type
of water, either fresh or saline, and migrate to the other type to
spawn.

"Disinfection" means the removal, destruction, or inactivation of
pathogenic and indicator organisms.

(Dissolved metal( means the concentration of metal that passes through a
0.45 (m membrane filter (as defined in (Methods for Chemical Analysis of
Water and Wastes,( EPA-600/4-79-020, March 1979).

"DRBC" means Delaware River Basin Commission.

"EC50" means the median effective concentration of a toxic substance
expressed as a statistical estimate of the concentration that has a
specified adverse effect on 50 percent of the test organisms under
specified test conditions, based on the results of an acute bioassay.

"Epilimnion" means the freely circulating upper region of a thermally
stratified waterbody extending from the surface to the thermocline.

"Existing uses" means those uses actually attained in the waterbody on
or after November 28, 1975, whether or not they are included in the
Surface Water Quality Standards.

"Federal Act" means the "Federal Water Pollution Control Act" (33 U.S.C.
( 1251 et seq.), commonly referred to as the Clean Water Act, including
all subsequent supplements and amendments.

"Flow-through bioassay" means a toxicity test in which the test
solutions flow into and out of the test chambers on a once-through basis
for the duration of the test, in accordance with N.J.A.C. 7:18.

"Fresh water(s)" means all nontidal and tidal waters generally having a
salinity, due to natural sources, of less than or equal to 3.5 parts per
thousand at mean high tide.

"FW" means the general surface water classification applied to fresh
waters.

"FW1" means those fresh waters, as designated in N.J.A.C. 7:9B-1.15(h)
Table 6, that are to be maintained in their natural state of quality
(set aside for posterity) and not subjected to any man-made wastewater
discharges or increases in runoff from anthropogenic activities.  These
waters are set aside for posterity because of their clarity, color,
scenic setting, other characteristic of aesthetic value, unique
ecological significance, exceptional recreational significance,
exceptional water supply significance, or exceptional fisheries
resource(s).

"FW2"  means the general surface water classification applied to those
fresh waters that are not designated as FW1 or Pinelands Waters.

"Groundwater" means that portion of water beneath the land surface that
is within the zone of saturation (below the water table) where pore
spaces are filled with water.

"Heat dissipation area" means a mixing zone, as may be designated by the
Department, into which thermal effluents may be discharged for the
purpose of mixing, dispersing, or dissipating such effluents without
creating nuisances, hazardous conditions, or violating the provisions of
this chapter, the Surface Water Quality Standards.

"Hypolimnion" means the lower region of a stratified waterbody that
extends from the thermocline to the bottom of the waterbody, and is
isolated from circulation with the upper waters, thereby receiving
little or no oxygen from the atmosphere.

"Important species" means species that are commercially valuable (for
example, within the top 10 species landed, by dollar value);
recreationally valuable; threatened or endangered; critical to the
organization and/or maintenance of the ecosystem; or other species
necessary in the food web for the well-being of the species identified
in this definition.

"Industrial water supply" means water used for processing or cooling.

"Intermittent stream" means a stream with a MA7CD10 flow of less than
one-tenth (0.1) cubic foot per second.

"Lake, pond, or reservoir" means any impoundment, whether naturally
occurring or created in whole or in part by the building of structures
for the retention of surface water, excluding sedimentation control and
stormwater retention/detention basins and ponds designed for treatment
of wastewater.  Lakes, ponds, and reservoirs are characterized by a long
term or permanent downgradient restriction of surface water flow from
the impoundment and areas of quiescent water within the body of the
impoundment.  Lakes, ponds, and reservoirs are frequently characterized
by greater water depths within the impoundment than either the
upgradient or downgradient surface water flow and by shallow water
lateral edges containing emergent or submerged plant species.  For
regulatory purposes, the upgradient boundary of a lake, pond,
impoundment, or reservoir shall be considered to be the point at which
areas of greater depth and relatively quiescent water can be
differentiated from the upgradient surface water input into the
impoundment under average flow conditions.

"LC50" means the median lethal concentration of a toxic substance,
expressed as a statistical estimate of the concentration that kills 50
percent of the test organisms under specified test conditions, based on
the results of an acute bioassay.

"Limiting nutrient" means a nutrient whose absence or scarcity exerts a
restraining influence upon an aquatic biological population.

(Load allocation( means the portion of a receiving water(s total maximum
daily load (TMDL) for a specific pollutant that is allocated to existing
or future nonpoint sources of pollution.

"MA1CD10" means the minimum average one day flow with a statistical
recurrence interval of 10 years.

"MA7CD10" means the minimum average seven consecutive day flow with a
statistical recurrence interval of 10 years.

"MA30CD10" means the minimum average 30 consecutive day flow with a
statistical recurrence interval of ten years.

"Measurable changes" means changes measured or determined by a
biological, chemical, physical, or analytical method, conducted in
accordance with USEPA approved methods as identified in 40 C.F.R. 136 or
other analytical methods (for example, mathematical models, ecological
indices) approved by the Department, that might adversely impact a water
use (including, but not limited to, aesthetics).

"Natural flow" means the water flow that would exist in a waterway
without the addition of flow of artificial origin.

"Natural water quality" means the water quality that would exist in a
waterway or a waterbody without the addition of water or waterborne
substances from artificial origin.

"NJPDES" means New Jersey Pollutant Discharge Elimination System.

"Nondegradation waters" means those waters set aside for posterity
because of their clarity, color, scenic setting, other characteristic of
aesthetic value, unique ecological significance, exceptional
recreational significance, or exceptional water supply significance. 
These waters include all waters designated as FW1 in this subchapter.

"Nonpersistent" means degrading relatively quickly, generally having a
half-life of less than 96 hours.

"Nonpoint source" or "NPS" means:

1. Any man-made or man-induced activity, factor, or condition, other
than a point source, from which pollutants are or may be discharged;

2. Any man-made or man-induced activity, factor, or condition, other
than a point source, that may temporarily or permanently change any
chemical, physical, biological, or radiological characteristic of waters
of the State from what was or is the natural, pristine condition of such
waters, or that may increase the degree of such change; or

3. Any activity, factor, or condition, other than a point source, that
contributes or may contribute to water pollution.

"Nontrout waters" means fresh waters that have not been designated in
N.J.A.C. 7:9B-1.15(b) through (h) as trout production or trout
maintenance.  These waters are generally not suitable for trout because
of their physical, chemical, or biological characteristics, but are
suitable for a wide variety of other fish species.

"NPDES" means National Pollutant Discharge Elimination System.

"NT" means nontrout waters.

"Nutrient" means a chemical element or compound, such as nitrogen or
phosphorus, which is essential to and promotes the growth and
development of organisms.

"Outstanding National Resource Waters" or "ONRW" means high quality
waters that constitute an outstanding national resource (for example,
waters of National/State Parks and Wildlife Refuges and waters of
exceptional recreational or ecological significance).  Waters classified
as FW1 waters and Pinelands waters are Outstanding National Resource
Waters.

"Persistent" means relatively resistant to degradation, generally having
a half life of over 96 hours.

"Pinelands waters" means all waters within the boundaries of the
Pinelands Area, except those waters designated as FW1 in N.J.A.C.
7:9B-1.15(h) Table 6, as established in the Pinelands Protection Act
(N.J.S.A. 13:18A-1 et seq.) and shown on Plate 1 of the "Comprehensive
Management Plan" adopted by the New Jersey Pinelands Commission in
November 1980.

"PL" means the general surface water classification applied to Pinelands
Waters.

"Point source" or "PS" means any discernible, confined, and discrete
conveyance, including, but not limited to, any pipe, ditch, channel,
tunnel, conduit, well, discrete fissure, container, rolling stock,
concentrated animal feeding operation, landfill leachate collection
system, vessel, or other floating craft, from which pollutants are or
may be discharged.  This term does not include return flows from
irrigated agriculture.

"Pollutant" means any dredged spoil, solid waste, incinerator residue,
filter backwash, sewage, garbage, refuse, oil, grease, sewage sludge,
munitions, chemical wastes, biological materials, medical wastes,
radioactive substance (except those regulated under the Atomic Energy
Act of 1954, as amended (42 U.S.C. ( 2011 et. seq. )), thermal waste,
wrecked or discarded equipment, rock, sand, cellar dirt and industrial,
municipal, agricultural and construction waste or runoff or other
residue discharged directly or indirectly to the land, ground waters or
surface waters of the State, or to a domestic treatment works as defined
at N.J.A.C. 7:14A-1.2.  "Pollutant" includes both hazardous and
nonhazardous pollutants.

(Potable surface water intake( means any structure or apparatus used to
withdraw surface waters directly or indirectly that is conveyed to a
potable treatment plant or is used for other potable purposes.

"Primary contact recreation" means water related recreational activities
that involve significant ingestion risks and includes, but is not
limited to, wading, swimming, diving, surfing, and water skiing.

"Public hearing" means a legislative type hearing before a
representative or representatives of the Department providing the
opportunity for public comment, but does not include cross-examination.

(Regulatory mixing zones( means areas of surface waters established
pursuant to this chapter for the purpose of initial mixing, dispersion,
or dissipation of wastewater effluent at or near the discharge point. 
Regulatory mixing zones may be established for applicable criteria.

"River mile" or "R.M." means the distance, measured in statute miles,
between two locations on a stream, with the first location designated as
mile zero.  For example, mile zero for the Delaware River is located at
the intersection of the center line of the navigation channel and a line
between the Cape May Light, New Jersey, and the tip of Cape Henlopen,
Delaware.

"Saline waters" means waters having salinities generally greater than
3.5 parts per thousand at mean high tide.

"SC" means the general surface water classification applied to coastal
saline waters.

"SE" means the general surface water classification applied to saline
waters of estuaries.

"Secondary contact recreation" means recreational activities where the
probability of water ingestion is minimal and includes, but is not
limited to, boating and fishing.

"Shellfish" means those mollusks commonly known as clams, oysters, or
mussels.

"Shellfish waters" means waters classified as Approved, Seasonally
Approved, Special Restricted, Seasonally Special Restricted or Condemned
that support or possess the potential to support shellfish which are
within the Coastal Area Facility Review Act (C.A.F.R.A.) zone as
delineated in 1973, (excluding: 1 - The Cohansey River upstream of
Brown's Run; 2 - The Maurice River upstream of Route 548; 3 - The Great
Egg Harbor River upstream of Powell Creek; 4 - The Tuckahoe River
upstream of Route 50; 5 - The Mullica River upstream of the Garden State
Parkway) plus the adjacent areas between Route 35 (from its juncture
with the C.A.F.R.A. zone just north of Red Bank to its juncture with the
C.A.F.R.A. zone just south of Keyport) and the C.A.F.R.A. zone and the
area from the C.A.F.R.A. zone on the south northwesterly along Route 35
to the northern shore of the Raritan River, then easterly along the
northern shore of the Raritan River to the southeast point of Perth
Amboy, then due east to the New Jersey jurisdictional limit, and seaward
along the jurisdictional limit to the Atlantic Ocean.

(State Act( means the New Jersey (Water Pollution Control Act,( N.J.S.A.
58:10A-1 et seq., as amended.

"Stream temperature" means the temperature of a stream outside of a
designated heat dissipation area.

"Surface water classifications" means names assigned by the Department
as set forth at N.J.A.C. 7:9B-1.15(b) through (h) to waters having the
same designated uses and water quality criteria (for example, FW1, PL,
FW2-NT, SE1, SC, Zone 1C).

"Surface Water Quality Standards" (SWQS) means the rules, in this
chapter, N.J.A.C. 7:9B, which set forth, designated uses, use
classifications, and water quality criteria for the State's waters based
upon such uses, and the Department's policies concerning these uses,
classifications and criteria.

"Surface waters" means water at or above the land's surface which is
neither groundwater nor contained within the unsaturated zone,
including, but not limited to, the ocean and its tributaries, all
springs, streams, rivers, lakes, ponds, wetlands, and artificial
waterbodies.

"Thermal alterations" means the increase or decrease in the temperature
of surface waters, above or below the natural temperature, that may be
caused by the activities of man.

"Thermocline" means the plane of maximum rate of change in temperature
with respect to depth.

"Tidal waters" means fresh or saline water under tidal influence, up to
the head of tide.

"TM" means trout maintenance.

"Total maximum daily load" or "TMDL" means a total maximum daily load
formally established pursuant to Section 7 of the Water Quality Planning
Act (N.J.S.A. 58:11A-7) and Section 303(d) of the Clean Water Act, 33
U.S.C. ((1251 et seq.  A TMDL is the sum of individual wasteload
allocations for point sources, load allocations for nonpoint sources of
pollution, other sources such as tributaries, or adjacent segments, and
allocations to a reserve or margin of safety for an individual
pollutant.

"Total recoverable metal" means the concentration of metal in an
unfiltered sample following treatment with hot dilute mineral acid (as
defined in "Methods for Chemical Analysis of Water and Wastes",
EPA-600/4-79-020, March 1979, incorporated herein by reference).

"Toxic substance" or "toxic pollutant" means any pollutant identified
pursuant to the Federal Act, or any pollutant or combination of
pollutants, including disease causing agents, which after discharge and
upon exposure, ingestion, inhalation or assimilation into any organism,
either directly or indirectly by ingestion through food chains, may, on
the basis of the information available to the Department, cause death,
disease, behavioral abnormalities, cancer, genetic mutations,
physiological malfunctions, including malfunctions in reproduction, or
physical deformation, in such organisms or their offspring.  Toxic
pollutants shall, include but not be limited, to those pollutants
identified pursuant to Section 307 of the Federal Act or Section 4 of
the State Act, or in the case of (sludge use or disposal practices,( any
pollutant identified pursuant to Section 405(d) of the Federal Act.

"TP" means trout production.

"Trout maintenance waters" means waters designated at N.J.A.C.
7:9B-1.15(b) through (g) for the support of trout throughout the year.

"Trout production waters" means waters designated at N.J.A.C.
7:9B-1.15(b) through (g) for use by trout for spawning or nursery
purposes during their first summer.

"Unsaturated zone" means the subsurface volume between the land's
surface and the top of the saturated zone (water table), where moisture
does not fill all the pore spaces in the formation or soil.

"USEPA" means the United States Environmental Protection Agency.

"Wasteload allocation" or "WLA" means the portion of a receiving water's
total maximum daily load for a specific pollutant that is allocated to
one of its existing or future point sources of pollution.  WLAs
constitute a type of water quality-based effluent limitation.

"Water quality-based effluent limitations" means effluent limitations
established so that the quality of the waters receiving a discharge will
meet the surface water quality criteria and policies of this chapter
after the introduction of the effluent.

(Waters of the State( means the ocean and its estuaries, all springs,
streams, wetlands, and bodies of surface or ground water, whether
natural or artificial, within the boundaries of the State of New Jersey
or subject to its jurisdiction.

"Wetlands" means those areas that are inundated or saturated by surface
water or groundwater at a frequency and duration sufficient to support,
and that under normal circumstances do support, a prevalence of
vegetation typically adapted for life in saturated soil conditions,
commonly known as hydrophytic vegetation.  The Department shall evaluate
the parameters of hydrology, soils, and vegetation to determine the
presence and extent of wetlands.

"Zone" means the general surface water classification applied to the
mainstem Delaware River and Delaware Bay.

7:9B-1.5  Statements of policy

(a)	General policies are as follows:

1.	These Surface Water Quality Standards apply to all surface waters of
the State.

2.	Water is vital to life and comprises an invaluable natural resource
which is not to be abused by any segment of the State's population or
economy.  It is the policy of the State to restore, maintain and enhance
the chemical, physical and biological  integrity of its waters, to
protect the public health, to safeguard the aquatic biota, protect
scenic and ecological values, and to enhance the domestic, municipal,
recreational, industrial, agricultural and other reasonable uses of the
State's waters.

3.	The restoration, maintenance and preservation of the quality of the
waters of the State for the protection and preservation of public water
supplies is a paramount interest of the citizens of New Jersey.  In
order to provide adequate, clean supplies of potable water, it is the
policy of the State that all fresh waters be protected as potential
sources of public water supply.  Therefore, point and nonpoint sources
of pollutants shall be regulated to attain compliance with the Surface
Water Quality Standards human health criteria outside of regulatory
mixing zones.

4.	Toxic substances in waters of the State shall not be at levels that
are toxic to humans or the aquatic biota, or that bioaccumulate in the
aquatic biota so as to render them unfit for human consumption.

5.	The introduction of carcinogenic, mutagenic, or teratogenic
substances into the environment is of particular concern to the
Department.  Human health-based ambient criteria have been established
for carcinogenic substances at levels which would result in no greater
than a one-in-one-million lifetime excess cancer risk for Group A and B
carcinogens, under exposure assumptions appropriate for the designated
uses of the waterbody.  Criteria for Group C carcinogens, for which
reference doses are not available, have been established at levels which
would result in no greater than a one-in-one-hundred thousand lifetime
excess cancer risk.

6.	Existing uses shall be maintained and protected.  Designated uses
shall, as soon as technically and economically feasible, be attained
wherever these uses are not precluded by natural conditions.  Where
existing criteria are inadequate to support the existing or designated
uses, the criteria shall be changed to support the existing uses.

7.	The restoration of saline waters to levels which permit unrestricted
shellfish harvesting is an objective of the Department.



(b)	Interstate waters policies are as follows:

1.	The designated uses and water quality criteria for the fresh and
saline waters under the jurisdiction of the Delaware River Basin
Commission shall be as established in accordance with N.J.A.C.
7:9B-1.13, 1.14(c), and 1.14(d).

2.	The designated uses and water quality criteria for waters under the
jurisdiction of the Interstate Sanitation Commission in the New
Jersey/New York metropolitan area shall be as established in this
subchapter, or in accordance with the prevailing Water Quality
Regulations of the Interstate Sanitation Commission, including all
amendments and future supplements thereto, whichever are more stringent.

(c)	General technical policies are as follows:

1.	The natural water quality shall be used in place of the promulgated
water quality criteria of N.J.A.C. 7:9B-1.14 for all water quality
characteristics that do not meet the promulgated water quality criteria
as a result of natural causes.

Water quality criteria are expected to be maintained during periods when
nontidal or small tidal stream flows are at or greater than the
appropriate design flow.  For carcinogenic effect-based human health
criteria, toxic substances with a bioaccumulation or bioconcentration
factor greater than 200 Liters/kilogram (L/kg) (as listed at 1.5(c)2i
below) and for bromodichloromethane (BDCM), the design flow shall be the
flow which is exceeded 75% of the time for the appropriate (period of
record( as determined by the United States Geological Survey (USGS). 
For acute aquatic life protection criteria, the design flow shall be the
MA1CD10 flow.  For chronic aquatic life protection criteria for ammonia,
the design flow shall be the MA30CD10 flow.  The design flow for all
other criteria shall be the MA7CD10 flow.

Toxic substances having carcinogenic effect-based human health criteria
and with a bioaccumulation or bioconcentration factor greater than 200
L/kg are as follows:

(1)	Aldrin;

(2)	Chlordane;

(3)	4,4'-DDD (p,p'-TDE);

(4)	4,4'-DDE;

(5)	4,4'-DDT;

(6)	3,3'-Dichlorobenzidene;

(7)	Dieldrin;

(8)	Heptachlor;

(9)	Heptachlor epoxide;

(10)	Hexachlorobenzene;

(11)	Polychlorinated biphenyls (PCBs);

(12)	2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD); and

(13)	Toxaphene.

3.	Water quality criteria are expected to be maintained in intermittent
streams during all natural flow conditions.  When an intermittent stream
does not contain natural flow of sufficient magnitude to determine water
quality, the criteria to be maintained in the intermittent stream will
be those pertaining to the measurable natural flow immediately
downstream of the intermittent stream.

4.	All analytical data to be incorporated by the Department in water
quality monitoring or other activities shall be from laboratories
approved or certified by the Department for the analysis of those
specific parameters.  If certification is not offered for the specific
parameter, the laboratory performing the analysis shall, at a minimum,
hold certification in the category of certification covering that type
of parameter.

The Department shall utilize the parameter specific criteria contained
in N.J.A.C. 7:9B-1.14 in the development of chemical specific water
quality-based effluent limitations for point source discharges. 
Whenever parameter specific criteria have not been adopted, the
Department will utilize the best available scientific information in the
development of chemical specific water quality-based effluent
limitations for point source discharges.  Ambient criteria published by
the United States Environmental Protection Agency pursuant to section
304(a) of the Federal Clean Water Act represent the minimum acceptable
best scientific information to be used in the development of water
quality-based effluent limitations for point source discharges.

6.	Unless a metal translator is developed based on a site-specific water
quality study or approved by USEPA as part of a watershed study or TMDL,
the following metal translators shall be used for developing effluent
limitations or expressing aquatic life criteria in the equivalent total
recoverable form:

 ADVANCE \d6 

	 ADVANCE \d6 

Name of the Metal	 ADVANCE \d6 Freshwater Acute	 ADVANCE \d6 Freshwater
Chronic	 ADVANCE \d6 Saline Acute	 ADVANCE \d6 Saline Chronic

 ADVANCE \d6 

i.	 ADVANCE \d6 Arsenic	 ADVANCE \d6 

1.0	 ADVANCE \d6 1.0	 ADVANCE \d6 1.0	 ADVANCE \d6 1.0

 ADVANCE \d6 

ii.	 ADVANCE \d6 Cadmium	 ADVANCE \d6 

0.944*	 ADVANCE \d6 0.909*	 ADVANCE \d6 0.994	 ADVANCE \d6 0.994

 ADVANCE \d6 

iii.	 ADVANCE \d6 Chromium III	 ADVANCE \d6 

0.316	 ADVANCE \d6 0.860	 ADVANCE \d6 N/A	 ADVANCE \d6 N/A

 ADVANCE \d6 

iv.	 ADVANCE \d6 Chromium VI	 ADVANCE \d6 

0.982	 ADVANCE \d6 0.962	 ADVANCE \d6 0.993	 ADVANCE \d6 0.993

 ADVANCE \d6 

v.	 ADVANCE \d6 Copper	 ADVANCE \d6 

0.960	 ADVANCE \d6 0.960	 ADVANCE \d6 0.83	 ADVANCE \d6 0.83

 ADVANCE \d6 

vi.	 ADVANCE \d6 Lead	 ADVANCE \d6 

0.791*	 ADVANCE \d6 0.791*	 ADVANCE \d6 0.951	 ADVANCE \d6 0.951

 ADVANCE \d6 

vii.	 ADVANCE \d6 Mercury	 ADVANCE \d6 

0.85	 ADVANCE \d6 N/A	 ADVANCE \d6 0.85	 ADVANCE \d6 N/A

 ADVANCE \d6 

viii.	 ADVANCE \d6 Nickel	 ADVANCE \d6 

0.998	 ADVANCE \d6 0.997	 ADVANCE \d6 0.990	 ADVANCE \d6 0.990

 ADVANCE \d6 

ix.	 ADVANCE \d6 Selenium	 ADVANCE \d6 

N/A	 ADVANCE \d6 N/A	 ADVANCE \d6 0.998	 ADVANCE \d6 0.998

 ADVANCE \d6 

x.	 ADVANCE \d6 Silver	 ADVANCE \d6 

0.85	 ADVANCE \d6 N/A	 ADVANCE \d6 0.85	 ADVANCE \d6 N/A

 ADVANCE \d6 

xi.	 ADVANCE \d6 Zinc	 ADVANCE \d6 

0.978	 ADVANCE \d6 0.986	 ADVANCE \d6 0.946	 ADVANCE \d6 0.946

 ADVANCE \d6 *	Conversion factors for cadmium and lead are hardness
dependent.  Values shown are at a hardness of 100 mg/L of calcium
carbonate.

 ADVANCE \d6 Cadmium Acute Metal Translator =
1.136672-[ln(hardness)(0.041838)]

 ADVANCE \d6 Cadmium Chronic Metal Translator =
1.101672-[ln(hardness)(0.041838)]

 ADVANCE \d6 Lead Acute and Chronic Metal Translator =
1.46203-[ln(hardness)(0.145712)]

 ADVANCE \d6 N/A	not applicable

(d)	Antidegradation policies are as follows:

1.	These antidegradation policies apply to all surface waters of the
State.

2.	Existing uses shall be maintained and protected.  Designated uses
shall be maintained or, as soon as technically and economically
feasible, be attained wherever these uses are not precluded by natural
conditions.

3.	No irreversible changes may be made to existing water quality that
would impair or preclude attainment of the designated uses of a
waterway.

4.	No changes shall be allowed in waters which constitute an outstanding
National or State resource or in waters that may affect these
outstanding resource waters.

5.	Where water quality exceeds levels necessary to support the
designated uses, including but not limited to, propagation of fish,
shellfish, and wildlife and recreation in and on the water, that quality
shall be maintained and protected unless the Department finds, after
full satisfaction of the intergovernmental coordination and public
participation provisions of the Department's continuing planning process
as set forth in the Statewide Water Quality Management Plan (see
N.J.A.C. 7:15), which includes, but is not limited to, the NJPDES
Regulations (N.J.A.C. 7:14A), that allowing lower water quality is
necessary to accommodate important economic or social development in the
area in which the waters are located.

6.	These antidegradation policies shall be applied as follows:

i.	The quality of Nondegradation waters shall be maintained in their
natural state (set aside for posterity) and shall not be subject to any
manmade wastewater discharges.  The Department shall not approve any
activity which, alone or in combination with any other activities, might
cause changes, other than toward natural water quality, in the existing
surface water quality characteristics.

ii.	For Pinelands waters, the Department shall not approve any activity
which alone or in combination with any other activities, might cause
changes, other than toward natural water quality, in the existing
surface water quality characteristics.  This policy shall apply as
follows:

(1)	This policy is not intended to interfere with water control in the
operation of cranberry bogs or blueberry production.

(2)	Dischargers holding valid NJPDES permits as of May 20, 1985, shall
be allowed to continue discharging under the terms of their existing
NJPDES permits provided that the discharge is not creating any water
quality problems and that the designated uses are being attained.  If a
water quality problem has been created or the designated uses are not
being attained, the NJPDES permit shall be modified to eliminate the
water quality problem or attain the designated uses.

(3)	Existing dischargers shall be subject to all the provisions of this
subchapter when they apply for modification or expansion of their
existing discharge.

iii.	Category One Waters shall be protected from any measurable changes
(including calculable or predicted changes) to the existing water
quality.  Water quality characteristics that are generally worse than
the water quality criteria, except as due to natural conditions, shall
be improved to maintain or provide for the designated uses where this
can be accomplished without adverse impacts on organisms, communities or
ecosystems of concern.

iv.	For Category Two Waters, water quality characteristics that are
generally better than, or equal to, the water quality standards shall be
maintained within a range of quality that shall protect the
existing/designated uses, as determined by studies acceptable to the
Department, relating existing/designated uses to water quality.  Where
such studies are not available or are inconclusive, water quality shall
be protected from changes that might be detrimental to the attainment of
the designated uses or maintenance of the existing uses.  Water quality
characteristics that are generally worse than the water quality criteria
shall be improved to meet the water quality criteria.

7.	Where a lower classification of water (including the different
antidegradation waters) may impinge upon a higher classification of
water the Department shall ensure that the quality and uses of the
higher classification water are protected.

8.	A waterway or waterbody from which raw water is transferred to
another waterway or waterbody shall be treated as a tributary to the
waterway or waterbody receiving the transferred water.

9.	Modifications of water quality-based effluent limitations established
to implement this antidegradation policy may be granted pursuant to
N.J.A.C. 7:9B-1.8 and 1.9.

(e)	Water quality-based effluent limitation policies are as follows:

1.	Water quality-based effluent limitations may be established so as to
minimize total expenditures, subject to social and environmental
constraints, so that the provisions of the water quality standards
(which includes the antidegradation policies) are met.  This policy may
result in the assignment of different levels of treatment to different
dischargers where this proves more beneficial on a study area basis.

2.	Modifications of water quality-based effluent limitations established
to implement the water quality standards (which includes the
antidegradation policies) granted pursuant to N.J.A.C. 7:9B-1.8 and 1.9
, shall provide for effluent limits at least as stringent as those
required pursuant to sections 301, 306, and 307 of the Federal Clean
Water Act or the minimum BOD5 effluent standards at N.J.A.C. 7:14A-12.4,
where applicable, whichever are more stringent.

3.	Water quality-based effluent limitations developed in accordance with
N.J.A.C. 7:14A-13.6 shall not interfere with the attainment of the
Surface Water Quality Standards, including the antidegradation policies.

4.	When a discharge is made to a tidal waterway in the reach where the
salinity varies from less than 3.5 ppt. to greater than 3.5 ppt., or the
salinity data are inconclusive, the Department shall establish as water
quality-based effluent limitations the more stringent of the
limitations, on a parameter specific basis, required for the upstream,
FW, waters or the downstream, SE, waters.

5.	Where the effluent limitations developed pursuant to N.J.A.C.
7:14A-13.6 are below the level of detectability of the procedures in
N.J.A.C. 7:18 the Department will use an effluent limitation of
nondetectable in any NJPDES permit.

6.	Compliance schedules may be issued in accordance with N.J.A.C.
7:14A-6.4 when it is demonstrated by a discharger that new or revised
water quality-based effluent limitations, based on ambient criteria
adopted or revised after July 1, 1977, cannot be consistently met with
the facility's existing treatment process.  No schedule of compliance
may be allowed for parameter specific water quality-based effluent
limitations where the parameter specific ambient water quality
criterion, which was the basis for developing that limitation, was
adopted prior to July 1, 1977, and has not been revised since adoption.

(f)	Bioassay and biomonitoring policies are as follows:

1.	Bioassay test species selection criteria follow:

i.	The objective of the Department is to use test species for toxicity
testing bioassays that are representative of the more sensitive aquatic
biota from the different trophic levels of the waters in question.

ii.	Test species need not be indigenous to, nor occur in the waters in
question.

iii.	When the bioassay test protocol being utilized falls under the
scope of N.J.A.C. 7:18 the Department shall designate the approved
representative species considered to be the most sensitive to the
discharge.

2.	Acute definitive bioassay tests, in accordance with N.J.A.C. 7:18,
will normally be utilized in determining the toxicity of a discharge to
the aquatic biota.

3.	The Department, in order to further characterize the toxicity of a
discharge, may allow or require the use of other procedures including,
but not limited to:

i.	Bioaccumulation testing;

ii.	Mutagenicity testing; and

iii.	Measures of the structure and function of the aquatic community in
the receiving waters.

4.	Parameter specific water quality criteria for toxic substances in a
waterbody may be established by the Department when adequate data, from
appropriate bioassays or scientific literature, are available as
follows:

i.	Appropriate bioassays, for purposes of this policy, shall include
both acute definitive and chronic definitive bioassays; and

ii.	The amount of bioassay data or scientific literature needed to
support adoption of a parameter specific criterion in a given waterbody
will be determined by the Department on a case-by-case basis.

(g)	Nutrient policies are as follows:

1.	These policies apply to all FW waters of the State.

2.	Except as due to natural conditions, nutrients shall not be allowed
in concentrations that cause objectionable algal densities, nuisance
aquatic vegetation, abnormal diurnal fluctuations in dissolved oxygen or
pH, changes to the composition of aquatic ecosystems, or otherwise
render the waters unsuitable for the designated uses.

3.	The Department may establish watershed or site-specific water quality
criteria for nutrients in lakes, ponds, reservoirs or streams, in
addition to or in place of the criteria in N.J.A.C. 7:9B-1.14, when
necessary to protect existing or designated uses.  Such criteria shall
become part of these Water Quality Standards.

4.	The Department shall establish water quality-based effluent limits
for nutrients, in addition to or more stringent than, the effluent
standard in N.J.A.C. 7:9-5.7, as necessary to meet the quality criteria.

5.	Activities resulting in the non-point discharge of nutrients shall
implement the best management practices determined by the Department to
be necessary to protect the existing or designated uses.

6.	The Department may allow or require the use of algal biostimulation
assays, to determine the limiting nutrient in a lake, pond, reservoir or
stream.

 ADVANCE \d6  ADVANCE \u6 (h)	A permittee may request that a regulatory
mixing zone be established by the Department for applicable criteria
except as otherwise provided in this section.  Regulatory mixing zones
may be evaluated as part of the development of water quality-based
effluent limitation(s) to provide for the initial dispersion of the
effluent in the receiving water body at or near the discharge point.

1.	The following are the general conditions for establishing regulatory
mixing zones:

Regulatory mixing zones shall be established in accordance with this
subsection;

Water quality criteria may be exceeded within the regulatory mixing
zone; however, surface water quality criteria must be met at the edge of
the regulatory mixing zone;

The regulatory mixing zone shall be no larger than that portion of the
receiving water where complete mixing occurs;

Regulatory mixing zones shall not be used for, or considered as a
substitute for, minimum treatment technology required by the Federal and
State Acts or other applicable Federal or State laws or regulations;

Regulatory mixing zones shall be established to assure that significant
mortality does not occur to free swimming or drifting organisms;

In individual regulatory mixing zones, discharges which meet acute
effluent toxicity of LC ADVANCE \d3 50 ADVANCE \u3  ( 50% shall be
deemed to comply with this requirement.

In cases of extended regulatory mixing zones resulting from multiple,
conjoined individual regulatory mixing zones, site-specific studies to
demonstrate no significant mortality shall be required, taking into
account factors including, time of travel, concentration, and the
toxicity of the parameters in question;

The existing and designated uses outside the regulatory mixing zone
shall not be adversely affected;

The total area and volume of a waterbody assigned to a regulatory mixing
zone shall be limited to that which will not adversely affect beneficial
uses or interfere with biological communities or populations of
important species (for example, commercially or recreationally
significant species; or threatened or endangered species);

Regulatory mixing zones, including those for shore hugging plumes,
shall not extend into recreational areas, potable surface water intakes
(1500 feet upstream and 500 feet downstream or to the farthest point of
backwatering due to the intake, whichever is more protective), shellfish
harvesting areas, threatened or endangered species habitat, and other
important biological or natural resource areas;

The regulatory mixing zone shall not inhibit or impede the passage of
aquatic biota; and

Overlapping regulatory mixing zones shall not inhibit or impede the
passage of aquatic biota.

Spatial limitations for regulatory mixing zones delineate the maximum
area in which the initial mixing may occur.  A site-specific study
performed in accordance with (h)3 below will be used to determine
dilution in tidal water bodies and in nontidal water bodies where mixing
is not shown to be rapid and complete.  A maximum area shall be applied
in any one of the following four situations:

Heat dissipation areas as provided at N.J.A.C. 7:9B-1.14(c)11.ii or a
variance issued pursuant to Section 316(a) of the Clean Water Act, 33
U.S.C. 1326(a).

For discharges to tidal water bodies:

Regulatory mixing zones for chronic and human health criteria are
limited to one fourth of the distance between the discharge port closest
to the shoreline and the shoreline during average tidal conditions, or
100 meters, whichever is greater; and

Regulatory mixing zones for acute criteria are limited by the distances
calculated in accordance with the USEPA (Technical Support Document For
Water Quality-Based Toxics Control( USEPA, EPA/505/2-90-001, March 1991,
incorporated herein by reference.  In no case shall a regulatory mixing
zone for acute criteria extend more than 100 meters from the discharge
point or include more than five percent of the total surface area of a
water body based on critical ambient tidal conditions during low slack,
astronomical spring tide for the applicable exposure period.

For discharges to non-tidal water bodies:

(1)	Regulatory mixing zones for chronic and human health criteria shall
be based on the design flows at (c)2 above.  If rapid, complete mix is
demonstrated, the entire available design flow may be used in dilution
calculations.  If rapid, complete mix is not demonstrated, only that
portion of the design flow that can be demonstrated to mix with the
effluent within 100 meters from the discharge point may be used in
dilution calculations; and

(2)	Regulatory mixing zones for acute criteria shall be based on the
MA1CD10 design flow.  If rapid, complete mix is demonstrated, the entire
available design flow may be used in dilution calculations.  If rapid,
complete mix is not demonstrated, only that portion of the design flow
that can be demonstrated to mix with the effluent within a downstream
distance calculated in accordance with the USEPA (Technical Support
Document For Water Quality-Based Toxics Control( USEPA,
EPA/505/2-90-001, March 1991 may be used. In no case shall a regulatory
mixing zone for acute criteria extend more than 100 meters from the
discharge point or include more than five percent of the total surface
area of a water body based on the design flow.

Site-specific spatial dimensions of the regulatory mixing zone for an
approved multiport diffuser shall be determined by the Department.  The
dimensions of the site-specific regulatory mixing zone and the allowable
dilution at the edge of the regulatory mixing zone may be established
using appropriate diffuser models (for example, CORMIX, PLUMES), tracer
studies, or other field studies approved by the Department in accordance
with (h)3 below.

A regulatory mixing zone study shall be conducted in accordance with a
workplan pre-approved by the Department.  General protocols for
conducting mixing zone studies are described in the USEPA (Technical
Support Document For Water Quality-Based Toxics Control( USEPA,
EPA/505/2-90-001, March 1991.  In addition, the following principles
apply:

i.	The design flows to be used in calculating available dilution in
nontidal waters shall be based on the design flows specified at (c)2
above; and

ii.	In tidal waters, the regulatory mixing zone for an acute criteria
shall be based on critical ambient tidal conditions during low slack,
astronomical spring tide for the applicable exposure period.  Regulatory
mixing zones for chronic and human health criteria shall be based on
average conditions during a normal tidal cycle.

In order to determine waste load allocations and NJPDES/DSW permit
effluent limitations that will comply with the regulatory mixing zone
requirements, instream pollutant concentrations at the boundary of the
regulatory mixing zone shall be determined as follows:

The instream concentrations shall be determined using either a general
mass balance equation or a mathematical model, if available; or the
information generated during the course of a study as described at (h)2
above.

If the regulatory mixing zone is based upon the guidance and procedures
in the USEPA (Technical Support Document For Water Quality-Based Toxics
Control( USEPA, EPA/505/2-90-001, March 1991, the Technical Support
Document will also be used to determine instream concentrations at the
boundary of the regulatory mixing zone.

5.	Regulatory mixing zones are prohibited as follows:

For indicators of pathogenic quality, including fecal coliform and
enterococci;

In intermittent streams;

For new or increased discharges to lakes, ponds, and reservoirs;

For discharges to areas of waters with documented occurrences of any
threatened or endangered species listed pursuant to the Federal or State
Threatened and Endangered Species Acts (Endangered Species Act of 1973,
16 U.S.C. 1531 et seq.; New Jersey Endangered and Non Game Species
Conservation Act of 1973, N.J.S.A. 23:2A-1 et seq.; Endangered Plant
Species List Act, N.J.S.A. 13:1B-15.151 et seq.), if those discharges
would likely have an adverse effect on the species or its associated
habitat;

For heat dissipation areas in FW2-TP waters;

For heat dissipation areas within 1500 feet of the shoreline in SC
waters;

For new discharges of the following pollutants:

(1)	alpha-BHC (alpha-HCH),

(2)	beta-BHC (beta-HCH),

(3)	gamma-BHC (gamma HCH / Lindane),

(4)	Chlordane,

(5)	4,4'-DDD (p,p'-TDE),

(6)	4,4'-DDE,

(7)	4,4'-DDT,

(8)	Dieldrin,

(9)	Hexachlorobenzene,

(10)	Hexachlorobutadiene,

(11)	Mercury,

(12)	Mirex,

(13)	Pentachlorobenzene,

(14)	Polychlorinated biphenyls (PCBs),

(15)	1,2,4,5-Tetrachlorobenzene,

(16)	2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD), and

Toxaphene; and

For new or expanded discharges, within 1500 feet upstream of a potable
surface water intake (including any reservoir) and 500 feet downstream
or to the farthest point of backwatering due to the intake, whichever is
more protective.

7:9B-1.6  Establishment of water quality-based effluent limitations

(a)	For Category One waters, as defined in N.J.A.C. 7:9B-1.4, water
quality-based effluent limitations shall be assigned to a point source
discharge so as to protect the existing water quality from any
measurable or calculable changes.  The Department shall establish water
quality-based effluent limitations, as appropriate, for those parameters
contained in N.J.A.C. 7:9B-1.14, as well as any other parameters the
Department believes may have a detrimental effect on the designated or
existing uses.

(b)	For Category Two waters, as defined in N.J.A.C. 7:9B-1.4, draft
water quality-based effluent limitations shall be assigned to a point
source discharge so as to:

1.	Maintain water quality characteristics that are generally better than
or equal to the water quality standards at a level that will protect the
existing and designated uses; and

2.	Bring water quality characteristics that are generally worse than the
water quality criteria, except as due to natural conditions, up to the
water quality criteria or to levels corresponding with wasteload
allocations established pursuant to N.J.A.C. 7:15-7.6.

(c).	Water quality-based effluent limits for chlorine produced oxidants
based on the criteria in N.J.A.C. 7:9B-1.14(c)14 are not applicable
where:

i.	The aquatic community of a waterbody is exposed to one or more point
source discharges of non-contact cooling water that is intermittently
chlorinated to control condenser biofouling;

ii.	The total period of such exposure to chlorinated wastewater is two
hours per day or less; and

iii.	The maximum concentration of chlorine produced oxidants in the
effluents of such discharges shall not exceed 200 ug/L.

7:9B-1.7  Waterway loadings in areawide water quality management plans

Any total maximum daily load, wasteload allocation, or load allocation
established as an amendment to an areawide water quality management plan
under N.J.A.C. 7:15-3.4 shall be consistent with all of the provisions
of this subchapter.

7:9B-1.8  Procedures for modifying water quality-based effluent
limitations for individual dischargers to Category One waters

(a)	An applicant requesting modification of a water quality-based
effluent limitation, established on a case-by-case basis, must
demonstrate, to the satisfaction of the Department, after public notice
(including notice to affected municipalities) and a public hearing
(where sufficient public interest exists), that:

1.	Some change in ambient water quality should be allowed because of
necessary and justifiable social or economic development;

2.	Alternative effluent limitations, at least as stringent as the
technology-based effluent limitations required by either sections 301,
306, and 307 of the Federal Clean Water Act, or the effluent limitations
resulting from application of the minimum BOD5 effluent standards in
N.J.A.C. 7:14A-12.4 (where applicable), whichever are more stringent,
will not interfere nor be injurious to the existing or designated uses;
and

3.	Where the requested modified effluent limitations would result in
contravention of the water quality criteria or the degradation of the
natural water quality, whichever is less stringent:

i.	The water quality criteria are not attainable because of natural
background; or

ii.	The water quality criteria are not attainable because of
irretrievable man-induced conditions; or

iii.	Natural, ephemeral, intermittent, or low flow conditions or water
levels prevent the attainment of the use, unless these conditions may be
compensated for by the discharge of sufficient volume of effluent
discharges without violating State water conservation requirements to
enable uses to be met; or

iv.	Controls more stringent than those required by Sections 301(b) and
306 of the Federal Clean Water Act would result in substantial and
widespread adverse social and economic impact.



(b)	It is the responsibility of the applicant to provide the Department
with all the information needed to evaluate the requested
modification(s).

(c)	In no case shall changes to water quality be allowed in Outstanding
National Resource Waters.

(d)	Modified effluent limitations may be granted for a time period not
to exceed three years or the time period of the permit in which the
modified effluent limitations appear, whichever is shorter.

(e)	Modified effluent limitations may be renewed if the discharger
demonstrates, to the Department's satisfaction, after public notice
(including notice to affected municipalities) and a public hearing
(where sufficient interest exists), that the basis for issuing the
modification still exists and there have been no adverse impacts on the
existing uses.

(f)	Where water quality criteria are not currently met the Department
shall not grant a modification, as set forth in this section,
establishing an effluent limitation less stringent than the
limitation(s) in the existing permit, unless the criteria are not met
because of natural conditions.

7:9B-1.9  Procedures for modifying water quality-based effluent
limitations for individual dischargers to Category Two waters.

(a)	The criteria for modifying water quality-based effluent limitations
established on a case-by-case basis are:

1.	The applicant for modification of effluent limitations for parameters
that are currently better than the water quality criteria must
demonstrate, to the satisfaction of the Department, after public notice
(including notice to affected municipalities) and a public hearing
(where sufficient public interest exists), that:

i.	Some degradation of water quality parameters currently better than
the water quality criteria should be allowed because of necessary and
justifiable social or economic development; and

ii.	Alternative effluent limitations, at least as stringent as the
technology-based effluent limitations required by either sections 301,
306, and 307 of the Federal Clean Water Act, or the effluent limitations
resulting from application of the effluent standards (where applicable)
in N.J.A.C. 7:14A-12, whichever are more stringent, will not interfere
with nor be injurious to the existing or designated uses.

2.	The applicant for modification of effluent limitations for
parameters that are currently equal to or currently do not meet the
water quality criteria in this subchapter must demonstrate, to the
satisfaction of the Department, after public notice (including notice to
affected municipalities) and a public hearing (where sufficient public
interest exists), that:

i.	The water quality criteria are not attainable because of natural
background; or

ii.	The water quality criteria are not attainable because of
irretrievable man-induced conditions; or

iii.	Natural, ephemeral, intermittent, or low flow conditions or water
levels prevent the attainment of the water quality criteria, unless
these conditions may be compensated for by the discharge of sufficient
volume of effluent discharges without violating State water conservation
requirements to enable uses to be met; or

iv.	Controls more stringent than those required by Section 301(b) and
306 of the Federal Clean Water Act would result in substantial and
widespread adverse social and economic impact.

(b)	Where water quality criteria are not currently met the Department
shall not grant a modification, as set forth in this section,
establishing an effluent limitation less stringent than the
limitation(s) in the existing permit, unless the criteria are not met
because of natural conditions.

(c)	Modified effluent limitations may be granted for a time period not
to exceed three years or the time period of the permit in which the
modified effluent limitations appear, whichever is shorter.

(d)	Modified effluent limitations may be renewed if the discharger
demonstrates, to the satisfaction of the Department, after public notice
(including notice to affected municipalities) and a public hearing
(where sufficient interest exists), that the basis for issuing the
modification still exists and there have been no adverse impacts on the
existing uses.

7:9B-1.10  Procedures for reclassifying specific segments for less
restrictive uses

(a)	The Department will entertain petitions, for reclassification of
specific segments to less restrictive uses, or may decide to initiate
reclassification proceedings on its own, at any time.

(b)	Any reclassification proceedings will include full documentation of
the items contained in (d) and (e) below.  The documentation will be
prepared by either the Department (where the Department has initiated
the reclassification on its own) or the petitioner for the
reclassification.

(c)	The Department shall issue public notice to all interested parties
(including affected municipalities) and shall hold public hearing(s) as
part of any reclassification proceeding.

(d)	The Department or the petitioner, as indicated in (b) above, shall
include in the reclassification documentation appropriate water quality
studies and analyses, biological studies and analyses, environmental,
social, and economic studies as are necessary to demonstrate the
satisfaction of (e) 1 and 2 below, in addition to at least one of the
remaining criteria in (e) below.

(e)	The Department may establish less restrictive uses than the
designated uses only after it has been demonstrated to the satisfaction
of the Department that:

1.	None of the uses being removed are existing uses; and

2.	The uses to be removed will not be attained by implementing effluent
limits required by Sections 301(b) and 306 of the Federal Clean Water
Act in conjunction with implementation of cost-effective and reasonable
best management requirements for nonpoint source pollution control; and

3.	The existing designated use is not attainable because of natural
background; or

4.	The existing designated use is not attainable because of
irretrievable man-induced conditions; or

5.	Natural, ephemeral, intermittent, or low flow conditions or water
levels prevent the attainment of the use, unless these conditions may be
compensated for by the discharge of sufficient volume of effluent
discharges without violating State water conservation  requirements to
enable uses to be met; or

6.	Physical conditions related to the natural features of the water
body, such as the lack of a proper substrate, cover, flow, depth, pools,
riffles, and the like, unrelated to water quality, preclude attainment
of aquatic life protection uses; or

7.	Controls more stringent than those required by Sections 301(b) and
306 of the Federal Clean Water Act would result in substantial and
widespread adverse social and economic impact.

(f)	Any reclassification for less restrictive uses, established
pursuant to this section shall be reviewed during each review of water
quality standards pursuant to Section 303 of the Federal Clean Water Act
(at least once every three years).  Either the Department or the
original petitioner, as indicated in (b) above, shall be responsible for
supplying documentation showing that the bases for the reclassification
still exist.

(g)	In those cases in which a thermal discharge is involved, the
procedures for reclassifying segments for less restrictive use shall be
consistent with section 316 of the Federal Clean Water Act.

7:9B-1.11  Procedures for reclassifying specific segments for more
restrictive uses

(a)	The Department will entertain petitions, for reclassification of
specific segments, pursuant to (e) below, or may decide to initiate
reclassification proceedings on its own, at any time.

(b)	The Department may entertain petitions for reclassification of
specific segments, pursuant to (f) below, at any time.

(c)	Documentation supporting the petition for reclassification for more
restrictive use(s) shall be prepared by the petitioner for such
reclassification, where one exists, or by the Department, where it
decides to initiate such reclassification on its own.

(d)	The Department shall issue public notice to all interested parties
(including affected municipalities and dischargers) and shall hold
public hearing(s) as part of any reclassification proceeding.

(e)	A reclassification for more restrictive uses shall be made whenever:

1.	It is demonstrated to the satisfaction of the Department that there
are existing uses of the specific segment that are not included in the
designated uses; or

2.	Where a reclassification for less restrictive uses has been granted
pursuant to N.J.A.C. 7:9B-1.10, the bases for the reclassification no
longer exist; or

3.	It is demonstrated to the satisfaction of the Department that any
uses in Section 101 (a) (2) of the Federal Clean Water Act, protection
and propagation of fish, shellfish, and wildlife, and recreation in and
on the water, which are not included in the designated uses listed in
this subchapter are attainable.

(f)	A reclassification for more restrictive uses may be made when:

1.	It is demonstrated to the satisfaction of the Department that the
waters should be set aside to represent the natural aquatic environment
and its associated biota; or

2.	It is demonstrated to the satisfaction of the Department that a more
restrictive use is necessary to protect a unique ecological system or
threatened/endangered species.

(g)	In those cases in which a thermal discharge is involved, the
procedures for reclassifying segments for more restrictive uses shall be
consistent with section 316 of the Federal Clean Water Act.



7:9B-1.12  Designated uses of FW1, PL, FW2, SE1, SE2, SE3, and SC waters

(a)	In all FW1 waters the designated uses are:

 ADVANCE \d6 1.	Set aside for posterity to represent the natural aquatic
environment and its associated biota;

 ADVANCE \d6 2.	Primary and secondary contact recreation;

 ADVANCE \d6 3.	Maintenance, migration and propagation of the natural
and established aquatic biota; and

 ADVANCE \d6 4.	Any other reasonable uses.

(b)	In all PL waters the designated uses are:

 ADVANCE \d6 1.	Cranberry bog water supply and other agricultural uses;

 ADVANCE \d6 2.	Maintenance, migration and propagation of the natural
and established biota indigenous to this unique ecological system;

 ADVANCE \d6 3.	Public potable water supply after conventional
filtration treatment (a series of processes including filtration,
flocculation, coagulation, and sedimentation, resulting in substantial
particulate removal but no consistent removal of chemical constituents)
and disinfection;

 ADVANCE \d6 4.	Primary and secondary contact recreation; and

 ADVANCE \d6 5.	Any other reasonable uses.

(c)	In all FW2 waters the designated uses are:

 ADVANCE \d6 1.	Maintenance, migration and propagation of the natural
and established biota;

 ADVANCE \d6 2.	Primary and secondary contact recreation;

 ADVANCE \d6 3.	Industrial and agricultural water supply;

 ADVANCE \d6 4.	Public potable water supply after conventional
filtration treatment (a series of processes including filtration,
flocculation, coagulation, and sedimentation, resulting in substantial
particulate removal but no consistent removal of chemical constituents)
and disinfection; and

 ADVANCE \d6 5.	Any other reasonable uses.

(d)	In all SE1 waters the designated uses are:

 ADVANCE \d6 1.	Shellfish harvesting in accordance with N.J.A.C. 7:12;

 ADVANCE \d6 2.	Maintenance, migration and propagation of the natural
and established biota;

 ADVANCE \d6 3.	Primary and secondary contact recreation; and

 ADVANCE \d6 4.	Any other reasonable uses.

(e)	In all SE2 waters the designated uses are:

 ADVANCE \d6 1.	Maintenance, migration and propagation of the natural
and established biota;

 ADVANCE \d6 2.	Migration of diadromous fish;

 ADVANCE \d6 3.	Maintenance of wildlife;

 ADVANCE \d6 4.	Secondary contact recreation; and

 ADVANCE \d6 5.	Any other reasonable uses.

(f)	In all SE3 waters the designated uses are:

 ADVANCE \d6 1.	Secondary contact recreation;

 ADVANCE \d6 2	Maintenance and migration of fish populations;

 ADVANCE \d6 3	Migration of diadromous fish;

 ADVANCE \d6 4.	Maintenance of wildlife; and

 ADVANCE \d6 5.	Any other reasonable uses.

(g)	In all SC waters the designated uses are:

 ADVANCE \d6 1.	Shellfish harvesting in accordance with N.J.A.C. 7:12;

 ADVANCE \d6 2.	Primary and secondary contact recreation;

 ADVANCE \d6 3.	Maintenance, migration and propagation of the natural
and established biota; and

 ADVANCE \d6 4.	Any other reasonable uses.

7:9B-1.13  Designated uses of mainstem Delaware River and Delaware Bay

(a)	The designated uses for the mainstem Delaware River and Delaware Bay
are those contained in "Delaware River Basin Commission, Water Quality
Regulations, Administrative Manual - Part III," Article 3, dated October
23, 1996, including all amendments and future supplements thereto.

(b)	The designated uses for other waters under the jurisdiction of the
DRBC are as set forth at N.J.A.C. 7:9B-1.15(d).



7:9B-1.14  Surface water quality criteria

(a)	Surface water quality criteria for FW1 waters shall be maintained as
to quality in their natural state.

(b)	Surface water quality criteria for PL waters are as follows:

1.	These waters shall be maintained as to quality in their existing
state or that quality necessary to attain or protect the designated
uses, whichever is more stringent.

i.	For Nitrate-Nitrogen a level of 2 mg/L shall be maintained in the
surface waters unless it is shown that a lower level must be maintained
to protect the existing surface water quality.

ii.	A pH level between 3.5 and 5.5 shall be maintained unless it is
demonstrated that a pH level outside of that range is necessary to
protect the existing/ designated uses.

2.	The water quality criteria for existing discharges are the water
quality criteria contained in "Surface Water Quality Standards" as
adopted in March 1981, except that:

i.	The criteria for Nitrate-Nitrogen and pH promulgated in N.J.A.C.
7:9B-1.14(b)1 for PL waters apply instead of the 1981 criteria, and;

ii.	The criteria for phosphorous and toxic substances promulgated in
N.J.A.C. 7:9B-1.14(c) apply instead of the 1981 criteria, as though the
freshwater portions of the PL waters were classified as FW2 and the
saline portions were classified as SE1.

(c)	Surface Water Quality Criteria for FW2, SE and SC Waters:



 ADVANCE \d12 1.	Bacterial quality (Counts/100 ml)	 ADVANCE \d12 i.
Bacterial Indicators shall not exceed, in all shellfish waters, the
standard for approved shellfish waters as established by the National
Shellfish Sanitation Program as set forth in its current manual of
operations.	 ADVANCE \d12 Shellfish Waters

 ADVANCE \d12 ii.	Fecal Coliforms:

	

 ADVANCE \d12 (1)	Fecal coliform levels shall not exceed a geometric
average of 50/100 ml.	 ADVANCE \d12 Within 1500 feet of shoreline in SC
waters.

 ADVANCE \d12 (2)	Fecal coliform levels shall not exceed a geometric
average of 200/100 ml nor should more than 10 percent of the total
samples taken during any 30-day period exceed 400/100 ml.  	 ADVANCE
\d12 FW2 , SE1, and SC    1500 feet to 3 miles from the shoreline.

 ADVANCE \d12 (3)	Fecal coliform levels shall not exceed a geometric
average of 770/100 ml.  	 ADVANCE \d12 SE2

 ADVANCE \d12 (4)	Fecal coliform levels shall not exceed a geometric
average of 1500/100ml.	 ADVANCE \d12 SE3



 ADVANCE \d12 iii.	Enterococci:

	

 ADVANCE \d12 (1)	Enterococci levels shall not exceed a geometric mean
of 33/100 ml, nor shall any single sample exceed 61/100 ml.	 ADVANCE
\d12 FW2

 ADVANCE \d12 (2)	Enterococci levels shall not exceed a geometric mean
of 35/100 ml, nor shall any single sample exceed 104/100 ml.	 ADVANCE
\d12 SE1 and SC

 ADVANCE \d12 iv.	Samples shall be obtained at sufficient frequencies
and at locations during periods which will permit valid interpretation
of laboratory analyses.  As a guideline and for the purpose of these
regulations, a minimum of five samples as equally spaced over a 30-day
period, as feasible, should be collected; however, the number of
samples, frequencies and locations will be determined by the Department
or other appropriate agency in any particular case.	 ADVANCE \d12 All
Classifications

 ADVANCE \d12 2.	Dissolved oxygen (mg/L)	 ADVANCE \d12 i.	Not less than
7.0 at any time;	 ADVANCE \d12 FW2-TP

 ADVANCE \d12 ii.	24 hour average not less than 6.0.  Not less than 5.0
at any time (see paragraph viii below);	 ADVANCE \d12 FW2-TM

 ADVANCE \d12 iii.	24 hour average not less than 5.0, but not less than
4.0 at any time (see paragraph viii below);	 ADVANCE \d12 FW2-NT (except
as in iv below), SE1

 ADVANCE \d12 iv.	Not less than 4.0 at any time;	 ADVANCE \d12 Tidal
portions of FW2-NT tributaries to the Delaware River, between Rancocas
Creek and Big Timber Creek inclusive.

 ADVANCE \d12 v.	Not less than 5.0 at any time;	 ADVANCE \d12 SC

 ADVANCE \d12 vi.	Not less than 4.0 at any time;	 ADVANCE \d12 SE2

 ADVANCE \d12 vii.	Not less than 3.0 at any time; and	 ADVANCE \d12 SE3

 ADVANCE \d12 viii.	Supersaturated dissolved oxygen values shall be
expressed as their corresponding 100 percent saturation values for
purposes of calculating      24 hour averages.	 ADVANCE \d12 FW2-TM,
FW2-NT, SE1

 ADVANCE \d12 3.	Floating, colloidal, color and settleable solids;
petroleum hydrocarbons and other oils and grease	 ADVANCE \d12 i.	None
noticeable in the water or deposited along the shore or on the aquatic
substrata in quantities detrimental to the natural biota.  None which
would render the waters unsuitable for the designated uses; and	 ADVANCE
\d12 All Classifications

 ADVANCE \d12 ii.	For "Petroleum Hydrocarbons" the goal is none
detectable utilizing the Federal EPA Environmental Monitoring and
Support Laboratory Method (Freon Extractable - Silica Gel Adsorption -
Infrared Measurement); the present criteria, however, are those of
paragraph i above.	 ADVANCE \d12 All Classifications

 ADVANCE \d12 4.	pH (Standard Units)	 ADVANCE \d12 i.	6.5-8.5	 ADVANCE
\d12 FW2, All SE

 ADVANCE \d12 ii.	Natural pH conditions shall prevail.	 ADVANCE \d12 SC

 ADVANCE \d12 5.	Phosphorus, Total (mg/L)	 ADVANCE \d12 i.	Lakes: 
Phosphorus as total P shall not exceed 0.05 in any lake, pond or
reservoir, or in a tributary at the point where it enters such bodies of
water, except where watershed or site-specific criteria are developed
pursuant to N.J.A.C. 7:9B-1.5(g)3.	 ADVANCE \d12 FW2

	 ADVANCE \d12 ii.	Streams:  Except as necessary to satisfy the more
stringent criteria in paragraph i above or where watershed or
site-specific criteria are developed pursuant to N.J.A.C 7:9B-1.5(g)3,
phosphorus as total P shall not exceed 0.1 in any stream, unless it can
be demonstrated that total P is not a limiting nutrient and will not
otherwise render the waters unsuitable for the designated uses.	 ADVANCE
\d12 FW2

 ADVANCE \d12 6.	Radioactivity	 ADVANCE \d12 i.	Prevailing regulations
including all amendments and future supplements thereto adopted by the
U.S. Environmental Protection Agency pursuant to Sections 1412, 1445,
and 1450 of the Public Health Services Act, as amended by the Safe
Drinking Water Act (PL 93-523)	 ADVANCE \d12 All Classifications

 ADVANCE \d12 7.	Solids, Suspended (mg/L) (Non-filterable residue)	
ADVANCE \d12 i.	25.0

ii.	40.0	 ADVANCE \d12 FW2-TP, FW2-TMFW2-NT

 ADVANCE \d12 iii.	None which would render the waters unsuitable for the
designated uses.	 ADVANCE \d12 All SE, SC

 ADVANCE \d12 8.	Solids, Total Dissolved (mg/L) (Filterable Residue)	
ADVANCE \d12 i.	No increase in background which may adversely affect the
survival, growth or propagation of the aquatic biota.  Compliance with
water quality-based WET limitations or LC ADVANCE \d3 50 ADVANCE \u3  (
50%, whichever is more stringent, shall be deemed to meet this
requirement.	 ADVANCE \d12 FW2

	 ADVANCE \d12 ii.	No increase in background which would interfere with
the designated or existing uses, or 500 mg/L, whichever is more
stringent.	 ADVANCE \d12 FW2

	 ADVANCE \d12 iii.	None which would render the water unsuitable for the
designated uses.	 ADVANCE \d12 All SE

 ADVANCE \d12 9.	Sulfate (mg/L)	 ADVANCE \d12 i.	250	 ADVANCE \d12 FW2

 ADVANCE \d12 10.	Taste and odor producing substances	 ADVANCE \d12 i.
None offensive to humans or which would produce offensive taste or odors
in water supplies and biota used for human consumption.  None which
would render the water unsuitable for the designated uses.	 ADVANCE \d12
All Classifications

 ADVANCE \d12 11.	Temperature and Heat Dissipation Areas	 ADVANCE \d12
i.	Thermal Alterations (Temperatures shall be measured outside of heat
dissipation areas)

	

 ADVANCE \d12 (1)	Streams

	

 ADVANCE \d12 (i)	No thermal alterations which would cause changes in
ambient temperatures except where properly treated wastewater effluents
are discharged.  Where such discharges occur, temperatures shall not
deviate more than 0.6 ADVANCE \u3 o ADVANCE \d3 C (1 ADVANCE \u3 o
ADVANCE \d3 F) from ambient temperature.	 ADVANCE \d12 FW2-TP

 ADVANCE \d12 (ii)	No thermal alterations which would cause temperatures
to exceed ambient by more than 1.1 ADVANCE \u3 o ADVANCE \d3 C (2
ADVANCE \u3 o ADVANCE \d3 F) at any time or which would cause
temperatures in excess of 20 ADVANCE \u3 o ADVANCE \d3 C (68 ADVANCE \u3
o ADVANCE \d3 F).	 ADVANCE \d12 FW2-TM

 ADVANCE \d12 (iii)	No thermal deviations which would cause temperatures
to deviate more than 2.8 ADVANCE \u3 o ADVANCE \d3 C (5 ADVANCE \u3 o
ADVANCE \d3 F) at any time from ambient temperatures.  No heat may be
added which would cause temperatures to exceed 27.8 ADVANCE \u3 o
ADVANCE \d3 C (82 ADVANCE \u3 o ADVANCE \d3 F) for small mouth bass or
yellow perch waters, or 30 ADVANCE \u3 o ADVANCE \d3 C (86 ADVANCE \u3 o
ADVANCE \d3 F) for other nontrout waters.	 ADVANCE \d12 FW2-NT

 ADVANCE \d12 (iv)	No thermal alterations which would cause temperatures
to deviate from ambient by more than 2.2 ADVANCE \u3 o ADVANCE \d3 C (4
ADVANCE \u3 o ADVANCE \d3 F), from September through May, nor more than
0.8 ADVANCE \u3 o ADVANCE \d3 C (1.5 ADVANCE \u3 o ADVANCE \d3 F) from
June through August, nor cause temperatures to exceed 29.4 ADVANCE \u3 o
ADVANCE \d3 C (85 ADVANCE \u3 o ADVANCE \d3 F).	 ADVANCE \d12 All SE

	 ADVANCE \d12 (2)	Lakes, Ponds or Reservoirs

	

 ADVANCE \d12 (i)	No thermal alterations except where it can be shown to
be beneficial to the designated and existing uses.	 ADVANCE \d12 FW2-TM,
FW2-TP

 ADVANCE \d12 (ii)	No thermal alterations of more than 1.7 ADVANCE \u3 o
ADVANCE \d3 C (3 ADVANCE \u3 o ADVANCE \d3 F) in the epilimnion of lakes
and other standing waters.  No discharges of heated effluent into the
hypolimnion nor pumping of water from the hypolimnion (for discharge
back into the same water body) shall be permitted unless it is
demonstrated, to the satisfaction of the Department, that such practices
will be beneficial to the existing and designated uses.	 ADVANCE \d12
FW2-NT

 ADVANCE \d12 (3)	Saline Bays - No thermal alterations which would
cause temperatures to deviate from ambient by more than 2.2 ADVANCE \u3
o ADVANCE \d3 C (4 ADVANCE \u3 o ADVANCE \d3 F), from September through
May, nor more than 0.8 ADVANCE \u3 o ADVANCE \d3 C (1.5 ADVANCE \u3 o
ADVANCE \d3 F) from June through August, nor cause temperatures to
exceed 29.4 ADVANCE \u3 o ADVANCE \d3 C (85 ADVANCE \u3 o ADVANCE \d3
F).	 ADVANCE \d12 All SE

 ADVANCE \d12 (4)	Coastal Waters - No direct heat additions within 1500
feet of the shoreline.  No thermal alterations which would cause
temperatures to deviate from ambient temperatures by more than 2.2
ADVANCE \u3 o ADVANCE \d3 C (4 ADVANCE \u3 o ADVANCE \d3 F) from
September through May, nor more than 0.8 ADVANCE \u3 o ADVANCE \d3 C
(1.5 ADVANCE \u3 o ADVANCE \d3 F) from June through August, nor which
would cause temperatures to exceed 26.7 ADVANCE \u3 o ADVANCE \d3 C (80
ADVANCE \u3 o ADVANCE \d3 F).	 ADVANCE \d12 SC

	 ADVANCE \d12 ii.	Heat Dissipation Areas

	

 ADVANCE \d12 (1)	Streams	 ADVANCE \d12 FW2-TM, FW2-NT, All SE

 ADVANCE \d12 (i)	Not more than one-quarter (1/4) of the cross section
and/or volume of the water body at any time;

	 ADVANCE \d12 (ii)	Not more than two-thirds (2/3) of the surface from
shore to shore at any time; and

	

 ADVANCE \d12 (iii)	These limits may be exceeded by special permission,
on a case-by-case basis, when a discharger can demonstrate that a larger
heat dissipation area meets the tests for a waiver under Section 316 of
the Federal Clean Water Act.

	

	 ADVANCE \d12 (2)	Lakes, Ponds, Reservoirs, Bays or Coastal Waters:
Heat dissipation areas will be developed on a case-by-case basis.	
ADVANCE \d12 All Classifications

 ADVANCE \d12 12.	Toxic Substances (general)	 ADVANCE \d12 i.	None,
either alone or in combination with other substances, in such
concentrations as to affect humans or be detrimental to the natural
aquatic biota, produce undesirable aquatic life, or which would render
the waters unsuitable for the designated uses.	 ADVANCE \d12 All
Classifications

 ADVANCE \d12 ii.	None which would cause standards for drinking water to
be exceeded after appropriate treatment.	 ADVANCE \d12 FW2

 ADVANCE \d12 iii.	Toxic substances shall not be present in
concentrations that cause acute or chronic toxicity to aquatic biota, or
bioaccumulate within an organism to concentrations that exert a toxic
effect on that organism or render it unfit for consumption.	 ADVANCE
\d12 All Classifications

	 ADVANCE \d12 iv.	The concentrations of nonpersistent toxic substances
in the State's waters shall not exceed one-twentieth (0.05) of the acute
definitive LC ADVANCE \d3 50 ADVANCE \u3  or EC ADVANCE \d3 50 ADVANCE
\u3  value, as determined by appropriate bioassays conducted in
accordance with N.J.A.C. 7:18.	 ADVANCE \d12 All Classifications

 ADVANCE \d12 v.	The concentration of persistent toxic substances in the
State's waters shall not exceed one-hundredeth (0.01) of the acute
definitive LC ADVANCE \d3 50 ADVANCE \u3  or EC ADVANCE \d3 50 ADVANCE
\u3  value, as determined by appropriate bioassays conducted in
accordance with N.J.A.C. 7:18.	 ADVANCE \d12 All Classifications

 ADVANCE \d12 13.	Toxic Substances (g/L):	 ADVANCE \d12 

	

 ADVANCE \d12 NOTE:  Except as noted, aquatic life criteria followed by
an (a) represent acute aquatic life protection criteria as a one-hour
average (3-hour for ammonia, 6-hours for lead) and aquatic life criteria
followed by (c) represent chronic aquatic life protection criteria as a
four-day average (30-day for ammonia).  No exceedance of aquatic life
criteria shall be permitted at or above the design flows specified in
section N.J.A.C. 7:9B-1.5(c)2.  Criteria followed by an (h) are
noncarcinogenic effect-based human health criteria as a 30-day average
with no frequency of exceedance at or above the design flows specified
in section N.J.A.C. 7:9B-1.5(c)2.  Criteria followed by an (hc) are
carcinogenic effect-based human health criteria as a 70-year average
with no frequency of exceedance at or above the design flows specified
in section N.J.A.C. 7:9B-1.5(c)2 and are based on a risk level of
one-in-one-million.  Criteria followed by an (hcc) are for toxic
substances considered to be possible human carcinogens as a 70-year
average with no frequency of exceedance at or above the design flows
specified in section N.J.A.C. 7:9B-1.5(c)2 and are based on a risk level
of one-in-one hundred thousand.  Criteria followed by an (OL) are
organoleptic effect-based criteria and are maximum concentrations.

 ADVANCE \d12 i.	Acenaphthylene	 ADVANCE \d12 	Reserved.

	 ADVANCE \d12 ii.	Acrolein	 ADVANCE \d12 (1)	320(h)(2)	780(h)	 ADVANCE
\d12 All FW2All SE, SC

 ADVANCE \d12 iii.	Acrylonitrile	 ADVANCE \d12 (1)	0.0591(hc)(2)
0.665(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 iv.	Aldrin	 ADVANCE \d12 (1)	3.0(a); 0.000135(hc)(2)
1.3(a); 0.000144(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 v.	Aluminum (Total recoverable)	 ADVANCE \d12 	Reserved.

	 ADVANCE \d12 vi.	Ammonia, un-ionized(mg NH ADVANCE \d3 3 ADVANCE \u3
-N/L)	 ADVANCE \d6 (1)	at pH ( 8.30

 ADVANCE \d6 	0.179(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (a)

 ADVANCE \d6 	0.046(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (c)

 ADVANCE \d6 	at pH ( 8.30

 ADVANCE \d6 	0.179(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (a)

 ADVANCE \d6 	0.046(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (c)

 ADVANCE \d6 (2)	at pH ( 8.30

 ADVANCE \d6 	0.201(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (a) (Summer ADVANCE \u4 1 ADVANCE \d4 )

 ADVANCE \d6 	0.054(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (c) (Summer ADVANCE \u6 1 ADVANCE \d6 )

 ADVANCE \d6 	0.232(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (a) (Winter ADVANCE \u4 2 ADVANCE \d4 )

 ADVANCE \d6 	0.060(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (c) (Winter ADVANCE \u4 2 ADVANCE \d4 )

 ADVANCE \d6 	at pH ( 8.30

 ADVANCE \d6 	0.201(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (a)
(Summer ADVANCE \u4 1 ADVANCE \d4 )

 ADVANCE \d6 	0.054(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (c)
(Summer ADVANCE \u4 1 ADVANCE \d4 )

 ADVANCE \d6 	0.232(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (a)
(Winter ADVANCE \u4 2 ADVANCE \d4 )

 ADVANCE \d6 	0.060(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (c)
(Winter ADVANCE \u4 2 ADVANCE \d4 ) 	 ADVANCE \d6 FW2-TP, FW2-TM

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d12 FW2-NT

 ADVANCE \d6 

Summer spawning period from March 1st through October 31st.

Winter non-spawning period from November 1st through February 28/29th.

 ADVANCE \d12 	 ADVANCE \d6 (3)	at pH ( 8.30

 ADVANCE \d6 	0.238(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (a)

 ADVANCE \d6 	0.061(10 ADVANCE \u6 0.026(Temp-20) + 0.41 (pH-7.80)
ADVANCE \d6 (c)

 ADVANCE \d6 	at pH ( 8.30

 ADVANCE \d6 	0.238(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (a)

 ADVANCE \d6 	0.061(10 ADVANCE \u6 0.026(Temp-20) + 0.20 ADVANCE \d6 (c)

 ADVANCE \d6 (4)	0.115(a)

0.030(c)

 ADVANCE \d6 (5)	0.094(a)

0.024(c)	 ADVANCE \d6 PL

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 

 ADVANCE \d6 All SE

 ADVANCE \d6 SC

 ADVANCE \d12 vii.	Anthracene	 ADVANCE \d12 (1)	9,570(h)(2)	108,000(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 viii.	Antimony (Total recoverable)	 ADVANCE \d12 (1)
12.2(h)(2)	4,300(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 ix.	Arsenic (Total recoverable)	 ADVANCE \d12 (1)
0.0170(hc)(2)	0.136(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 x.	Asbestos	 ADVANCE \d12 (1)	7 million fibers/L (h)
(fibers longer than 10 micrometers)	 ADVANCE \d12 All FW2

 ADVANCE \d12 xi.	Barium (Total recoverable)	 ADVANCE \d12 (1)	2,000(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 xii.	Benz(a)anthracene	 ADVANCE \d12 (1)	0.0028(hc)(2)
0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xiii.	Benzene	 ADVANCE \d12 (1)	0.150(hc)(2)	71(hc)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xiv.	Benzidine	 ADVANCE \d12 (1)	0.000118(hc)(2)
0.000535(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xv.	3,4-Benzofluoranthene (Benzo(b)fluoranthene)	 ADVANCE
\d12 (1)	0.0028(hc)(2)	0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xvi.	Benzo(a)pyrene (BaP)	 ADVANCE \d12 (1)	0.0028(hc)(2)
0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xvii.	Benzo(ghi)perylene	 ADVANCE \d12 	Reserved.

	 ADVANCE \d12 xviii.	Benzo(k)fluoranthene	 ADVANCE \d12 (1)
0.0028(hc)(2)	0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xix.	Beryllium (Total recoverable)	 ADVANCE \d12 
Reserved.

	 ADVANCE \d12 xx.	alpha-BHC (alpha-HCH)	 ADVANCE \d12 (1)
0.00391(hc)(2)	0.0131(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxi.	beta-BHC (beta-HCH)	 ADVANCE \d12 (1)	0.137(hcc)(2)
0.460(hcc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxii.	gamma-BHC (gamma-HCH/Lindane)	 ADVANCE \d12 (1)
2.0(a); 0.080(c)(2)	0.16(a)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxiii.	Bis(2-chloroethyl) ether	 ADVANCE \d12 (1)
0.0311(hc)(2)	1.4(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxiv.	Bis(2-chloroisopropyl) ether	 ADVANCE \d12 (1)
1,250(h)(2)	170,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxv.	Bis(2-ethylhexyl) phthalate	 ADVANCE \d12 (1)
1.76(hc)(2)	5.92(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxvi.	Bromodichloromethane (Dichlorobromomethane)	 ADVANCE
\d12 (1)	0.266(hc)(2)	22(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxvii.	Bromoform	 ADVANCE \d12 (1)	4.38(hc)(2)	360(hc)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxviii.	Butyl benzyl phthalate	 ADVANCE \d12 (1)	239(h)(2)
416(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxix.	Cadmium (Total recoverable)	 ADVANCE \d12 (1)	10(h)

	 ADVANCE \d12 All FW2

 ADVANCE \d12 xxx.	Carbon tetrachloride	 ADVANCE \d12 (1)	0.363(hc)(2)
6.31(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxi.	Chlordane	 ADVANCE \d12 (1)	2.4(a); 0.0043(c);
0.000277(hc)(2)	0.09(a); 0.0040(c); 0.000283(hc)	 ADVANCE \d12 All
FW2All SE, SC

 ADVANCE \d12 xxxii.	Chloride	 ADVANCE \d12 (1)	250,000 (ol);
860,000(a); 230,000(c)	 ADVANCE \d12 All FW2

 ADVANCE \d12 xxxiii.	Chlorine Produced Oxidants (CPO)	 ADVANCE \d12 (1)
19(a); 11(c)(2)	13(a); 7.5(c)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxiv.	Chlorobenzene	 ADVANCE \d12 (1)	22.0(h)(2)
21,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxv.	Chloroform	 ADVANCE \d12 (1)	5.67(hc)(2)	470(hc)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxvi.	2-Chlorophenol	 ADVANCE \d12 (1)	122(h)(2)	402(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxvii.	Chlorpyrifos	 ADVANCE \d12 (1)	0.083(a);
0.041(c)(2)	0.011(a); 0.0056(c)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxviii.	Chromium (Total recoverable)	 ADVANCE \d12 (1)
160(h)(2)	3,230(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xxxix.	Chrysene	 ADVANCE \d12 (1)	0.0028(hc)(2)	0.031(hc)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xl.	Copper (Dissolved)	 ADVANCE \d12 (1)	Reserved.(2)
Reserved.(3)	7.9(a); 5.6(c)	 ADVANCE \d12 New York/New Jersey Harbor
Estuary*

 ADVANCE \d12 xli.	Cyanide	 ADVANCE \d12 (1)	22(a); 5.2(c); 768(h)(2)
1.0(a); 1.0(c); 220,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xlii.	4,4'-DDD (p,p'-TDE)	 ADVANCE \d12 (1)
0.000832(hc)(2)	0.000837(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xliii.	4,4'-DDE	 ADVANCE \d12 (1)	0.000588(hc)(2)
0.000591(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xliv.	4,4'-DDT	 ADVANCE \d12 (1)	1.1(a); 0.0010(c);
0.000588(hc)(2)	0.13(a); 0.0010(c); 0.000591(hc)	 ADVANCE \d12 All
FW2All SE, SC

 ADVANCE \d12 xlv.	Demeton	 ADVANCE \d12 (1)	0.1(c)	 ADVANCE \d12 All
FW2, SE, and SC



 ADVANCE \d6 *	Waters which include Newark Bay, the New Jersey portions
of Raritan Bay, Upper New York Bay, Lower New York Bay, Arthur Kill,
Kill Van Kull, saline portions of the Passaic, Hackensak, and Hudson
Rivers and saline portions of tributaries to all of these waters.

 ADVANCE \d12 xlvi.	Dibenz(a,h)anthracene	 ADVANCE \d12 (1)
0.0028(hc)(2)	0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xlvii.	Dibromochloromethane (Chlorodibromomethane)	
ADVANCE \d12 (1)	72.6(h)	 ADVANCE \d12 All FW2

 ADVANCE \d12 xlviii.	Di-n-butyl phthalate	 ADVANCE \d12 (1)	3,530(h)(2)
15,700(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xlix.	1,2-Dichlorobenzene	 ADVANCE \d12 (1)	2,520(h)(2)
16,500(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 l.	1,3-Dichlorobenzene	 ADVANCE \d12 (1)	2,620(h)(2)
22,200(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 li.	1,4-Dichlorobenzene	 ADVANCE \d12 (1)	343(h)(2)
3,159(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lii.	3,3'-Dichlorobenzidine	 ADVANCE \d12 (1)
0.0386(hc)(2)	0.0767(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 liii.	1,2-Dichloroethane	 ADVANCE \d12 (1)	0.291(hc)(2)
99(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 liv.	1,1-Dichloroethylene	 ADVANCE \d12 (1)	4.81(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 lv.	trans-1,2-Dichloroethylene	 ADVANCE \d12 (1)	592(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 lvi.	2,4-Dichlorophenol	 ADVANCE \d12 (1)	92.7(h)(2)
794(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lvii.	1,3-Dichloropropene	 ADVANCE \d12 (1)	0.193(hc)(2)
1,700(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lviii.	Dieldrin	 ADVANCE \d12 (1)	2.5(a); 0.0019(c);
0.000135(hc)(2)	0.71(a); 0.0019(c); 0.000144(hc)	 ADVANCE \d12 All
FW2All SE, SC

 ADVANCE \d12 lix.	Diethyl phthalate	 ADVANCE \d12 (1)	21,200(h)(2)
111,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lx.	Dimethyl phthalate	 ADVANCE \d12 (1)	313,000(h)(2)
2,900,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxi.	4,6-Dinitro-o-cresol	 ADVANCE \d12 (1)	13.4(h)(2)
765(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxii.	2,4-Dinitrophenol	 ADVANCE \d12 (1)	69.7(h)(2)
14,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxiii.	2,4-Dinitrotoluene	 ADVANCE \d12 (1)	0.11(hc)(2)
9.1(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxiv.	1,2-Diphenylhydrazine	 ADVANCE \d12 (1)
0.0405(hc)(2)	0.541(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxv.	Endosulfans (alpha and beta)	 ADVANCE \d12 (1)
0.22(a); 0.056(c); 0.932(h)(2)	0.034(a); 0.0087(c); 1.99(h)	 ADVANCE
\d12 All FW2All SE, SC

 ADVANCE \d12 lxvi.	Endosulfan sulfate	 ADVANCE \d12 (1)	0.93(h)(2)
2.0(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxvii.	Endrin	 ADVANCE \d12 (1)	0.18(a); 0.0023(c);
0.629(h)(2)	0.037(a); 0.0023(c); 0.678(h)	 ADVANCE \d12 All FW2All SE,
SC

 ADVANCE \d12 lxviii.	Endrin aldehyde	 ADVANCE \d12 (1)	0.76(h)(2)
0.81(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxix.	Ethylbenzene	 ADVANCE \d12 (1)	3,030(h)(2)	27,900(h)
 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxx.	Fluoranthene	 ADVANCE \d12 (1)	310(h)(2)	393(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxi.	Fluorene	 ADVANCE \d12 (1)	1,340(h)	 ADVANCE \d12
All FW2

 ADVANCE \d12 lxxii.	Guthion	 ADVANCE \d12 (1)	0.01(c)	 ADVANCE \d12
All FW2, SE and SC

 ADVANCE \d12 lxxiii.	Heptachlor	 ADVANCE \d12 (1)	0.52(a); 0.0038(c);
0.000208(hc)(2)	0.053(a); 0.0036(c); 0.000214(hc)	 ADVANCE \d12 All
FW2All SE, SC

 ADVANCE \d12 lxxiv.	Heptachlor epoxide	 ADVANCE \d12 (1)	0.52(a);
0.0038(c); 0.000103(hc)(2)	0.053(a); 0.0036(c); 0.000106(hc)	 ADVANCE
\d12 All FW2All SE, SC

 ADVANCE \d12 lxxv.	Hexachlorobenzene	 ADVANCE \d12 (1)	0.000748(hc)(2)
0.000775(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxvi.	Hexachlorobutadiene	 ADVANCE \d12 (1)	6.94(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 lxxvii.	Hexachlorocyclopentadiene	 ADVANCE \d12 (1)
245(h)(2)	17,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxviii.	Hexachloroethane	 ADVANCE \d12 (1)	2.73(h)(2)
12.4(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxix.	Indeno(1,2,3-cd)pyrene	 ADVANCE \d12 (1)
0.0028(hc)(2)	0.031(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxx.	Iron (Total recoverable)	 ADVANCE \d12 	Reserved.

	 ADVANCE \d12 lxxxi.	Isophorone	 ADVANCE \d12 (1)	552(h)	 ADVANCE \d12
All FW2

 ADVANCE \d12 lxxxii.	Lead (Total recoverable)	38(a); 5.4(c)
(Dissolved); 5(h) (Total recoverable)(2)	210(a); 24(c) (Dissolved)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxxiii.	Malathion	 ADVANCE \d12 (1)	0.1(c)	 ADVANCE \d12
All FW2, SE and SC

 ADVANCE \d12 lxxxiv.	Manganese (Total recoverable)	 ADVANCE \d12 (1)
100(h)	 ADVANCE \d12 All SE, SC

 ADVANCE \d12 lxxxv.	Mercury (Total recoverable)	 ADVANCE \d12 (1)
0.144(h)(2)	0.146(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxxvi.	Methoxychlor	 ADVANCE \d12 (1)	0.03(c); 40(h)(2)
0.03(c)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxxvii.	Methyl bromide (Bromomethane)	 ADVANCE \d12 (1)
48.4(h)(2)	4,000(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 lxxxviii.Methyl chloride (Chloromethane)	 ADVANCE \d12 
Reserved.

	 ADVANCE \d12 lxxxix.	Methylene chloride	 ADVANCE \d12 (1)	2.49(hc)(2)
1,600(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xc.	Mirex	 ADVANCE \d12 (1)	0.001(c)	 ADVANCE \d12 All
FW2, SE and SC

 ADVANCE \d12 xci.	Nickel (Total recoverable)	 ADVANCE \d12 (1)
516(h)(2)	3,900(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xcii.	Nitrate (as N)	 ADVANCE \d12 (1)	10,000(h)	 ADVANCE
\d12 All FW2

 ADVANCE \d12 xciii.	Nitrobenzene	 ADVANCE \d12 (1)	16.0(h)(2)	1,900(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xciv.	N-Nitrosodi-n-butylamine	 ADVANCE \d12 (1)
0.00641(hc)	 ADVANCE \d12 All FW2

 ADVANCE \d12 xcv.	N-Nitrosodiethylamine	 ADVANCE \d12 (1)	0.000233(hc)	
ADVANCE \d12 All FW2

 ADVANCE \d12 xcvi.	N-Nitrosodimethylamine	 ADVANCE \d12 (1)
0.000686(hc)(2)	8.1(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xcvii.	N-Nitrosodiphenylamine	 ADVANCE \d12 (1)
4.95(hc)(2)	16.2(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 xcviii.	N-Nitrosopyrrolidine	 ADVANCE \d12 (1)	0.0167(hc)	
ADVANCE \d12 All FW2

 ADVANCE \d12 xcix.	Parathion	 ADVANCE \d12 (1)	0.065(a); 0.013(c)	
ADVANCE \d12 All FW2

 ADVANCE \d12 c.	Pentachlorobenzene	 ADVANCE \d12 (1)	3.67(h)(2)	4.21(h)
 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 ci.	Pentachlorophenol	 ADVANCE \d12 (1)	e ADVANCE \u3
(1.005(pH)-4.830) ADVANCE \d3 (a); e ADVANCE \u3 (1.005(pH)-5.290)
ADVANCE \d3 (c); 0.282(hc)

(2)	13(a); 7.9(c); 8.2(hc)	 ADVANCE \d12 All FW2

All SE, SC

 ADVANCE \d12 cii.	Phenanthrene	 ADVANCE \d12 	Reserved.

	 ADVANCE \d12 ciii.	Phenol	 ADVANCE \d12 (1)	20,900(h)(2)	4,600,000(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 civ.	Phosphorous (yellow)	 ADVANCE \d12 (1)	0.1(c)	
ADVANCE \d12 All SE, SC

 ADVANCE \d12 cv.	Polychlorinated biphenyls (PCBs)	 ADVANCE \d12 (1)
0.014(c); 0.00017(hc)(2)	0.030(c); 0.00017(hc)	 ADVANCE \d12 All FW2All
SE, SC

 ADVANCE \d12 cvi.	Pyrene	 ADVANCE \d12 (1)	797(h)(2)	8,970(h)	 ADVANCE
\d12 All FW2All SE, SC

 ADVANCE \d12 cvii.	Selenium (Total recoverable)	 ADVANCE \d12 (1)	10(h)
 ADVANCE \d12 All FW2

 ADVANCE \d12 cviii.	Silver (Total recoverable)	 ADVANCE \d12 (1)	164(h)
 ADVANCE \d12 All FW2

 ADVANCE \d12 cix.	Sulfide-hydrogen sulfide (undissociated)	 ADVANCE
\d12 (1)	2(c)	 ADVANCE \d12 All FW2, SE and SC

 ADVANCE \d12 cx.	1,2,4,5-Tetrachlorobenzene	 ADVANCE \d12 (1)
2.56(h)(2)	3.25(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxi.	2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD)	 ADVANCE
\d12 (1)	0.000000013(hc)(2)	0.000000014(hc)	 ADVANCE \d12 All FW2All SE,
SC

 ADVANCE \d12 cxii.	1,1,2,2-Tetrachloroethane	 ADVANCE \d12 (1)
1.72(hcc)	 ADVANCE \d12 All FW2

 ADVANCE \d12 cxiii.	Tetrachloroethylene	 ADVANCE \d12 (1)	0.388(hc)(2)
4.29(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxiv.	Thallium (Total recoverable)	 ADVANCE \d12 (1)
1.70(h)(2)	6.22(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxv.	Toluene	 ADVANCE \d12 (1)	7,440(h)(2)	200,000(h)	
ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxvi.	Toxaphene	 ADVANCE \d12 (1)	0.73(a); 0.0002(c);
0.000730(hc)(2)	0.21(a); 0.0002(c); 0.000747(hc)	 ADVANCE \d12 All
FW2All SE, SC

 ADVANCE \d12 cxvii.	1,2,4-Trichlorobenzene	 ADVANCE \d12 (1)	30.6(h)(2)
113(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxviii.	1,1,1-Trichloroethane	 ADVANCE \d12 (1)	127(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 cxix.	1,1,2-Trichloroethane	 ADVANCE \d12 (1)	13.5(h)	
ADVANCE \d12 All FW2

 ADVANCE \d12 cxx.	Trichloroethylene	 ADVANCE \d12 (1)	1.09(hc)(2)
81(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxxi.	2,4,5-Trichlorophenol	 ADVANCE \d12 (1)	2,580(h)(2)
9,790(h)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxxii.	2,4,6-Trichlorophenol	 ADVANCE \d12 (1)	2.14(hc)(2)
6.53(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxxiii.	Vinyl chloride	 ADVANCE \d12 (1)	0.0830(hc)(2)
525(hc)	 ADVANCE \d12 All FW2All SE, SC

 ADVANCE \d12 cxxiv.	Zinc (Total recoverable)	 ADVANCE \d12 	Reserved.	
ADVANCE \d12 

 ADVANCE \d12 14.	Turbidity (Nephelometric 	Turbidity Unit-NTU)	 ADVANCE
\d12 i.	Maximum 30-day average of 15 NTU, a maximum of 50 NTU at any
time.	 ADVANCE \d12 FW2, SE3

 ADVANCE \d12 ii.	Maximum 30-day average of 10 NTU, a maximum of 30 NTU
at any time.	 ADVANCE \d12 SE1, SE2

 ADVANCE \d12 iii.	Levels shall not exceed 10.0 NTU.	 ADVANCE \d12 SC



(d) Surface water quality criteria for waters under the jurisdiction of
the DRBC:

1.	Mainstem Delaware River and Delaware Bay:

i.	For parameters with criteria in "Delaware River Basin Commission,
Administrative Manual - Part III, Water Quality Regulations," Article 3,
dated October 23, 1996, including all amendments and future supplements
thereto, the criteria contained therein are the applicable criteria.

ii.	For parameters without criteria in "Delaware River Basin Commission,
Administrative Manual - Part III, Water Quality Regulations," Article 3,
dated October 23, 1996, including all amendments and future supplements
thereto, the criteria at (c) above are the applicable criteria and shall
be applied as follows:

(1)	Criteria applicable to FW2-NT waters apply where salinities are less
than or equal to 3.5 parts per thousand (ppt) at mean high tide;

(2)	Criteria applicable to SE waters apply where salinities are greater
than 3.5 ppt at mean high tide; and

(3)	Where salinities vary from 3.5 ppt or less, to greater than 3.5 ppt,
at mean high tide, the more stringent of the FW2-NT or SE criteria
apply.

2.	Tributaries to the mainstem Delaware River and Delaware Bay:

i.	The applicable criteria are those contained in "Delaware River Basin
Commission, Administrative Manual - Part III, Water Quality
Regulations," Article 3, dated October 23, 1996, including all
amendments and supplements thereto; or

ii.	The criteria at (c) above, whichever are more stringent.

3.	For all waters under the jurisdiction of the DRBC where criteria are
not established in "Delaware River Basin Commission, Administrative
Manual - Part III, Water Quality Regulations," Article 3, dated October
23, 1996, including all amendments and future supplements thereto, or at
(c) above, the Department shall use criteria based upon the best
available scientific information, in accordance with (d)1ii above and
N.J.A.C. 7:9B-1.5(c)5, to establish water quality-based effluent
limitations.

7:9B-1.15  Surface water classifications for the waters of the State of
New Jersey

(a)  This section contains the surface water classifications for the
waters of the State of New Jersey.  Surface water classifications are
presented in tabular form.  Subsections (c) through (g) contain surface
water classifications by major drainage basin.  Subsection (h) lists FW1
waters by tract within basins and subsection (i) identifies the
Outstanding National Resource Waters of the State.

(b)  The following are instructions for the use of Tables 1 through 5
found in N.J.A.C. 7:9B-1.15(c) through (g) respectively:

1.  The surface water classification tables give the surface water
classifications for waters of the State.  Surface waters of the State
and their classification are listed in the table covering the major
drainage basin in which they are located.  The major drainage basins
are:

i.	The Atlantic Coastal drainage basin which contains the surface waters
listed in Table 1 in (c) below;

ii.	The Delaware River drainage basin which contains the surface waters
listed in Table 2 in (d) below;

iii.	The Passaic River, Hudson River and New York Harbor Complex
drainage basin which contains the surface waters listed in Table 3 in
(e) below;

iv.	The Raritan River and Raritan Bay drainage basin which contains the
surface waters listed in Table 4 in (f) below; and 

v.	The Wallkill River drainage basin which contains the surface waters
listed in Table 5 in (g) below.

2.  Within each basin the waters are listed alphabetically and segment
descriptions begin at the headwaters and proceed downstream.

3.  To find a stream:

i.	Determine which major drainage basin the stream is in;

ii.	Look for the name of the stream in the appropriate table and find
the classification;

iii.	For unnamed or unlisted streams, find the stream or other waterbody
that the stream of interest flows into and look for the classification
of that stream or waterbody.  The classification of the stream of
interest may then be determined by referring to (b)5 below.  If the
second stream or waterbody is also unlisted, repeat the process until a
listed stream or waterbody is found.  Use (b)5iv below to classify
streams entering unlisted lakes.

4.  To find a lake or other non-stream waterbody:

i.	Determine which major drainage basin the waterbody is in;

ii.	Look for the waterbody name in the appropriate table;

iii.	If the waterbody is not listed, use (b)5ii, 5iii, 5vi, and 5vii
below to determine the appropriate classification.

5.  To find unnamed waterways or waterbodies or named waterways or
waterbodies which do not appear in the listing, use the following
instructions:

i.	Unnamed or unlisted freshwater streams that flow into streams
classified as FW2-TP, FW2-TM, or FW2-NT take the classification of the
classified stream they enter, unless the unlisted stream is a PL water
which is covered in (b)5vii below.  If the stream could be a C1 water,
see (b)5vi below.

ii.	All freshwater lakes, ponds and reservoirs that are five or more
acres in surface area, that are not located entirely within the
Pinelands Area boundaries (see (b)5vii below) and that are not
specifically listed as FW2-TP or FW2-TM are classified as FW2-NT.  This
includes lakes, ponds and reservoirs on segments of streams which are
classified as FW2-TM or FW2-TP such as Saxton Lake on the Musconetcong
River.  If the waterbody could be a C1 water, also check (b)5vi below.

iii.	All freshwater lakes, ponds and reservoirs, that are less than five
acres in surface area, upstream of and contiguous with FW2-TP or FW2-TM
streams, and which are not located entirely within the Pinelands Area
boundaries (see(b)5vii below) are classified as FW2-TM.  All other
freshwater lakes, ponds and reservoirs that are not otherwise classified
in this subsection or the following tables are classified as FW2-NT.  If
the waterbody could be a C1 water, also check (b)5vi below.

iv.	Unnamed or unlisted streams that enter FW2 lakes, ponds and
reservoirs take the classification of either the listed tributary stream
flowing into the lake with the highest classification or the listed
tributary stream leaving the lake with the highest classification,
whichever has the highest classification, or, if there are no listed
tributary or outlet streams to the lake, the first listed stream
downstream of the lake.  If the stream is located within the boundaries
of the Pinelands Area, see (b)5.vii. below; if it could be a C1 water,
also see (b)5vi below.

v.	Unnamed or unlisted saline waterways and waterbodies are classified
as SE1 in the Atlantic Coastal Basin.  Unnamed or unlisted saline
waterways which enter SE2 or SE3 waters in the Passaic, Hackensack and
New York Harbor Complex basin are classified as SE2 unless otherwise
classified within Table 3 in (e) below.  Freshwater portions of unnamed
or unlisted streams entering SE1, SE2, or SE3 waters are classified as
FW2-NT.  This only applies to waters that are not PL waters (see (b)5vii
below).  If the waterbody or waterway could be a C1 water, also see
(b)5vi below.

vi.	If the waterway or waterbody of interest flows through or is
entirely located within State parks, forests or fish and game lands,
Federal wildlife refuges, other special holdings, or is a State
shellfish water as defined in this subchapter, the Department's maps
should be checked to determine if the waterbody of interest is mapped as
a C1 water.  If the waterway or waterbody does not appear on the United
States Geological Survey quadrangle that the Department used as a base
map in its designation of the C1 waters, the Department will determine
on a case-by-case basis whether the waterway or waterbody should be
designated as C1.

vii. All waterways or waterbodies, or portions of waterways or
waterbodies, that are located within the boundaries of the Pinelands
Area established at N.J.S.A. 13:18A-11a are classified as PL unless they
are listed as FW1 waters in Table 6 in (h) below.  A tributary entering
a PL stream is classified as PL only for those portions of the tributary
that are within the Pinelands Area.  Lakes are classified as PL only if
they are located entirely within the Pinelands Area.

6.  The following 10 classifications are used for the sole purpose of
identifying the water quality classification of the waters listed in the
tables in (c) through (h) below:

i.	"FW1" means freshwaters wholly within Federal or State lands or
special holdings that are preserved for posterity and are not subject to
manmade wastewater discharges.

ii.	"FW2-TP" means FW2 trout production.

iii.	"FW2-TM" means FW2 trout maintenance.

iv.	"FW2-NT" means FW2 non trout.

v.	"PL" means Pinelands Waters.

vi.	"SE1" means saline estuarine waters whose designated uses are listed
in N.J.A.C. 7:9B-1.12(d).

vii."SE2"  means saline estuarine waters whose designated uses are
listed in N.J.A.C. 7:9B-1.12(e).

viii."SE3" means saline estuarine waters whose designated uses are
listed in N.J.A.C. 7:9B-1.12(f).

ix.	"SC" means the general surface water classification applied to
saline coastal waters.

x.	FW2-NT/SE1 (or a similar designation that combines two
classifications) means a waterway in which there may be a salt
water/fresh water interface.  The exact point of demarcation between the
fresh and saline waters must be determined by salinity measurements and
is that point where the salinity reaches 3.5 parts per thousand at mean
high tide.  The stream is classified as FW2-NT in the fresh portions
(salinity less than or equal to 3.5 parts per thousand at mean high
tide) and SE1 in the saline portions.

7.  The following water quality designations are used in Tables 1
through 5 in (c) through (g), respectively, below:

i.	"(C1)" means Category One waters;

ii.	"(tp)" indicates trout production in waters which are classified as
FW1.  This is for information only and does not affect the water quality
criteria for those waters;

iii.	"(tm)" indicates trout maintenance in waters which are classified
as PL or FW1.  For FW1 waters this is for information only and does not
affect the water quality criteria for those waters.

(c)  The surface water classifications in Table 1 are for waters of the
Atlantic Coastal Basin:

TABLE  1

Waterbody									Classification

ABRAMS CREEK

(Marmora) - Entire length, except portion outside the 		FW2-NT/SE1(C1)

boundaries of the MacNamara Wildlife Management Area 

(Griscom) - Portions of the Creek and tributaries outside 	FW2-NT/SE1

of the MacNamara Wildlife Management Area

ABSECON BAY (Absecon) - All waters within Absecon Wildlife 	SE1(C1)

Management Area

ABSECON CREEK

(Egg Harbor) - North and South Branches from their 		PL

origins downstream to the boundary of the Pinelands Protection and
Preservation Area

(Absecon) - Entire length, except portions described 		FW2-NT/SE1

above

ARNOLD POND (Barnegat)						FW2-NT/SE1(C1)

ATLANTIC OCEAN

(Offshore) - Waters from the shoreline out to the three 	SC

mile limit, except areas described below

(Beach Haven) - Waters of the Atlantic Ocean out to the 	SC(C1)

State's three mile limit from Beach Haven Inlet to Cape May Point,
excluding the following waters:

1.   (Atlantic City) - All of the Ocean waters inshore of a line that
begins at the center of Convention Hall, Atlantic City bearing
approximately 153 degrees T (True North) and extends 2.0 nautical miles
to a point with coordinates of latitude 39 degrees 19.4 minutes N.,
longitude 74 degrees 25.1 minutes W., from this point, approximately 2
nautical miles offshore, the line runs parallel to the shoreline in a
southwesterly direction for approximately 2.1 nautical miles to a point
with coordinates of latitude 39 degrees 18.4 minutes N., longitude 74
degrees 27.5 minutes W., then bearing approximately 333 degrees T
(reciprocal 153 degrees T) for approximately 1.9 nautical miles to the
outermost tip of the Ventnor City Fishing Pier located at the Boardwalk
and South Cambridge Ave., City of Ventnor, then along that pier to the
shore and terminating.

2.   (Ocean City) - All of the ocean waters inshore of a line which
begins at the City of Ocean City's Beach Patrol, First Aid and Rest Room
building located on the beach at 34th Street, with coordinates of
latitude 39 degrees 15.0 minutes N., longitude 74 degrees 36.6 minutes
W., and bears approximately 126 degrees T (True North) for approximately
1.5 nautical miles from the shoreline to a point with coordinates of
latitude 39 degrees 14.1 minutes N., longitude 74 degrees 35.0 minutes
W., then bears approximately 216 degrees T along the shoreline in a
southwesterly direction 1.5 nautical miles offshore, for approximately
2.3 nautical miles to a point with coordinates of latitude 39 degrees
12.3 minutes N., longitude 74 degrees 36.7 minutes W., then bears
approximately 306 degrees T for approximately 1.4 nautical miles to the
outermost tip of Anglers Fishing Club's Pier, 5825 Central Ave., Ocean
City, then along that pier to the shoreline.

3.   Seven mile beach outfall exclusion

4.   Wildwood outfall exclusion

  TRIBUTARIES, ATLANTIC OCEAN

(New Jersey Coast) - All those streams or segments of 	FW2-NT/SE1

streams that flow directly into the Atlantic Ocean or into back bays of
the Ocean which are not included elsewhere in this list, are not within
the boundaries of the Pinelands Protection or Preservation Areas and are
not mapped as C1 waters by the Department

(Pinelands) - All streams or segments of streams which 	PL

flow directly into the Atlantic Ocean or into back bays of the Ocean,
are within the boundaries of the Pinelands Protection and Preservation
Areas and are not classified as FW1 in this Table

(New Jersey Coast) - All streams or segments of		FW2-NT/SE1(C1)

streams which flow directly into the Atlantic Ocean or into back bays of
the Ocean, are mapped as C1 waters by the Department, are not trout
maintenance waters, and are not classified as FW1 in this Table

BABCOCK CREEK (Marmora) - Entire length 				FW2-NT/SE1(C1)

BALLANGER CREEK

(New Gretna) - Source to Pollys Ditch				FW2-NT/SE1

(New Gretna) - Pollys Ditch to Bay				SE1(C1)

BANKS CREEK (Marmora) - Entire length				SE1(C1)

BARNEGAT BAY

(Barnegat National Wildlife Refuge) - All waters within 	SE1(C1)

the boundaries of the Barnegat National Wildlife Refuge

(Barnegat Light) - All other waters of the Bay			SE1(C1)

(Island Beach State Park) - All freshwater ponds within 	FW1

the boundaries of Island Beach State Park

(Island Beach State Park) - All waters in the Park, not 	FW2-NT/SE1/

classified as FW1 above					SC(C1)

BARNEGAT BAY TRIBUTARIES - See ATLANTIC OCEAN,

TRIBUTARIES

BASS RIVER

(Oswego Lake) - Source to Pineland Protection and 		PL

Preservation Area boundary at the Garden State Parkway, except those
branches described separately below

(New Gretna) - Pineland Protection and Preservation 		FW2-NT/SE1

Area boundary to the boundary of shellfish waters 

(New Gretna) - Boundary of shellfish waters to 			SE1(C1)

Mullica River

(Bass River State Forest) - Tommy's Branch from its 		FW1

headwaters to the Bass River State Forest Recreation Area service road

(Bass River State Forest) - Falkenburg Branch of Lake 	FW1

Absegami from its headwaters to the Lake

BATSTO RIVER

(Browns Mills) - Entire length, except waters described 	PL

separately below

(Wharton) - Skit Branch and tributaries from their 		FW1

headwaters to the confluence with Robert's Branch

(Wharton) - The easterly branches of the Batsto River 	FW1

from Batsto Village upstream to the confluence with Skits Branch

BEACH THOROFARE (Margate) - Entire length			SE1(C1)

BEAR SWAMP BROOK 

(Squankum) - Entire length, except segment described 	FW2-NT

below

(Allaire) - Segment within the boundaries of Allaire 		FW2-NT(C1)

State Park

BIG ELDER CREEK

(Sea Isle City) - Segment within the boundaries of 		SE1(C1)

Marmora Wildlife Management Area

(Sea Isle City) - Segment outside the boundaries of 		SE1

Marmora Wildlife Management Area

BIG GRAVELING CREEK (Great Bay) - Entire length			SE1(C1)

BIG GREAVES CREEK

(MacNamara) - Segment of the Creek outside the 		SE1

boundaries of MacNamara Wildlife Management Area

(MacNamara) - Creek and tributaries within the boundaries 	SE1(C1)

of MacNamara Wildlife Management Area

BIG THOROFARE

(Tuckerton) - Source to boundary of Great Bay Blvd. 		SE1

Wildlife Management Area

(Tuckerton) - Segment within the boundaries of Great 	SE1(C1)

Bay Blvd. Wildlife Management Area

BLUEFISH BROTHERS (Stone Harbor) - Entire length		SE1(C1)

BLUEFISH CREEK (Stone Harbor) - Entire length			SE1(C1)

BOG BRANCH CREEK (Middletown) - Entire length			SE1(C1)

BRIGANTINE (Brigantine National Wildlife Refuge) - All waters 
FW2-NT/SE1(C1)

within the boundaries of the Brigantine National Wildlife Refuge

BRISBANE LAKE

(Allaire State Park) - The Lake and its tributaries within 	FW2-NT(C1)

the boundaries of Allaire State Park, except Mill Run, which is listed
separately, and the tributary described separately below

(Allaire State Park) - The easterly tributary to Mill Run 	FW1

upstream of Brisbane Lake, located entirely within the Allaire State
Park boundaries

(Mill Run) - Mill Run from its source to Brisbane Lake		FW2-NT(C1)

(Mill Run) - Mill Run from the outlet of Brisbane Lake 		FW2-NT(C1)

to the Manasquan River 

BROAD CREEK (New Gretna) - Entire length				SE1(C1)

BROAD THOROFARE

(Longport) - South of Rt. 152					SE1

(Longport) - North of Rt. 152					SE1(C1)

BROTHERS CREEK (Burleigh) - Entire length				SE1(C1)

CABBAGE THOROFARE (Great Bay) - Entire length			SE1(C1)

CEDAR BRIDGE BRANCH (Lakewood) - Entire length		FW2-NT

CEDAR CREEK

(Manahawkin) - Source to boundaries of the 			FW2-NT/SE1

Manahawkin Wildlife Management Area

(Manahawkin) - Creek and tributaries within the 		FW2-NT/SE1(C1)

boundaries of the Manahawkin Wildlife Management Area

CEDAR CREEK

(Cedar Crest) - Source to the boundaries of the 		PL

Pinelands Protection and Preservation Area at the Garden State Parkway,
except branches described separately below

(Berkeley) - Garden State Parkway to Barnegat Bay		FW2-NT/SE1

(Greenwood Forest) - Webbs Mill Branch and tributaries 	FW1

located entirely within the boundaries of Greenwood Forest Wildlife
Management Area

(Greenwood Forest) - Chamberlain's Branch from its 		FW1

origins to a point 1000 feet west of Route 539

(Greenwood Forest) - Those portions of the tributaries		FW1

to Chamberlain's Branch originating and wholly contained within the
boundaries of the Greenwood Forest Wildlife Management Area

CEDAR HAMMOCKS CREEK (English Creek Landing) - 		SE1(C1)

Entire length

CEDAR RUN

(Stafford) - Source to the boundaries of the Pinelands		PL

Protection and Preservation Area at the Garden State Parkway

(Cedar Run) - Garden State Parkway to the boundaries	FW2-NT/SE1

of the Barnegat National Wildlife Refuge

(Barnegat) - National Wildlife Refuge boundaries to 		FW2-NT/SE1(C1)

Barnegat Bay

CEDAR SWAMP CREEK

(Cedar Spring) - Entire length, except segment described 	FW2-NT/SE1

separately below

(Marmora) - Creek and tributaries within the boundaries 	FW2-NT/SE1(C1)

of the MacNamara Wildlife Management Area

CHAMBERLAIN BRANCH - See CEDAR CREEK

CHANNEL CREEK (Barnegat Bay) - Entire length			SE1(C1)

CHARLEY CREEK (Marmora) - Entire length				FW2-NT/SE1(C1)

CLEAR STREAM (JACKSON) - Entire length				FW2-TM

COLLINS TIDE PONDS (Barnegat)					FW2-NT/SE1(C1)

COMMANDO CREEK (Marmora) - Entire length			SE1(C1)

CRANBERRY BROOK (Monmouth) - Entire length			FW2-NT/SE1

DAVENPORT BROOK

(Berkeley) - Source to the boundaries of the Pinelands 	PL

Protection and Preservation Area at the Penn Central railroad tracks

(Toms River) - Railroad tracks to confluence with 		FW2-NT

Wrangel Brook

DEEP CREEK (Herbertsville) - Entire length				FW2-NT

DEEP RUN (Wharton) - Run and tributaries from their sources to 	FW1

Springer's Brook

DICKS BROOK (Larrabee's Crossing) - Entire length			FW2-NT

DINNER POINT CREEK (Staffordsville) - Entire length		SE1(C1)

DOCK THOROFARE (Northfield) - Entire length			SE1(C1)

DOVE MILL BRANCH - See TOMS RIVER 

EDWARD CREEK

(Ocean City) - Source to the boundary of Marmora 		SE1

Wildlife Management Area

(Ocean City) - Boundary of Marmora Wildlife 			SE1(C1)

Management Area to Horn Creek

FALKENBURG BRANCH - See BASS RIVER

FLAT CREEK (Marmora) - Entire length					FW2-NT/SE1(C1)

FLATTERAS CREEK (Beach Haven Heights) - Entire length		SE1(C1)

FORKED RIVER

(Lacey) - River and branches from their sources to the 	PL

boundaries of the Pinelands Protection and Preservation Area at the
Garden State Parkway

(Forked River) - Garden State Parkway to Barnegat Bay	FW2-NT/SE1

FORTESCUE (Fortescue) - All waters within the Fortescue 	
FW2-NT/SE1(C1)

Wildlife Management Area 

GIBSON CREEK

(Gibson Landing) - Entire length, except segment 		PL

described below

(Marmora) - Segment and tributaries within the 		FW2-NT/SE1(C1)

MacNamara Wildlife Management Area

GO THROUGH CREEK

(Burleigh) - Entire length, except segment described 		SE1

below

(Burleigh) - Segment within the boundaries of the 		SE1(C1)

Marmora Wildlife Management Area

GOING THROUGH CREEK (English Creek Landing)			SE1(C1)

GREAT BAY (Brigantine) - All waters of the Bay and all natural 
FW2-NT/SE1(C1)

waterways which are tributary to the Bay and all waters, including both
natural and manmade channels and ponds within the boundaries of the
Brigantine National Wildlife Refuge and the Great Bay Wildlife
Management Area

GREAT EGG HARBOR RIVER

(Berlin) - Source to confluence with Tinker Branch		FW2-NT

(Berlin) - Tinker Branch, the River from its confluence 		PL

with Tinker Branch, and all tributaries within the Pinelands Protection
and Preservation Area, downstream to the boundary at the Rt. 40 bridge
in Mays Landing	

(Winslow) - All tributaries or segments of tributaries 		FW2-NT

outside of the boundaries of the Pinelands Protection and Preservation
Area,downstream to Rt. 40 at Mays Landing

(Mays Landing) - Rt. 40 bridge to Great Egg Harbor, 		FW2-NT/SE1

except those tributaries described separately below

(Mays Landing) - All tributaries or segments of tributaries 	PL

within the boundaries of the Pinelands Protection and Preservation Areas

(Egg Harbor) - Tributaries and all other waters within 		FW2-NT/SE1(C1)

MacNamara Wildlife Management Area, except tributary described below

(Tuckahoe) - Stream adjacent to and north of Hawkin's 	FW1

Creek, and its tributaries, from their origins to the point where the
influence of impoundment begins

GREAT SOUND (Avalon) - All waters within Great Sound 		SE1(C1)

State Park

GREAT THOROFARE

(Ventnor) - West of Rt. 40						SE1(C1)

(Ventnor) - East of Rt. 40						SE1

GRISCOM CREEK (Gibson Landing) - Entire length			FW2-NT/SE1(C1)

GUNNING RIVER

(Barnegat) - Entire length, except segment described 		FW2-NT/SE1

below

(Barnegat) - Stream and tributaries within the boundaries 
FW2-NT/SE1(C1)

of Barnegat National Wildlife Refuge

HALFWAY CREEK

(Middletown) - Source to the boundary of the MacNamara 	FW2-NT/SE1

Wildlife Management Area

(MacNamara) - Creek and tributaries within the boundaries 	SE1(C1)

of the MacNamara Wildlife Management Area

HARRY POND (Barnegat) 							FW2-NT/SE1(C1)

HATFIELD CREEK (Beach Haven Heights) - Entire length		SE1(C1)

HAWKINS CREEK

(Tuckahoe) - Source to the point where the influence of 	FW1

impoundment begins

(Tuckahoe) - Downstream of the influence of impoundment	SE1(C1)

HAY STACK BROOK (Howell) - Entire length 				FW2-NT

HOSPITALITY CREEK (Longport) - Entire length			SE1(C1)

JACOVY CREEK (Stone Harbor) - Entire length 			SE1(C1)

JAKES BRANCH

(Berkeley) - Source to the boundaries of the Pinelands 	PL

Protection and Preservation Area at the Garden State Parkway

(Beachwood) - Garden State Parkway to Toms River		FW2-NT/SE1

JAY CREEK 									SE1(C1)

JIMMIES CREEK

(Great Bay) - Source to the boundary of Great Bay 		SE1(C1)

Wildlife Management Area

(Parkers Landing) - Segments of the Creek outside the 	SE1

boundaries of Great Bay Wildlife Management Area

JOSH CREEK (Stone Harbor) - Entire length				SE1(C1)

JUDIES CREEK

(Great Bay) - Source to widening of creek 			SE1

(Great Bay) - Widening of creek to mouth 			SE1(C1)

JUMPING BROOK (Neptune) - Entire length				FW2-NT/SE1

KNOLL POND (Barnegat)							FW2-NT/SE1(C1)

LAKES BAY (Ventnor)							SE1(C1)

LAKES CHANNEL (Ventnor) - Entire length				SE1(C1)

LITTLE GREAVES CREEK (MacNamara) - Entire length		SE1(C1)

LITTLE SCOTCH BONNET

(Stone Harbor) - Entire length, except segment described 	SE1

below

(Stone Harbor) - Segment within the boundaries of 		SE1(C1)

Marmora Wildlife Management Area

LITTLE THOROFARE (Tuckerton) - Entire length			SE1(C1)

LONG BROOK (JACKSON) - Entire length				PL

LONG POINT CREEK (Marmora) - Entire length			FW2-NT/SE1(C1)

LONG SWAMP BROOK

(Squankum) - Entire length, except segment within the 	FW2-NT

boundaries of Allaire State Park

(Allaire) - Segment within the boundaries of Allaire 		FW2-NT(C1)

State Park

LOWER LONG REACH (Stone Harbor) - Entire length		SE1(C1)

LUDLAM CREEK (Marmora) - Entire length				SE1(C1)

MAIN MARSH CREEK (Brigantine) - Entire length 			SE1(C1)

MANAHAWKIN CREEK

(Manahawkin) - Source to the boundaries of 			FW2-NT/SE1

Manahawkin Wildlife Management Area

(Manahawkin) - Within the boundaries of the Wildlife 		FW2-NT/SE1(C1)

Management Area

MANASQUAN RIVER 

  MAIN STEM

(Freehold) - Source to Rt. 9 bridge, except tributaries 		FW2-NT

described separately under Tributaries, below

(Farmingdale) - Rt. 9 bridge to the "Narrows" in the 		FW2-TM

vicinity of the Meadows Marina, except tributaries described separately
under Tributaries, below

(Meadows Marina) - The "Narrows" to surf waters		SE1

  TRIBUTARIES, MANASQUAN RIVER (See also 

BRISBANE LAKE)

(Adelphia) - Entire length						FW2-NT

(Allaire) - Those portions of the first and second 		FW1(tm)

southerly tributaries west of the Hospital Rd. which are located
entirely within the boundaries of Allaire State Park

(Brick) - Tributaries within the boundaries of Allaire 		FW2-TM(C1)

State Park and Manasquan River Wildlife Management Area, except those
designated FW1, above

(Freehold) - Tributaries within the boundaries of Turkey 	FW2-NT(C1)

Swamp Wildlife Management Area

MARMORA WILDLIFE MANAGEMENT AREA

(Strathmere) - All waters within the boundaries of 		FW2-NT/SE1(C1)

Marmora Wildlife Management Area

MARSH BOG BROOK

(Farmingdale) - Source to Yellow Brook Rd. 			FW2-NT

(Allaire) - Allaire State Park boundary at Yellow Brook Rd. 	FW2-NT(C1)

to Manasquan River

MASONS CREEK (Marmora) - Entire length				SE1(C1)

MCNEALS BRANCH - See TUCKAHOE RIVER

METEDECONK RIVER

  SOUTH BRANCH

(Lakewood) - Entire length, except segment described 	FW2-NT

below

(Turkey Swamp) - Tributaries within the boundaries of 	FW2-NT(C1)

Turkey Swamp Wildlife Management Area

  NORTH BRANCH METEDECONK RIVER 

(Freehold) - Source to Aldrich Rd., except segment 		FW2-NT

described below

(Turkey Swamp) - River and tributaries within the 		FW2-NT(C1)

boundaries of Turkey Swamp Wildlife Management Area

(Lakewood) - Aldrich Rd. to Lanes Mills 				FW2-TM

(Brick) - Lanes Mills to confluence with Metedeconk 		FW2-NT

River, South Branch

  MAIN STEM METEDECONK RIVER

(Brick) - Confluence of North and South branches to 		FW2-NT/SE1

Barnegat Bay

MIDDLE RIVER

(Tuckahoe) - Entire length, except the segment described 	FW2-NT/SE1

below

(Middletown) - Segment within the boundaries of 		FW2-NT/SE1(C1)

MacNamara Wildlife Management Area

MILE THOROFARE (Brigantine) - Entire length				SE1(C1)

MILL RUN (Allaire) - See BRISBANE LAKE

MINGAMAHONE BROOK

  MAINSTEM

(Farmingdale) - Entire length, except segment 			FW2-TM

described below

(Allaire State Park) - Brook and tributaries within the 		FW2-TM(C1)

boundaries of Allaire State Park

  EAST BRANCH

(Farmingdale) - Source to confluence with mainstem 		FW2-NT

north of Farmingdale

MIRY RUN (MacNamara) - Entire length 				FW2-NT/SE1(C1)

MOTT CREEK (Brigantine) - Entire length 				SE1(C1)

MUD CREEK (MacNamara) - Entire length 				SE1(C1)

MUDDY FORD BROOK (Larrabee's Crossing) - Entire length	FW2-TM

MULBERRY THOROFARE (Northfield) - Entire length			SE1(C1)

MULLICA RIVER

(Berlin) - Source to Pinelands Protection and 			PL

Preservation Area boundaries at the Garden State Parkway, except
branches and tributaries described below

(Wharton) - Stream in the southeasterly corner of the 		FW1

Wharton State Forest located between Ridge Rd. and Seaf Weeks Rd.,
downstream to the boundaries of the Wharton State Forest

(Wharton) - Gun Branch from its headwaters to US Rt. 206	FW1

(New Gretna) - River and tributaries from the Pinelands 	SE1(C1)

Protection and Preservation Area boundary to Great Bay

(Wharton) - Brooks and tributaries between and 		FW1

immediately to the west of Tylertown and Crowleytown, from their
headwaters to the head of tide at mean high water

NARROWS CREEK (Middletown) - Entire length 			SE1(C1)

NORTH CHANNEL POND (Stone Harbor)				FW2-NT/SE1(C1)

OLDMAN CREEK (Stone Harbor) - Entire length 			SE1(C1)

OTTER CREEK (Middletown) - Entire length 				SE1(C1)

OYSTER CREEK

(Brookville) - Source to the boundaries of the Pinelands 	PL

Protection and Preservation Area at the Garden State Parkway

(Forked River) - Garden State Parkway to Barnegat Bay	FW2-NT/SE1

OYSTER CREEK (Great Bay) - Entire length 				SE1(C1)

REEVY BRANCH - See SHARK RIVER

RING ISLAND CREEK (Stone Harbor) - Entire length			SE1(C1)

RISLEY CHANNEL (Margate) - Entire length 				SE1(C1)

ROUNDABOUT CREEK (New Gretna) - Entire length 			SE1(C1)

SALT CREEK (Stone Harbor) - Entire length 				SE1(C1)

SCULL BAY (Linwood)							SE1(C1)

SEDGE CREEK (MacNamara) - Entire length				SE1(C1)

SHARK CREEK (Stone Harbor) - Entire length 				SE1(C1)

SHARK RIVER

(Colts Neck) - Source to Rt. 33					FW2-NT

(Neptune) - Rt. 33 to Brighton Ave. bridge, Glendola		FW2-TM/SE1

(Glendola) - Brighton Ave. bridge to Atlantic Ocean		FW2-NT/SE1

  TRIBUTARY

REEVY BRANCH (Reevytown) - Source to confluence 	FW2-NT

with Shark River

SHELL THOROFARE (Wildwood Gables) - Entire length		SE1(C1)

SHELTER ISLAND BAY (Margate) 					SE1(C1)

SHELTER ISLAND WATERS (Margate) - Entire length		SE1(C1)

SKIT BRANCH - See BATSTO RIVER

SOD THOROFARE (Linwood) - Entire length				SE1(C1)

SOUTHEAST CREEK (Stone Harbor) - Entire length 			SE1(C1)

SQUANKUM BROOK

(Squankum) - Entire length, except segment described 	FW2-NT

below

(Allaire) - Segment within Allaire State Park			FW2-NT(C1)

STEELMAN BAY (Somers Point) 						SE1(C1)

SWAN POND (Marmora) 							FW2-NT/SE1(C1)

SWAN POND RACE (Marmora) - Entire length				FW2-NT/SE1(C1)

TAUGH CREEK

(Whitesboro) - Entire length, except segment described 	SE1(C1)

below

(Whitesboro) - Portions outside the boundaries of 		SE1

Marmora Wildlife Management Area

TIMBER SWAMP BROOK (Oak Glen) - Entire length			FW2-NT

TINKER BRANCH - See GREAT EGG HARBOR RIVER

TITMOUSE BROOK (Howell) - Entire length 				FW2-TM

TOMMYS BRANCH - See BASS RIVER 

TOMS RIVER

  MAIN STEM

(Holmeson) - Source to Rt. 528 bridge, Cassville except 	FW2-NT

those tributaries described separately under Tributaries below

(Van Hiseville) - Rt. 528 bridge to Rt. 547 bridge in 		PL(tm)

Whitesville, except tributaries described separately, under Tributaries
below

(Whitesville) - Rt. 547 bridge to Pinelands Protection and 	PL(tm)

Preservation Area boundaries at the NJ Central Railroad tracks, except
tributaries described separately, under Tributaries below

(Manchester) - NJ Central Railroad tracks to Rt. 571 		FW2-TM

bridge, except tributaries described separately, 

under Tributaries below

(Toms River) - Rt. 571 bridge to Barnegat Bay, except 	FW2-NT/SE1

tributaries described separately, under Tributaries below

  TRIBUTARIES, TOMS RIVER 

(Holmeson) - Tributaries within the boundaries of the 		PL

Pinelands Protection and Preservation Area 

(Van Hiseville) - All tributaries outside the boundaries 		FW2-TM

of the Pinelands Protection and Preservation Area which enter the River
between the Rt. 528 bridge, Cassville, and the Rt. 547 bridge,
Whitesville, except Dove's Mill Branch described separately below

(Toms River) - All tributaries within the  boundaries of the 	PL

Pinelands Protection and Preservation Area

(Archer's Corners) - All tributaries outside the boundaries 	FW2-NT(C1)

of the Pinelands Protection Area and within the boundaries of Colliers
Mills Wildlife Management Area

  DOVE'S MILL BRANCH

(Van Hiseville) - Entire length, except the segment 		FW2-NT

described separately below

(Holmansville) - Stream and tributaries within Butterfly 	FW2-NT(C1)

Bogs Wildlife Management Area 

  MAPLE ROOT BRANCH (Jackson) - Source to confluence 		PL

with Toms River

TUCKAHOE LAKE (Tuckahoe) 						FW2-NT(C1)

TUCKAHOE RIVER

(Milmay) - Source to Pinelands Protection and 			PL

Preservation Area boundary at Rt. 49

(Head of River) - McNeals Branch and the River within the 
FW2-NT/SE1(C1)

boundaries of the Peaselee Wildlife Management Area, except tributaries
within the boundaries of the Pinelands Protection and Preservation Area,
described separately below

(Head of River) - Tributaries within the Pinelands 		PL

Protection and Preservation Area boundaries

(Tuckahoe) - Edge of Fish and Wildlife Management 		FW2-NT/SE1(C1)

Area at confluence with Warners Mill Stream to Great Egg Harbor, except
segment described separately below 

(Tuckahoe) - River, tributaries and all other waters within 
FW2-NT/SE1(C1)

boundaries of the MacNamara Wildlife Management Area

TULPEHOCKEN CREEK

(Wharton) - Creek and tributaries from their origin to the 	FW1

confluence with Featherbed Branch

(Wharton) - The westerly tributaries and those natural 	FW1

ponds within the lands bounded by Hawkins (Bulltown-Hawkins) Rd.,
Hampton Gate (Tuckerton) Rd., and Sandy Ridge Rd.

TURTLE GROUND CREEK (Jeffers Landing) - Entire length		SE1(C1)

TURTLE GUT (Ventnor) - Entire length 					SE1(C1)

WADING RIVER 

(Chatsworth) - Entire length, except tributaries described 	PL

separately below

(Greenwood Forest) - Westerly tributary to Howardsville 	FW1

Cranberry Bog Reservoir and other tributaries located entirely within
the boundaries of the Greenwood Forest Wildlife Management Area

WARNERS MILL STREAM

(Head of River) - Source to Pinelands Protection and 		PL

Preservation Area boundary at Aetna Dr.

(Head of River) - Aetna Dr. to boundary of the Peaselee 	FW2-NT/SE1

Wildlife Management Area 

(Head of River) - Within the boundaries of the Peaselee 	FW2-NT/SE1(C1)

Wildlife Management Area to the Tuckahoe River 

WEBBS MILL BRANCH - See CEDAR CREEK

WIGWAM CREEK

(Great Bay) - Source to Rt. 9 					FW2-NT/SE1

(Great Bay) - Rt. 9 to Mott Creek 					SE1(C1)

WINTER CREEK (New Gretna) - Entire length 				SE1(C1)

WHIRLPOOL CHANNEL (Margate) - Entire length 			SE1(C1)

WORLDS END CREEK (New Gretna) - Entire length 			SE1(C1)

WRANGLE BROOK

(Keswick Grove) - Entire length, except segment 		FW2-NT/SE1

described below

(Whiting) - Brook and tributaries within Whiting Wildlife 	FW2-NT(C1)

Management Area 

WRANGLE CREEK (Forked River) - Entire length and all waters 
FW2-NT/SE1(C1)

within Forked River Game Farm

WRECK POND BROOK (Wall) - Entire length 				FW2-NT

(d)  The surface water classifications in Table 2 are for waters of the
Delaware River Basin:

TABLE  2

Waterbody 									Classification

ALEXAUKEN CREEK (Lambertville) - Entire length			FW2-TM

ALLAMUCHY CREEK (Allamuchy) - Entire length 			FW2-NT(C1)

ALLAMUCHY POND (Allamuchy)						FW2-NT(C1)

ALLAMUCHY POND TRIBUTARIES (Allamuchy) - All tributaries 	FW1

that are located entirely within the boundaries of Allamuchy State Park
and that flow into Allamuchy Pond

ALLOWAY CREEK (Alloways) - Entire length 				FW2-NT/SE1

ALMS HOUSE BROOK

(Hampton) - Source to, but not including, County 		FW2-TM

Farm Pond

(Frankford) - County Farm Pond to Paulins Kill			FW2-NT

ANDOVER JUNCTION BROOK (Andover) - Entire length 		FW2-TM

ASHROE LAKE (Stokes State Forest)					FW2-NT(C1)

ASHROE LAKE TRIBUTARIES

(Stokes State Forest) -Tributary to the Lake from 		FW2-TP(C1)

Deer Lake and portion of southernmost tributary to Ashroe Lake outside
of the Stokes State Forest boundary

(Stokes State Forest) - Southernmost tributary to the 		FW1(tp)

Lake from its source to the Stokes State Forest boundary

ASSISCUNK CREEK (Burlington) - Entire length			FW2-NT

ASSUNPINK CREEK 

(Trenton) - Source to confluence with the Delaware 		FW2-NT

River, except segments described separately below

(Roosevelt) - Creek and those tributaries within the 		FW2-NT(C1)

boundaries of the Assunpink Wildlife Management Area

(Quaker Bridge) - Portions of the creek within the 		FW2-NT(C1)

boundaries of Van Ness Refuge

BALDRIDGE CREEK

(Salem Creek) - Entire length, except segments 		FW2-NT/SE1(C1)

described below

(Salem Creek) - Segments outside the boundaries of the 	FW2-NT/SE1

Supawna National Wildlife Refuge

BARKERS MILL BROOK (Independence) - Entire length		FW2-TP(C1)

BAY PONDS (Egg Island) 							FW2-NT/SE1(C1)

BEADONS CREEK (Fortescue) - Entire length				SE1(C1)

BEAR BROOK (Johnsonburg) - Entire length 				FW2-TP(C1)

BEAR CREEK

(Johnsonburg) - Mud Pond to the Erie-Lackawanna 		FW1(tm)

Railroad trestle north of Johnsonburg

(Frelinghuysen) - Erie-Lackawanna Railroad trestle 		FW2-TM

to confluence with Pequest River

BEATTY'S BROOK (Penwell) - Entire length 				FW2-TP(C1)

BEAVER BROOK (Hope) - Entire length 				FW2-NT

BEAVER BROOK (Jefferson) - Source to, but not including, 		FW2-NT

Lake Shawnee

BEAVERDAM BRANCH

(Glassboro) - Source to boundary of the Glassboro 		FW2-NT

Wildlife Management Area

(Glassboro) - Within the boundaries of Glassboro 		FW2-NT(C1)

Wildlife Management Area

BEERSKILL

(High Point State Park) - Source to boundary of High Point 	FW1(tp)

State Park at 41 ADVANCE \u4 o ADVANCE \d4 15'48" N, 74 ADVANCE \u4 o
ADVANCE \d4 45'49" W

(Shaytown) - Boundary of High Point State Park to 		FW2-TP(C1)

confluence with Little Flat Brook

BIG FLAT BROOK

(Montague) - Sawmill Pond to confluence with Parker 		FW2-NT(C1)

Brook, except segments described under the listing for Flat Brook, below

(Sandyston) - Confluence with Parker Brook, through 		FW2-TP(C1)

the Blewitt Tract, to the confluence with Flat Brook, except tributaries
described under the listing for Flat Brook, below

(Tuttles Corner) - Outlet stream from Lake Ashroe to 		FW2-TP(C1)

its confluence with Big Flat Brook

BIG TIMBER CREEK (Westville) - Entire length			FW2-NT

BLACKBIRD GUT (Newport) - Entire length 				SE1(C1)

BLACKS CREEK (Bordentown) - Entire length 				FW2-NT

BLAIR CREEK

(Hardwick) - Source to Bass Lake 				FW2-NT

(Hardwick Center) - Bass Lake outlet to Paulins Kill		FW2-TM

BOILER DITCH (Egg Island) - Entire length 				FW2-NT/SE1(C1)

BRASS CASTLE CREEK (Brass Castle) - Entire length		FW2-TP(C1)

BROOKALOO SWAMP (Hope) - Entire length 				FW2-TM

BUCKHORN CREEK (Hutchinson) - Entire length 			FW2-TP(C1)

BUCKS DITCH (Mad Horse Creek) - Entire length 			SE1(C1)

BUCKSHUTEM CREEK

(Centre Grove) - Entire length, except segments 		FW2-NT

described separately below

(Edward G. Bevan) - Creek and tributaries within the 		FW2-NT(C1)

boundaries of Edward G. Bevan Wildlife Management Area, except those
tributaries described separately below

(Edward G. Bevan) - Joshua and Pine Branches to their 	FW1

confluence with Buckshutem Creek

CAT GUT (Mad Horse Creek) - Entire length 				SE1(C1)

CEDAR BRANCH (Manumuskin River) - Source to 			FW1

Manumuskin River 

CEDAR BRANCH (Edward G. Bevan) - Entire length			FW1

CEDAR BRANCH (Edward G. Bevan) - See NANTUXENT CREEK

CEDAR CREEK

(Dividing Creek Station) - Entire length, except 			FW2-NT

portions described separately below

(Edward G. Bevan) - Those tributaries to Cedar Creek 	FW1

that originate in and are located entirely within the boundaries of
Edward G. Bevan Wildlife Management Area

CEDARVILLE POND (Cedarville)						FW2-NT(C1)

CHERRY TREE CREEK (Mad Horse Creek) - Entire length		SE1(C1)

CLARKS POND (Bridgeton) 						FW2-NT(C1)

CLEARVIEW CREEK (Hampton) - Source to Alms House Brook	FW2-NT

CLINT MILLPOND (Beaver Swamp) 					FW2-NT(C1)

CLOVE (MILL) BROOK

(Montague) - Lake Marcia outlet to State line, except 		FW2-TP(C1)

tributaries described below

(High Point State Park) - The second and third 			FW1(tp)

northerly tributaries to Clove Brook, the tributaries to Steeny Kill
Lake, and those tributaries downstream of Steeny Kill Lake that
originate in High Point State Park downstream to their confluence with
Clove Brook or to the High Point State Park Boundaries

(High Point State Park) - Those northerly tributaries to 	FW1(tp)

Mill Brook that are located due west of Steeny Kill Lake, within the
boundaries of High Point State Park

COHANSEY RIVER (Bridgeton) - Entire length 			FW2-NT/SE1

COOPER BRANCH - See RANCOCAS CREEK 

COOPER RIVER (Camden) - Entire length 				FW2-NT

COOPERMINE BROOK (Pahaquarry) - Entire length 			FW1

COURTENY PONDS (Egg Island) 					FW2-NT/SE1(C1)

CRANBERRY LAKE (Byram) 						FW2-TM(C1)

CRANBERRY LAKE OUTLET STREAM 

(Byram) - Entire length within Cranberry Lake State Park	FW2-NT(C1)

(Byram) - Stream outside of Cranberry Lake State Park	FW2-NT

CRISS BROOK (Stokes State Forest) - Entire length within 		FW1(tp)

the boundaries of Stokes State Forest

CROSSWICKS CREEK (Bordentown) - Entire length 			FW2-NT

CROW CREEK (S. Dennis) - Entire length 				FW2-NT/SE1(C1)

CULVER'S CREEK (Frankford) - Entire length 				FW2-TM

CULVER'S LAKE (Frankford)						FW2-TM

DEER LAKE (Sandyston)							FW2-NT(C1)

DEER PARK BRANCH - See RANCOCAS CREEK 

DEER PARK POND

(Allamuchy) - Pond and tributaries to the pond within 		FW2-NT(C1)

Allamuchy State Park, except those tributaries classified as FW1, below

(Allamuchy) - All tributaries to the Pond and to its outlet 	FW1

stream that are located entirely with the boundaries of Allamuchy State
Park

(Allamuchy) - Deer Park Pond outlet stream downstream 	FW2-TM(C1)

to Musconetcong River

DELAWANNA CREEK

(Delaware) - Source downstream to, but not including,		FW2-TM

Delaware Lake

(Delaware) ( Delaware Lake dam downstream to 		FW2-TP(C1)

Delaware River, including tributaries

DELAWARE AND RARITAN CANAL (Lambertville) - Entire 		FW2-NT

length

DELAWARE RIVER

  MAIN STEM (Interstate Waters - Classifications from 

Delaware River Basin Commission (DRBC))

(State Line) - That portion of DRBC's Zone 1C from the 	Zone 1C

New York-New Jersey state line to the proposed axis of the Tocks Island
Dam at River Mile 217.0

(Tocks Island) - Proposed axis of Tocks Island Dam at 	Zone 1D

River Mile 217.0 to the mouth of the Lehigh River at Easton,
Pennsylvania, at River Mile 183.66

(Easton, Pa.) - Mouth of the Lehigh River at River Mile 	Zone 1E

183.66, to the head of tide at the Trenton-Morrisville Toll Bridge,
Trenton at River Mile 133.4

(Trenton) - Head of tide at the Trenton-Morrisville Bridge, 	Zone 2

Trenton, River Mile 133.4 to below the mouth of Pennypack Creek,
Pennsylvania at River Mile 108.4

(Philadelphia) - River Mile 108.4 to below the mouth of 	Zone 3

Big Timber Creek, New Jersey, at River Mile 95.0

(Gloucester) - River Mile 95.0 to the Pennsylvania-		Zone 4

Delaware state line at River Mile 78.8

(Marcus Hook) - Pennsylvania-Delaware state line at 		Zone 5

River Mile 78.8 to Liston Pt., Delaware at River Mile 48.2

(Liston Point) - Delaware Bay from Liston Point, 		Zone 6(C1)

Delaware at River Mile 48.2 to River Mile 0.0 at the intersection of the
centerline of the navigation channel and a line between Cape May Light
and the tip of Cape Henlopen, Delaware

  TRIBUTARIES, DELAWARE RIVER

(Holland) - Entire length 						FW2-TP(C1)

(Port Jervis) - Unnamed or unlisted direct tributaries 		FW2-NT

that are north of Big Timber Creek, are outside of the Pinelands
Protection and Preservation Areas, and are not mapped as C1 waters by
the Department

(Knowlton) - Source, north of Hope-Delaware Road, 		FW2-TP(C1)

to confluence with the Delaware River 0.5 mile south of Ramseysburg

(Titusville) - Unnamed tributaries through Washington 	FW2-NT(C1)

Crossing State Park

(Brooklawn) - Unnamed or unlisted direct tributaries, 		FW2-NT/SE2

south of Big Timber Creek and north of Oldmans Creek, that are outside
of the Pinelands Protection and Preservation Areas and are not mapped as
C1 waters by the Department

(Penns Grove) - Unnamed or unlisted direct tributaries, 	FW2-NT/SE1

south of and including Oldmans Creek, that are outside of the Pinelands
Protection and Preservation Areas and are not mapped as C1 waters by the
Department

(Pinelands) - All streams or segments of streams 		PL

which flow directly into the Delaware River, are within the boundaries
of the Pinelands Area and are not classified FW1 waters in this Table

DENNIS CREEK

(South Dennis) - Entire length, except segments 		FW2-NT/SE1

described below

(Woodbine) - All tributaries within the boundaries of the 	PL

Pinelands Protection and Preservation Areas



(Dennis Creek) - Segment of the Creek, all tributaries, 	FW2-NT/SE1(C1)

and all other surface waters within the boundaries of the Dennis Creek
Wildlife Management Area

DEVILS GUT

(Mad Horse Creek) - Entire length, except tributaries 		SE1(C1)

described below

(Mad Horse Creek) - Tributaries outside the Mad Horse 	SE1

Creek Wildlife Management Area

DIVIDING CREEK

(Dividing Creek) - Entire length, except those segments 	FW2-NT/SE1

described below

(Edward G. Bevan) - Those segments of tributaries 		FW1

that are located entirely within the boundaries of the Edward G. Bevan
Wildlife Management Area

DIVISION CREEK (Dix) - Entire length					SE1(C1)

DOCTORS CREEK

(Red Creek) - Entire length, except segment described 	FW2-NT

below

(Imlaystown) - Segment within Imlaystown Lake 		FW2-NT(C1)

Wildlife Management Area

DONKEY'S CORNER BROOK (Delaware Water Gap) - 		FW1

Entire length

DRUMBO CREEK

(Dix) - Entire length, except segment described below		FW2-NT/SE1

(Dix) - Segment within the boundaries of Dix Wildlife 		FW2-NT/SE1(C1)

Management Area

DRY BROOK (Branchville) - Entire length				FW2-NT

DUCK POND (Swartswood)						FW2-NT(C1)

DUNNFIELD CREEK

(Del. Water Gap) - Source to Rt. I-80				FW1(tp)

(Del. Water Gap) - Rt. I-80 to Delaware River, except 		FW2-TP(C1)

tributaries described below

(Worthington) - All unnamed waters that are located 		FW1

entirely within the boundaries of the Worthington State Forest

EAST CREEK

(Dennis) - Source to boundaries of the Pinelands 		PL

Protection and Preservation Area except those portions described
separately below

(Belleplain) - A stream and tributary that originate 		FW1

just south of East Creek Mill Rd., 1.2+ miles north-northeast of Eldora
and are located entirely within the boundaries of Belleplain State
Forest

(Eldora) - Boundary of the Pinelands Protection 		FW2-NT/SE1

and Preservation Area to Delaware Bay except segment described
separately below

(Dennis Creek) - Segment within the boundaries of the 	FW2-NT/SE1(C1)

Dennis Creek Wildlife Management Area

ELDER GUT (Egg Island) - Entire length					FW2-NT/SE1(C1)

FIDDLERS CREEK (Titusville) - Entire length				FW2-TM

FISHING CREEK (Egg Island) - Entire length				FW2-NT/SE1(C1)

FISHING CREEK

(Canton) - Source to Mad Horse Creek Wildlife 		SE1

Management Area and all tributaries outside of the boundaries of Mad
Horse Creek Wildlife Management Area

(Mad Horse Creek) - Creek and tributaries within the 		SE1(C1)

boundaries of Mad Horse Creek Wildlife Management Area

FLAT BROOK

(Flatbrook-Roy) - Confluence of Big Flat Brook and 		FW2-TP(C1)

Little Flat Brook to the boundary of Flatbrook-Roy Wildlife Management
Area, except segments described below

(Flatbrook-Roy) - Brook within the boundaries of		FW2-TM(C1)

Flatbrook-Roy Wildlife Management Area

(Flatbrookville) - Flatbrook-Roy Wildlife Management 		FW2-TM

Area boundary to Delaware River, except segments described below

(Walpack) - Segment of the Brook within Walpack 		FW2-TM(C1)

Wildlife Management Area

(Stokes State Forest) - Two tributaries to Flat Brook 		FW1(tm)

which originate along Struble Road in Stokes State Forest to their
confluences with Flat Brook within the boundaries of Flatbrook-Roy
Wildlife Management Area

(High Point) - All surface water of the Flat Brook 		FW1

drainage area within the boundaries of High Point State Park and Stokes
State Forest, except the following waters:

1. Saw Mill Pond and Big Flat Brook downstream to the confluence with
Flat Brook;

2. Mashipacong Pond and its outlet stream (Parker Brook) to the
confluence with Big Flat Brook;

3. Lake Wapalanne and its outlet stream to the confluence with Big Flat
Brook;

4. Lake Ocquittunk and waters connecting it with Big Flat Brook;

5. Stony Lake and its outlet stream (Stony Brook) to the confluence with
Big Flat Brook;

6. Kittatinny Lake, that portion of its inlet stream outside the Stokes
State Forest boundaries, and its outlet stream, including the Shotwell
Camping Area tributary, to the confluence with Big Flat Brook;

7. Deer Lake and its outlet stream to Lake Ashroe;

8. Lake Ashroe, portions of its tributaries outside the Stokes State
Forest boundaries, and its outlet stream to the confluence with Big Flat
Brook;

9. Lake Shawanni and its outlet stream to its confluence with Flat
Brook;

10. Crigger Brook and tributary to its confluence with Big Flat Brook

(Del. Water Gap) - All tributaries to Flat Brook that flow 	FW1

from the Kittatiny Ridge and are located entirely within the boundaries
of the Delaware Water Gap National Recreation Area

FORKED BROOK (Stokes State Forest) - Entire length		FW2-TP(C1)

FURNACE (OXFORD) BROOK

(Oxford) - Source to railroad bridge at Oxford			FW2-TP(C1)

(Oxford) - Railroad bridge to Pequest River			FW2-NT

FURNACE LAKE (Oxford)							FW2-TM

GARDNERS LAKE (Andover)						FW2-TM

GOOSE POND (Mad Horse Creek)					SE1(C1)

GOSHEN CREEK

(Woodbine) - Entire length except segment described 	SE1

below

(Dennis Creek) - Segment and all tributaries within the 	SE1(C1)

Dennis Creek Wildlife Management Area

GRAVELLY RUN (Edward G. Bevan) - Downstream to the 		FW1

Edward G. Bevan Wildlife Management Area boundaries

HAINESVILLE POND (Hainesville)					FW2-NT(C1)

HAKIHOKAKE CREEK (Milford) - Entire length, including		FW2-TP(C1)

headwaters known as Little York Creek

  TRIBUTARIES

(Wydner) - Source to confluence with Hakihokake 		FW2-TP(C1)

Creek west of York Road

HALFWAY HOUSE BROOK (Franklin) - Entire length			FW2-TP(C1)

HANCES BROOK (Rockport) - Entire length				FW2-TP(C1)

HARIHOKAKE CREEK

(Alexandria) - Source to Rt. 519 bridge				FW2-NT

(Frenchtown) - Rt. 519 bridge to Delaware River		FW2-TM

HARRISONVILLE LAKE (Harrisonville)					FW2-NT(C1)

HATCHERY BROOK (Hackettstown) - Entire length			FW2-TM

HIGBEE BEACH (Higbee Beach Wildlife Management Area)		FW2-NT/SE1(C1)

All waters within the boundaries of Higbee Beach Wildlife Management
Area

HIGHS BEACH (Highs Beach) - All waters within the			FW2-NT/SE1(C1)

Wildlife Management Area south of Highs Beach

HONEY RUN (Hope) - Entire length					FW2-TM

HOPATCONG, LAKE (Hopatcong)					FW2-TM

ILLIF, LAKE (Andover)							FW2-TM

IMLAYSTOWN LAKE (Imlaystown)					FW2-NT(C1)

INDEPENDENCE CREEK

(Alphano) - Source to Alphano Rd.				FW2-TP(C1)

(Alphano) - Alphano Rd. to Pequest River			FW2-NT

INDIAN DITCH (Egg Island) - Entire length 				FW2-NT/SE1(C1)

ISLAND DITCH (Egg Harbor) - Entire length				FW2-NT/SE1(C1)

JACKSONBURG CREEK (Blairstown) - Entire length			FW2-TM

JACOBS CREEK (Hopewell) - Entire length				FW2-NT

JADE RUN (Lebanon State Forest)					FW1

JOSHUA BRANCH - See BUCKSHUTEM CREEK

KING POND (Egg Island)							SE1(C1)

KITTATINNY LAKE (Sandyston)						FW2-NT(C1)

KITTATINNY LAKE TRIBUTARY

(Stokes State Forest) - Source to boundary of Stokes 		FW1(tp)

State Forest

(Sandyston) - State Forest boundary to Kittatinny Lake	FW2-TP(C1)

KNOWLTON BROOK (Knowlton) - Entire length			FW2-TP(C1)

KURTENBACH'S BROOK (Waterloo) - Entire length			FW2-TP(C1)

KYMER BROOK (Andover) - Entire length				FW2-NT

LAHAWAY CREEK

(Prospertown) - Entire length, except tributaries described 	FW2-NT

separately below

(Colliers Mills) - All tributaries which originate in the 		FW1

Colliers Mills Wildlife Management Area north-northeast of Archers
Corners, from their sources to the boundaries of the Colliers Mills
Wildlife Management Area

LAKE - See listing under Name

LITTLE EASE RUN

(Glassboro) - Entire length, except portion described 		FW2-NT

separately below

(Glassboro) - Run and tributaries within the Glassboro 	FW2-NT(C1)

Wildlife Management Area, except tributary described separately below

(Glassboro) - The portion of a branch of Little Ease 		FW1

Run situated immediately north of Stanger Avenue, and entirely within
the Glassboro Wildlife Management Area

(Glassboro) - The first and second easterly tributaries 		FW1

to Little Ease Run north of Academy Road

LITTLE FLAT BROOK

(High Point State Park) - Source to boundary of High 		FW1(tp)

Point State Park

(Layton) - State park boundary to, but not including, 		FW2-TP(C1)

tributary described below, to confluence with Big Flat Brook

(Flatbrook-Roy) - Tributary which originates north of 		FW1(tp)

Bevans-Layton Rd. downstream to the first pond adjacent to the Fish and
Game headquarters building

LITTLE SHABACUNK CREEK (Lawrence) - Entire length		FW2-NT

LITTLE SWARTSWOOD LAKE (Swartswood)				FW2-NT(C1)

LITTLE YORK CREEK (Little York) - Entire length			FW2-TP(C1)

LOCKATONG CREEK

(Kingwood) - Source to Idell Bridge				FW2-NT

(Raven Rock) - Idell Bridge to Delaware River			FW2-TM

LOGAN POND (Repaupo)							FW2-NT(C1)

LOMMASONS GLEN BROOK (Lommasons Glen) - Entire length	FW2-TP(C1)

LONG POND (Mad Horse Creek)						SE1(C1)

LONE TREE CREEK (Egg Island) - Entire length			SE1(C1)

LOPATCONG CREEK

(Allens Mills) - Source to Decker Rd. bridge			FW2-TP(C1)

(Herkers Hollow) - Decker Rd. bridge to Rt. 57 bridge		FW2-TM

(Phillipsburg) - Rt. 57 bridge to a point 560 feet (straight	FW2-TP(C1)

line distance) upstream of the Penn Central railroad track

(Phillipsburg) - From a point 560 feet (straight line		FW2-NT

distance) upstream of the Penn Central railroad track downstream to the
confluence with the Delaware River

  TRIBUTARY

(Uniontown) - Entire length						FW2-TP(C1)

LOWER BROTHERS CREEK (Egg Island) - Entire length		SE1(C1)

LOWER DEEP CREEK (Mad Horse Creek) - Entire length		SE1(C1)

LUBBERS RUN (Byram) - Entire length					FW2-TM

MAD HORSE CREEK

(Canton) - Source to the boundary of Mad Horse Creek 	FW2-NT/SE1

Wildlife Management Area and all tributaries outside the boundaries of
the Wildlife Management Area

(Mad Horse Creek) - Creek and all waters within the 		FW2-NT/SE1(C1)

Mad Horse Creek Wildlife Management Area

MALAPATIS CREEK

(Mad Horse Creek) - Entire length, except segment 		SE1(C1)

described below

(Mad Horse Creek) - Portions of the Creek beyond the 	SE1

boundaries of the Mad Horse Creek Wildlife Management Area

MANANTICO CREEK

(Millville) - Entire length, except segment described below	FW2-NT

(Manantico) - Segment within the boundaries of the 		FW2-NT(C1)

Manantico Ponds Wildlife Management Area

MANTUA CREEK (Woodbury) - Entire length				FW2-NT/SE2

MARCIA LAKE

(High Point State Park) - Entire Lake				FW2-TM(C1)

(High Point State Park) - Outlet stream from the Lake to 	FW2-TP(C1)

the confluence with Clove (Mill) Brook

MASHIPACONG POND (Montague)					FW2-NT(C1)

MASON CREEK

(Springville) - Entire length, except segment described 	FW2-NT

below

(Medford) - Segment within Medford Wildlife 			FW2-NT(C1)

Management Area

MASONS RUN

(Pine Hill) - Source to Little Mill Rd.				FW2-TP(C1)

(Lindenwold) - Little Mill Rd. to confluence with Big 		FW2-NT

Timber Creek

MAURICE RIVER

  MAIN STEM

(Willow's Grove) - Source to the boundary of the section 	FW2-NT

of Union Lake Wildlife Management Area north of Vineland

(Vineland) - Boundary of the Union Lake Wildlife 		FW2-NT(C1)

Management Area to confluence with Blackwater Branch

(Vineland) - Confluence with Blackwater Branch to 		FW2-NT/SE1

Delaware Bay, except tributaries described under Tributaries below

  TRIBUTARIES, MAURICE RIVER

(Willow's Grove) - Those portion of tributaries that are 	PL

within the boundaries of the Pinelands Protection and Preservation Area

(Vineland) - All tributaries within the boundaries of the 
FW2-NT/SE1(C1)

Union Lake Wildlife Management Area and within the Wildlife Management
Area that borders Delaware Bay

MCCORMICK POND (Egg Island)					FW2-NT/SE1(C1)

MACDONALD BRANCH - See RANCOCAS CREEK

MERRILL CREEK (Harmony) - Entire length, but not including 	FW2-TP(C1)

Merrill Creek Reservoir

MERRILL CREEK RESERVOIR (Harmony)				FW2-TM

MIDDLE BROTHERS CREEK (Egg Island) - Entire length		SE1(C1)

MIDDLE MARSH CREEK

(Dix) - All fresh waters which originate in and are located 	FW1

entirely within the boundaries of the Dix Wildlife Management Area

MILE BRANCH - Entire length						FW1

MILL BROOK (Montague) - See CLOVE BROOK

MILL BROOK (Broadway) - Entire length				FW2-TP(C1)

MILL CREEK

(Carmel) - Entire length, except segment described 		FW2-NT

below

(Union Lake) - Creek and tributaries within the boundaries 	FW2-NT(C1)

of the Union Lake Wildlife Management Area

MINE BROOK

(Mt. Olive) - Source to, but not including, Upper Mine 		FW2-TM

Brook Reservoir, downstream to Lower Mine Brook Reservoir outlet

(Mt. Olive) - Lower Mine Brook Reservoir outlet 		FW2-TP(C1)

downstream to Drakestown Road bridge

(Hackettstown) - Drakestown Road bridge downstream 	FW2-TM

to confluence with Musconetcong River

  TRIBUTARIES

(Drakestown) - Source downstream to, but not including, 	FW2-TP(C1)

Burd Reservoir

(Drakestown) - Burd Reservoir downstream to confluence 	FW2-TM

with Mine Brook

(Washington) - Entire length of tributary which joins 		FW2-TP(C1)

Mine Brook approximately 280 yards upstream of the confluence with the
Musconetcong River

MIRY RUN (Mercerville) - Entire length					FW2-NT

MOORE CREEK (Hopewell) - Entire length				FW2-TM

MOUNT MISERY BROOK

(Woodmansie) - Entire length, except segments 		PL

described below

  SOUTH BRANCH, MOUNT MISERY BROOK

(Lebanon State Forest) - All tributaries to the South 		FW1

Branch that are located entirely within the boundaries of Lebanon State
Forest

(Pasadena) - The two easterly branches of the Branch 	FW1

which are located entirely within the boundaries of the Pasadena
Wildlife Management Area

MOUNTAIN LAKE (Liberty)						FW2-TM

MOUNTAIN LAKE CREEK

(Liberty) - Source to Mountain Lake				FW2-TM

(White) - Mountain Lake dam to Pequest River			FW2-NT

MUDDY BROOK (Hope) - Entire length					FW2-NT

MUDDY CREEK

(Mad Horse Creek) - Entire length, except segments 		SE1 (C1)

described below

(Mad Horse Creek) - Segments outside of the boundaries 	SE1

of the Mad Horse Creek Wildlife Management Area

MUDDY RUN

(Elmer) - Entire length, except segments described 		FW2-NT

below

(Elmer) - Portion of the Run within Greenwood Pond 		FW2-NT(C1)

Wildlife Management Area

(Centerton) - Portion of the Run within Parvin State Park	FW2-NT(C1)

(Pittsgrove) - Portion of the run within Union Lake Wildlife 	FW2-NT(C1)

Management Area

MUD POND (Johnsonburg)						FW1

MUSCONETCONG RIVER

(Hackettstown) - Lake Hopatcong dam to Delaware 		FW2-TM

River, except tributaries described below

  TRIBUTARIES

(Anderson) - Entire length						FW2-TP(C1)

(Changewater) - Entire length					FW2-TP(C1)

(Deer Park Pond) - See DEER PARK POND

(Franklin) - Entire length						FW2-TP(C1)

(N. of Hackettstown) - Entire length				FW2-TM

(Lebanon) - Entire length						FW2-TP(C1)

(Port Murray) - Entire length					FW2-TP(C1)

(S. of Point Mtn.)							FW2-TP(C1)

(S. of Schooley's Mtn. Brook) - Entire length			FW2-TP(C1)

(Waterloo) - Tributary west of Kurtenbach's Brook from 	FW2-TP(C1)

source downstream to Waterloo Valley Road bridge

MUSKEE CREEK

(Port Elizabeth) - Source to boundary of Pinelands 		PL

Protection and Preservation Area, except segments described separately
below

(Peaselee) - The Middle Branch from its origin to the 		FW1

boundaries of the Peaselee Wildlife Management Area

(Peaselee) - Those portions of the tributaries to Slab 		FW1

Branch which are located entirely within the boundaries of the Peaselee
Wildlife Management Area

(Bricksboro) - Pinelands Protection and Preservation 		FW2-NT

Area boundaries to Maurice River

NANCY GUT

(Nantuxent) - Source to the boundary of Nantuxent Creek 	SE1(C1)

Wildlife Management Area

(Newport) - Stream and all tributaries outside of the 		SE1

boundaries of the Nantuxent Creek Wildlife Management Area

NANTUXENT CREEK

(Newport Landing) - Entire length, except segment 		FW2-NT/SE1

described below

(Nantuxent) - All waters within the boundaries of 		FW2-NT/SE1(C1)

Nantuxent Creek Wildlife Management Area

NEW WAWAYANDA LAKE (Andover)					FW2-TM

NISHISAKAWICK CREEK (Frenchtown) - Entire length		FW2-NT

OLDMANS CREEK

(Lincoln) - Entire length, except portion described below	FW2-NT/SE1

(Harrisonville) - Portion within Harrisonville Lake 		FW2-NT(C1)

Wildlife Management Area

OCQUITTUNK LAKE

(Stokes State Forest) - Entire lake				FW2-NT(C1)

(Stokes State Forest) - From the outlet of the Lake 		FW2-TP(C1)

to the confluence with Big Flat Brook

OCQUITTUNK LAKE TRIBUTARY (Stokes State Forest) -		FW1(tp)

Source to Ocquittunk Lake

ORANDAKEN CREEK

(Fortescue) - Source to boundary of Egg Island 		FW2-NT/SE1

Berrytown Wildlife Management Area

(Egg Island) - Creek and tributaries within the 			FW2-NT/SE1(C1)

boundaries of the Egg Island Berrytown Wildlife Management Area

PARGEY CREEK

(Gibbstown) - Entire length, except segment described 	FW2-NT/SE2

below

(Logans Pond) - Segment within the boundaries of 		FW2-NT/SE2(C1)

Logans Pond Wildlife Management Area

PARKER BROOK (Montague) - Entire length				FW2-TP(C1)

PARVIN LAKE (Parvin State Park)					FW2-NT(C1)

PATTYS FORK - See MAD HORSE CREEK

PAULINA CREEK (Paulina) - Entire length				FW2-TM

PAULINS KILL

  EAST BRANCH

(Andover) - Source to Limecrest quarry				FW2-NT(C1)

(Lafayette) - Limecrest quarry to confluence with Paulins 	FW2-TP(C1)

Kill, West Branch, except tributary described below

  TRIBUTARY EAST BRANCH

(Sussex Mills) - Entire length of tributary to the East 		FW2-NT(C1)

Branch at Sussex Mills

  WEST BRANCH (Newton) - Entire length				FW2-NT

  MAIN STEM

(Blairstown) - Confluence of East and West branches 		FW2-TM

to Rt. 15 bridge (bench mark 507)

(Hampton) - Rt. 15 bridge to Paulins Kill Lake dam		FW2-NT

(Paulins Kill Lake) - Paulins Kill Lake dam to Delaware 	FW2-TM

River, except tributaries described separately below

  TRIBUTARIES, MAIN STEM

(Blairstown) - Entire length of tributary east of Walnut 		FW2-TM

Valley

(Emmons Station) - Entire length					FW2-TP(C1)

(Stillwater) - Entire length						FW2-TM

(Stillwater Station) - Entire length					FW2-TP(C1)

PENNSAUKEN CREEK (Cinnaminson) - Entire length			FW2-NT

PEQUEST RIVER

(Tranquility) - Source to Tranquility bridge except 		FW2-TM

segments described below

(Whittingham) - Northwesterly tributaries, including 		FW1(tm)

Big Spring, located within the boundaries of the Whittingham Wildlife
Management Area, southwest of Springdale, from their origins to their
confluence with the Pequest River

(Whittingham) - Stream and tributaries within the 		FW2-TM(C1)

Whittingham Wildlife Management Area, except those classified as FW1,
above

(Vienna) - Tranquility bridge to Townsbury bridge		FW2-NT

(Townsbury) - Townsbury bridge to Delaware River, 		FW2-TM

except segment described below

(Pequest) - Segment and tributaries within the boundaries 	FW2-TM(C1)

of the Pequest Wildlife Management Area

  TRIBUTARIES

(Petersburg) - Headwaters and tributaries downstream 	FW2-TP(C1)

to Ryan Road bridge

PIERSONS DITCH (Egg Island) - Entire length				FW2-NT/SE1(C1)

PINE BRANCH - See BUCKSHUTEM CREEK

PLUM BROOK (Sergeantsville) - Entire length				FW2-TM

POHATCONG CREEK

  MAIN STEM

(Mansfield) - Source to Karrsville bridge				FW2-TP(C1)

(Pohatcong) - Karrsville bridge to Delaware River		FW2-TM

  TRIBUTARIES

(Greenwich) - Entire length						FW2-TP(C1)

(New Village) - Entire length					FW2-TP(C1)

(Willow Grove) - Entire length					FW2-TP(C1)

POND BROOK (Middleville) - Swartswood Lake outlet to 		FW2-NT

Trout Brook

POPHANDUSING BROOK

(Hazen) - Source downstream to Route 519 bridge		FW2-TP(C1)

(Belvidere) - Route 519 bridge downstream to confluence 	FW2-TM

with the Delaware River

RACCOON CREEK (Logan) - Entire length				FW2-NT/SE2

RANCOCAS CREEK

  NORTH BRANCH

(North Hanover) - Source to boundary of the Pinelands 	PL

Protection and Preservation Area at Pemberton

(Pemberton) - Boundary of the Pinelands Protection 		FW2-NT

and Preservation Area to the Delaware River, except tributaries
described below

(Pemberton) - Tributaries within the boundaries of the 	PL

Pinelands Protection and Preservation Areas

  SOUTH BRANCH RANCOCAS CREEK

(Southhampton) - Source to Pinelands Protection 		PL

and Preservation Area boundaries at Rt. 206 bridge south of Vincentown

(Vincentown) - Vincentown to Delaware River, except 		FW2-NT

tributaries described separately below

(Vincentown) - All tributaries within the Pinelands 		PL

Protection and Preservation Area

  COOPER BRANCH RANCOCAS CREEK

(Woodmansie) - Entire length, except portions described 	PL

separately, below

(Lebanon State Forest) - Branch and tributaries 		FW1

downstream to Pakim Pond, and tributaries to Cooper Branch located
entirely within the Lebanon State Forest boundaries

  DEER PARK BRANCH RANCOCAS CREEK

(Buckingham) - Stream and tributaries near Buckingham 	FW1

to confluence with Pole Bridge Branch

  MACDONALDS BRANCH RANCOCAS CREEK

(Woodmansie) - Entire length, except as described 		PL

separately below

(Lebanon State Forest) - Branch and tributaries located 	FW1

entirely within Lebanon State Forest

  SHINNS BRANCH RANCOCAS CREEK

(Lebanon State Forest) - Branch and tributaries 		FW1

located entirely within the boundaries of Lebanon State Forest, from
their sources to the forest boundary

(Lebanon Lake Estates) - Forest boundary to lake		PL

ROARING DITCH

(Heislerville) - Entire length, except segment described 	SE1

below

(Eldora) - Ditch and all tributaries within the Dennis 		SE1(C1)

Creek Wildlife Management Area boundaries

ROWANDS POND (Clementon) - Pond, inlet stream and outlet 	FW2-NT(C1)

stream within Rowands Pond Wildlife Management Area

RUNDLE BROOK (Del. Water Gap) - Source to Sussex 		FW1

County Route 615

SALEM RIVER (Salem) - Entire length					FW2-NT/SE1

SAMBO ISLAND BROOK (Del. Water Gap) - Entire length		FW1

SAMBO ISLAND POND (Del. Water Gap) 				FW1

SANDYSTON CREEK (Sandyston) - Entire length			FW2-TP(C1)

SAVAGES RUN (East Creek)

(Belleplain State Forest) - Entire length, except portions	PL

described separately, below

(Belleplain State Forest) - Those two tributaries and		FW1

portions thereof downstream of Lake Nummi and all tributaries to Lake
Nummi that are located entirely within the boundaries of Belleplain
State Forest

SAWMILL POND (High Point)						FW2-NT(C1)

SCHOOLEYS MTN. BROOK (Schooley's Mtn.) - Entire length	FW2-TP(C1)

SHABAKUNK CREEK (Ewing) - Entire length				FW2-NT

SHABBECONG CREEK (Washington) ( Entire length			FW2-TM

SHAWANNI CREEK

(Stokes State Forest) - Headwaters and tributaries		FW1(tp)

downstream to, but not including, Shawanni Lake

(Stokes State Forest) - Outlet of Shawanni Lake		FW2-TP(C1)

downstream to confluence with Flat Brook

SHAWANNI LAKE (Stokes State Forest)				FW2-NT(C1)

SHAWS MILL POND (Cedarville)						FW2-NT/SE1(C1)

  TRIBUTARIES

(Edward G. Bevan) - Cedar and Mile Branches to 		FW1

Shaw's Mill Pond

SHIMERS BROOK

(Millville) - Entire length, except those segments 		FW2-TP(C1)

designated FW1, below

(High Point) - That segment of Shimers Brook and all 		FW1 (tp)

tributaries within the boundaries of High Point State Park

SHINNS BRANCH - See RANCOCAS CREEK

SHIPETAUKIN CREEK (Lawrenceville) - Entire length			FW2-NT

SHORE DITCH (Mad Horse Creek) - Entire length			SE1(C1)

SILVER LAKE (Hope)							FW2-TM

SILVER LAKE FORK - See MAD HORSE CREEK

SLAB BRANCH - See MUSKEE CREEK

SLUICE CREEK

(South Dennis) - Entire length, except segment 		FW2-NT/SE1

described below

(Dennis Creek) - Segments of tributaries that are within 	FW2-NT/SE1(C1)

the Dennis Creek and the Beaver Swamp Wildlife Management Areas

SMITH FERRY BROOK (Del. Water Gap) - Entire length		FW1

SPARTA JUNCTION BROOK (Sparta Junction) - Entire length	FW2-TM(C1)

SPRING MILLS BROOK (Milford) ( Entire length			FW2-TP(C1)

STEELE RUN

(Washington Crossing State Park) - Source to confluence 	FW1

with westerly tributary

(Titusville) - Confluence with westerly tributary to the 		FW2-NT

Delaware River

STEENY KILL LAKE (High Point) 					FW1

STEEP RUN (Mauricetown) - Entire length				FW2-NT(C1)

STEPHENSBURG BROOK (Stephensburg) - Entire length		FW2-TP(C1)

STONY BROOK (Knowlton) - Entire length				FW2-TP(C1)

STONY BROOK

(Stokes State Forest) - Source and tributaries, wholey 	FW1(tp)

contained within Stokes State Forest, from their origins to, but not
including, Stony Lake

(Stokes State Forest) - Tributary originating approximately 	FW1(tp)

one mile west of the Branchville Reservoir to the confluence with Stony
Brook

(Stokes State Forest) - Outlet of Stony Lake to the 		FW2-TP(C1)

confluence with Big Flat Brook

STONY LAKE (Stokes State Forest)					FW2-TM(C1)

  TRIBUTARIES - See STONY BROOK

STOW CREEK

(Stow Creek Landing) - Entire length, except tributaries 	FW2-NT/SE1

described separately below

(Mad Horse Creek) - Tributaries within the boundaries 	FW2-NT/SE1(C1)

of the Mad Horse Creek Wildlife Management Area

STRAIGHT CREEK (Berrytown) - Entire length				SE1(C1)

SUNFISH POND (Worthington) - The pond and its outlet stream 	FW1

to the Delaware River

SWAN CREEK (Lambertville) - Entire length				FW2-NT

SWARTSWOOD CREEK (Swartswood) - Entire length		FW2-TM

SWARTSWOOD LAKE (Stillwater)					FW2-TM(C1)

TAR HILL BROOK

(Lake Lenape) - Source to, but not including, Lake 		FW2-TM

Lenape

(Lake Lenape) - Lake Lenape to Andover Junction Brook	FW2-NT

THREE MOUTHS (Egg Island)						FW2-NT/SE1(C1)

THUNDERGUST BROOK

(Deerfield) - Entire length, except segment described 		FW2-NT

below

(Deerfield) - That segment within the boundaries of 		FW2-NT(C1)

Parvin State Park

THUNDERGUST LAKE (Parvin State Park)				FW2-NT(C1)

TILLMAN BROOK (Walpack) - Entire length				FW1(tp)

TROUT BROOK (Hackettstown) - Entire length				FW2-TM(C1)

TROUT BROOK (Tranquility) - Entire length				FW2-TP(C1)

TROUT BROOK (Hope) - Entire length					FW2-TM

TROUT BROOK (Allamuchy) - Entire length				FW2-NT

TROUT BROOK

(Middleville) - Source to confluence with Pond Brook		FW2-TP(C1)

(Middleville) - Confluence with Pond Brook to Paulins Kill	FW2-NT

TURKEY HILL BROOK (Bethlehem) - Entire length			FW2-TP(C1)

TURNERS FORK - See MAD HORSE CREEK

TUTTLES CORNER BROOK (Tuttles Corner) - Entire length		FW2-TP(C1)

UPPER BROTHERS CREEK (Egg Island) - Entire length		SE1(C1)

UPPER DEEP CREEK (Mad Horse Creek) - Entire length		SE1(C1)

VANCAMPENS BROOK (Millbrook) - Entire length			FW2-TP(C1)

WAPALANNE LAKE (Stokes State Forest)				FW2-NT(C1)

WARFORD CREEK (Barbertown) ( Entire length			FW2-TP(C1)

WELDON BROOK (Jefferson Township) - From source to, 		FW2-TM

but not including, Lake Shawnee

WEST CREEK

(Halberton) - Source to the boundary of the Pinelands 	PL

Protection and Preservation Areas, except those portions described
separately, below

(Belleplain) - The portion of the tributary that originates 	FW1

about 0.9 miles southeast of Hoffman's Mill and is located entirely
within the boundaries of Belleplain State Forest

(Belleplain) - Those tributaries that originate about 		FW1

0.5 miles upstream of Hoffman's Mill and are located entirely within the
boundaries of Belleplain State Forest

(Belleplain) - Eastern branch of the easterly tributary 		FW1

to Pickle Factory Pond from its origin to its confluence with the
western branch

(Delmont) - Boundary of the Pinelands Protection and 	FW2-NT/SE1(C1)

Preservation Area to the boundary of the Fish and Game lands

(Delmont) - Boundary of the Fish and Game lands to 		SE1

Delaware Bay

WEST PORTAL CREEK (West Portal) - Entire length			FW2-TP(C1)

WHITE BROOK (Montague) - Entire length				FW2-TP(C1)

WHITE LAKE (Hardwick)							FW2-TM

WICKECHEOKE CREEK

(Locktown) - Source to confluence with Plum Brook		FW2-NT

(Stockton) - Confluence with Plum Brook to Delaware 		FW2-TM

River

WIDGEON PONDS (Egg Island)						FW2-NT/SE1(C1)

WILLS BROOK (Mt. Olive) - Entire length				FW2-TM

YARDS CREEK (Blairstown) - Entire length				FW2-TP(C1)

(e)  The surface water classifications in Table 3 are for waters of the

Passaic, Hackensack and New York Harbor Complex Basin:

TABLE  3

Waterbody									Classification

APSHAWA BROOK (Macopin) - Entire length				FW2-TP(C1)

ARTHUR KILL

(Perth Amboy) - The Kill and its saline New Jersey 		SE2

tributaries between the Outerbridge Crossing and a line connecting Ferry
Pt., Perth Amboy to Wards Pt., Staten Island, New York

(Elizabeth) - From an east-west line connecting 		SE3

Elizabethport with Bergen Pt., Bayonne to the Outerbridge Crossing

(Woodbridge) - All freshwater tributaries				FW2-NT

BEAR SWAMP BROOK (Mahwah) - Entire length			FW2-TP(C1)

BEAR SWAMP LAKE (Ringwood State Park)				FW2-NT(C1)

BEAVER BROOK

(Meriden) - From Splitrock Reservoir Dam downstream 	FW2-TP(C1)

to Meriden Road Bridge

(Denville) - Meriden Road Bridge to Rockaway River		FW2-NT

  TRIBUTARIES

(Meriden) - Two tributaries located approximately 		FW2-TP(C1)

three quarters of a mile southwest of Meriden

BEECH BROOK

(West Milford) - From State line downstream to 		FW2-TM

Monksville Reservoir

BELCHER CREEK (W. Milford) - Entire length				FW2-NT

BERRYS CREEK (Secaucus) - Entire length				FW2-NT/SE2

BLACK BROOK

(Meyersville) - Entire length, except segment described 	FW2-NT

below

(Great Swamp) - Segment and tributaries within 		FW2-NT(C1)

the Great Swamp National Wildlife Refuge

BLUE MINE BROOK

(Wanaque) - Headwaters Downstream to lower Snake	FW2-TP(C1)

Den Road bridge

(Wanaque) - lower Snake Den Road bridge to the 		FW2-TM

boundary of Norvin Green State Forest

(Norvin Green State Forest) - That portion of the stream 	FW2-TM(C1)

and any tributaries within the Norvin Green State Forest

BRUSHWOOD POND (Ringwood State Park)				FW2-TM(C1)

BUCKABEAR POND (Newfoundland) - Pond, its tributaries 		FW2-NT(C1)

and connecting stream to Clinton Reservoir

BURNT MEADOW BROOK (Green Pond) - Source downstream 	FW2-NT

to confluence with Green Pond Brook

BURNT MEADOW BROOK (Stonetown) - Entire length		FW2-TP(C1)

CANISTEAR RESERVOIR (Vernon)					FW2-TM

CANISTEAR RESERVOIR TRIBUTARY (Vernon) - The 		FW1

southern branch of the eastern tributary to the Reservoir

CANOE BROOK (Chatham) - Entire length				FW2-NT

CEDAR POND (Postville) - Pond and all tributaries			FW1

CHARLOTTEBURG RESERVOIR (Charlotteburg)			FW2-TM

CHERRY RIDGE BROOK

(Vernon) - Tributaries not contained within Wawayanda 	FW2-NT

State Park and Newark Watershed lands

(Wawayanda State Park) - Brook and tributaries 		FW1

upstream of Canistear Reservoir located entirely within the boundaries
of Wawayanda State Park and the Newark Watershed lands

CLINTON BROOK (W. Milford) - Clinton Reservoir dam to		FW2-TP(C1)

Pequannock River

CLINTON RESERVOIR (W. Milford)					FW2-TM(C1)

CLOVE BROOK - See STAG BROOK

COOLEY BROOK

(W. Milford) - Entire length, except segments described 	FW2-TP(C1)

below

(Hewitt State Forest) - Segments of the brook and all 		FW1(tp)

tributaries which originate and are located entirely within Hewitt State
Forest

CORYS BROOK (Warren) - Entire length				FW2-NT

CRESSKILL BROOK

(Alpine) - Source to Duck Pond Rd. bridge, Demarest		FW2-TP(C1)

(Demarest) - Duck Pond Rd. bridge to Tenakill Brook		FW2-NT

CROOKED BROOK TRIB. (East of Sheep Hill) - Entire length	FW2-TP(C1)

CUPSAW BROOK

(Skylands) - Source to Wanaque Reservoir, except 		FW2-NT

segment described below

(Ringwood State Park) - That segment of Cupsaw Brook 	FW2-NT(C1)

within the boundaries of Ringwood State Park

DEAD RIVER (Liberty Corners) - Entire length				FW2-NT

DEN BROOK (Randolph) - Entire length					FW2-NT

  TRIBUTARY

(Randolph) - Tributary west of Shongum Lake 			FW2-TP(C1)

DUCK POND (Ringwood)							FW2-NT(C1)

ELIZABETH RIVER

(Elizabeth) - Source to Broad St. bridge, Elizabeth and 	FW2-NT

all freshwater tributaries

(Elizabeth) - Broad St. bridge to mouth				SE3

FOX BROOK (Mahwah) - Entire length					FW2-NT

GLASMERE POND (Ringwood)						FW2-NT(C1)

GOFFLE BROOK (Hawthorne) - Entire length				FW2-NT

GRANNEY BROOK - See SPRING BROOK

GRANNIS BROOK (Morris Plains) - Entire length			FW2-NT

GREAT BROOK

(Chatham) - Entire length, except segment described 		FW2-NT

below

(Great Swamp) - Segment within the boundaries of the 	FW2-NT(C1)

Great Swamp National Wildlife Refuge

GREEN BROOK

(W. Milford) - Entire length, except those segments 		FW2-TP(C1)

described below

(Hewitt State Forest) - Those segments and tributaries 	FW1(tp)

which originate and are located entirely within the Hewitt State Forest
boundaries

GREEN POND (Rockaway)						FW2-TM

GREEN POND BROOK

(Picatinny Arsenal) - Green Pond outlet to, but not 		FW2-TP(C1)

including, Picatinny Lake

(Wharton) - Outlet of Picatinny Lake to the confluence 	FW2-NT

with the Rockaway River

GREENWOOD LAKE (W. Milford)					FW2-TM

HACKENSACK RIVER

(Oradell) - Source to Oradell dam					FW2-NT

(Oradell) - Main stem and saline tributaries from 		SE1

Oradell dam to the confluence with Overpeck Creek

(Little Ferry) - Main stem and saline tributaries from 		SE2

Overpeck Creek to Route 1 and 9 crossing

(Kearny Point) - Main stem downstream from Route 1 	SE3

and 9 crossing

  TRIBUTARIES

(Oradell) - Tributaries joining the main stem between 		FW2-NT/SE1

Oradell dam and the confluence with Overpeck Creek

(Little Ferry) - Tributaries joining the main stem 		FW2-NT/SE2

downstream of Overpeck Creek

HANKS POND (Clinton) - Pond and all tributaries			FW1

HARMONY BROOK (Brookside) - Entire length				FW2-TP(C1)

HARRISONS BROOK (Bernards) - Entire length			FW2-NT

HAVEMEYER BROOK (Mahwah) - Entire length			FW2-TP(C1)

HEWITT BROOK (W. Milford) - Entire length				FW2-TP(C1)

HIBERNIA BROOK

(Marcella) - Source to first Green Pond Road bridge 		FW2-TP(C1)

downstream of Lake Emma

(Hibernia) - First Green Pond Road bridge to confluence	FW2-TM

with Beaver Brook

  TRIBUTARY

(Lake Ames) - Source to, but not including, Lake Ames	FW2-TP(C1)

HIGH MOUNTAIN BROOK (Ringwood) - Source to, but not 		FW2-TP(C1)

including, Skyline Lake

HOHOKUS BROOK (Hohokus) - Entire length				FW2-NT/SE2

HUDSON RIVER

(Rockleigh) - River and saline portions of New Jersey 		SE1

tributaries from the New Jersey-New York boundary line in the north to
its confluence with the Harlem River, New York

(Englewood Cliffs) - River and saline portions of New 		SE2

Jersey tributaries from the confluence with the Harlem River, New York
to a north-south line connecting Constable Hook (Bayonne) to St. George
(Staten Island, New York)

  TRIBUTARIES

(Rockleigh) - Freshwater portions of tributaries to the 		FW2-NT

Hudson River in New Jersey

INDIAN GROVE BROOK (Bernardsville) - Entire length		FW2-TP(C1)

JACKSON BROOK

(Mine Hill) - Source to the boundary of Hurd Park, Dover	FW2-TP(C1)

(Dover) - Hurd Park to Rockaway River				FW2-NT

JENNINGS CREEK (W. Milford) - State line to Wanaque River	FW2-TP(C1)

JERSEY CITY RESERVOIR (Boonton)					FW2-TM

KANOUSE BROOK (Newfoundland) - Entire length			FW2-TP(C1)

KIKEOUT BROOK (Butler) - Entire length				FW2-NT

KILL VAN KULL (Bayonne) - Westerly from a north-south line 	SE3

connecting Constable Hook (Bayonne) to St. George (Staten Island, New
York)

LAKE RICKONDA OUTLET STREAM (Monks) - That segment 	FW2-TM(C1)

of the outlet stream from Lake Rickonda within Ringwood State Park

LAKE STOCKHOLM BROOK

(Stockholm) - Entire length, except tributaries described 	FW2-TP(C1)

separately below

(Stockholm) - Portion of westerly tributary, from its 		FW1(tp)

origins to about 1000 feet south of the Route 23 bridge, located
entirely within the boundaries of the Newark watershed

(Stockholm) - Brook between Hamburg Turnpike and 		FW1(tp)

Vernon-Stockholm Rd. to its confluence with Lake Stockholm Brook, north
of Rt. 23

LITTLE POND BROOK (Oakland) - Entire length			FW2-TP(C1)

LOANTAKA BROOK

(Green Village) - Entire length, except segment 		FW2-NT

described below

(Great Swamp) - Brook and all tributaries within the 		FW2-NT(C1)

boundaries of Great Swamp National Wildlife Refuge

LUD-DAY BROOK (Camp Garfield) - Source downstream to its	FW1

confluence with the southwestern outlet stream from Clinton Resevoir
just upstream of the confluence of the outlet stream and a tributary
from Camp Garfield

MACOPIN RIVER

(Newfoundland) - Source to Echo Lake dam			FW2-NT

(Newfoundland) - Echo Lake dam to Pequannock River	FW2-TM

MEADOW BROOK

(Wanaque) - Skyline Lake to E. Belmont Ave.			FW2-NT

(Wanaque) - E. Belmont Ave. downstream to Wanaque	FW2-TP(C1)

River

MILL BROOK

(Randolph) - Source to Rt. 10 bridge				FW2-TP(C1)

(Randolph) - Rt. 10 bridge to Rockaway River, including	FW2-TM

the easterly tributary

MONKSVILLE RESERVOIR (Long Pond Iron Works 			FW2-TM(C1)

State Park)

MORSES CREEK (Linden) - Entire length				FW2-NT/SE3

MOSSMANS BROOK (West Milford) - Source to confluence 		FW2-TP(C1)

with Clinton Reservoir

MT. TABOR BROOK (Morris Plains) - Entire length			FW2-NT

NEWARK BAY (Newark) - North of an east-west line connecting 	SE3

Elizabethport with Bergen Pt., Bayonne up to the mouths of the Passaic
and Hackensack Rivers

NOSENZO POND (Upper Macopin)					FW2-NT(C1)

OAK RIDGE RESERVOIR (Oak Ridge)					FW2-TM

OAK RIDGE RESERVOIR (Oak Ridge) - Northwestern 		FW1(tm)

tributary to Reservoir

OHIO BROOK (Morris Township) - Source downstream		FW2-TM

to Morristown town line

OVERPECK CREEK (Palisades Park) - Entire length			FW2-NT/SE2

PACOCK BROOK

(Canistear) - Brook and tributaries upstream of 			FW1

Canistear Reservoir located entirely within the boundaries of the Newark
Watershed

(Stockholm) - Outlet of Canistear Reservoir to 			FW2-NT

Pequannock River

PASSAIC RIVER

(Mendham) - Source downstream to, but not including,	FW2-TP(C1)

Osborn Pond or tributaries described separately below

(Paterson) - Outlet of Osborn Pond to Dundee Lake dam	FW2-NT

(Little Falls) - Dundee Lake dam to confluence with 		FW2-NT/SE2

Second River

(Newark) - Confluence with Second River to mouth		SE3

  TRIBUTARIES

(Great Piece Meadows State Park) - Tributaries within 	FW2-NT(C1)

Great Piece Meadows State Park

PECKMAN RIVER (Verona) - Entire length				FW2-NT

PEQUANNOCK RIVER

  MAIN STEM

(Vernon) - Source to confluence with Pacock Brook 		FW1(tp)

(Hardyston) - River and the easterly tributary from 		FW2-TP(C1)

Pacock Brook to, but not including, Oak Ridge Reservoir

(Newfoundland) - Outlet of Oak Ridge Reservoir		FW2-TP(C1)

downstream to, but not including Charlotteburg Reservoir

(Charlotteburg) - Outlet of Charlotteburg Reservoir to,		FW2-TM

but not including, Macopin Reservoir or the tributaries described
separately below

(Kinnelon) - Macopin Reservoir outlet to Hamburg 		FW2-TP(C1)

Turnpike bridge in Pompton Lakes Borough

(Riverdale) - Hamburg Turnpike bridge in Pompton 		FW2-TM

Lakes Borough to confluence with Wanaque River

(Pompton Plains) - Confluence with Wanaque River 		FW2-NT

downstream to confluence with Pompton River

  TRIBUTARIES

(Copperas Mtn.) - Entire length					FW2-TP(C1)

(Smoke Rise) - Entire length					FW2-TP(C1)

(Green Pond Junction) - Tributary at Green Pond 		FW1(tm)

Junction from its origin downstream to Route 23

(Jefferson) - Tributary joining the main stem about 		FW1(tm)

3500+ feet southeast of the Sussex-Passaic County line, near Jefferson
from its origin to about 2000 feet upstream of the pond

(Lake Kampfe) - Source to, but not including, 			FW2-TM

Lake Kampfe

(Lake Kampfe) - Lake Kampfe to Pequannock River, 		FW2-NT

except tributary described separately below

(Lake Kampfe) - Tributary within the boundaries of 		FW2-NT(C1)

Norvin Green State Forest, originating west of Torne Mtn.

PILES CREEK (Grasselli) - Entire length					SE3

POMPTON LAKE (Pompton Lakes)					FW2-NT

POMPTON RIVER (Wayne) - Entire length				FW2-NT

POND BROOK (Oakland) - Entire length				FW2-NT

POSTS BROOK

(Bloomingdale) - Source to confluence with Wanaque 	FW2-NT

River, except Wanaque Reservoir and segment described below

(Norvin Green State Forest) - That segment of the 		FW2-NT(C1)

stream and all tributaries within the boundaries of Norvin Green State
Forest

PREAKNESS (SINGAC) BROOK

(Wayne) - Source to, but not including, Barbour Pond		FW2-TP(C1)

(Barbour Pond) - Pond to Passaic River				FW2-NT

PRIMROSE BROOK

(Harding) - Source to Lees Hill Road bridge			FW2-TP(C1)

(Harding) - Lees Hill Road bridge to Great Swamp 		FW2-NT

National Wildlife Refuge boundary

(Great Swamp) - Wildlife Refuge boundary to Great 		FW2-NT(C1)

Brook

RAHWAY RIVER

  SOUTH BRANCH

(Rahway) - Source to Hazelwood Ave., Rahway		FW2-NT

(Rahway) - Hazelwood Ave. to mouth				SE2

  MAIN STEM

(Rahway) - Upstream of Pennsylvania Railroad bridge		FW2-NT

(Linden) - Penn. Railroad bridge to Route 1&9 crossing	SE2

(Carteret) - Route 1&9 crossing to mouth			SE3

RAMAPO LAKE (Ramapo) - Lake and all outlet streams 		FW2-NT(C1)

and tributaries within the boundaries of Ramapo Mtn. State Forest

RAMAPO RIVER (Mahwah) - State line to Pompton River		FW2-NT

  TRIBUTARY (Oakland) - Entire length					FW2-TP(C1)

RINGWOOD CREEK

(Ringwood) - Entire length, except segment described 	FW2-TM

below

(Sloatsburg) - Creek within Ringwood State Park		FW2-TM(C1)

RINGWOOD MILL POND (Ringwood)					FW2-NT(C1)

ROCKAWAY RIVER

(Wharton) - Source to Washington Pond outlet, excluding 	FW2-NT

the segment within the boundaries of the Berkshire Valley Wildlife
Management Area

(Berkshire Valley) - That segment within the boundaries 	FW2-NT(C1)

of the Berkshire Valley Wildlife Management Area

(Dover) - Washington Pond outlet downstream to		FW2-TM(C1)

Rt. 46 bridge

(Boonton) - Rt. 46 bridge to Passaic River, excluding 		FW2-NT

Jersey City Reservoir

RUSSIA BROOK

(Sparta) - Source to Lake Hartung dam				FW2-NT

(Milton) - Lake Hartung dam to, but not including, 		FW2-TM

Lake Swannanoa

  TRIBUTARIES

(S. of Mt. Paul) ( Entire length					FW2-TP(C1)

SADDLE RIVER

(Upper Saddle River) - State line to Bergen County 		FW2-TP(C1)

Rt. 2 bridge

(Saddle River) - Bergen County Rt. 2 bridge to 			FW2-TM

Allendale Rd. bridge

(Lodi) - Allendale Rd. bridge to Passaic River			FW2-NT/SE3

SAWMILL CREEK (Pompton Plains) - Entire length			FW2-NT

SCARLET OAK POND (Mahwah)						FW2-TM

SHEPPARD LAKE (Ringwood)						FW2-TM(C1)

SINGAC BROOK - See PREAKNESS BROOK

SLOUGH BROOK (Livingston) - Entire length				FW2-NT

SMITH CREEK (Woodbridge) - Entire length				FW2-NT/SE3

SPLIT ROCK RESERVOIR (Rockaway)					FW2-TM

SPLIT ROCK RESERVOIR TRIBUTARIES

(Farny State Park)- Three tributaries within Farny 		FW2-NT(C1)

State Park

SPRING (GRANNEY) BROOK (Mine Hill) - Entire length		FW2-TP(C1)

SPRING GARDEN BROOK (Florham) - Entire length			FW2-NT

STAG (CLOVE) BROOK (Mahwah) - Entire length			FW2-TP(C1)

STEPHENS BROOK

(Roxbury) - Entire length, except segment described 		FW2-NT

separately, below

(Berkshire Valley) - That segment north of the 			FW1

boundaries of the Berkshire Valley Wildlife Management Area

STONE HOUSE BROOK (Kinnelon) - Entire length			FW2-NT

STONY BROOK (Boonton) - Entire length				FW2-NT

SURPRISE LAKE (Hewitt)							FW1

SWAN POND (Ringwood)							FW2-NT(C1)

TENAKILL BROOK (Demarest) - Entire length				FW2-NT

TERRACE POND (Wawayanda)						FW2-NT(C1)

TIMBER BROOK (Kitchell) - Entire length, except tributary 		FW2-NT

described separately below

TIMBER BROOK (Farny State Park) - Headwater segment 		FW2-NT(C1)

of tributary to Timber Brook within Farny State Park

TROY BROOK (Troy Hills) - Entire length				FW2-NT

WANAQUE RESERVOIR							FW2-TM

WANAQUE RIVER

  MAIN STEM

(Wanaque) - Greenwood Lake outlet, through Wanaque 	FW2-TM(C1)

Wildlife Management Area and Long Pond Iron Works State Park, including
the Monksville Reservoir, to the Monksville Reservoir dam at Stonetown
Road, except tributary described separately below

(Hewitt) - Entire length of tributary south of Jennings 		FW2-TP(C1)

Creek

(Pompton Lakes) - Wanaque Reservoir dam to Wanaque	FW2-NT

Ave. bridge

(Pompton Lakes) - Wanaque Ave. bridge downstream to	FW2-TM

Pequannock River

WEST BROOK (W. Milford) - Entire length				FW2-TP(C1)

WEST POND (Hewitt)							FW1

WEYBLE POND (Ringwood)						FW2-NT(C1)

WHIPANNY RIVER

(Brookside) - Source to Whitehead Rd. bridge			FW2-TP(C1)

(Morristown) - Whitehead Rd. bridge to Rockaway River	FW2-NT

  TRIBUTARIES

(Brookside) - Entire length						FW2-TP(C1)

(E. of Brookside) - Entire length					FW2-TM

(E. of Washington Valley) - Entire length				FW2-TM

(Gillespie Hill) - Entire length					FW2-TP(C1)

(Shongum Mtn.) - Entire length					FW2-NT

WONDER LAKE (West Milford)						FW2-NT(C1)

WOODBRIDGE CREEK (Woodbridge) - Entire length			FW2-NT/SE3

(f)  The surface water classifications in Table 4 are for waters of the

Raritan River and Raritan Bay Basin:

TABLE  4

Waterbody									Classification

ALLERTON CREEK (Allerton) - Entire length				FW2-NT

AMBROSE BROOK (Piscataway) - Entire length			FW2-NT

AMWELL LAKE (Syndertown)						FW2-NT(C1)

ASSISCONG CREEK (Flemington) - Entire length			FW2-NT

BACK BROOK (Vanliew's Corners) - Entire length			FW2-NT

BALDWINS CREEK

(Pennington) - Entire length, except segment described 	FW2-NT

separately below

(Baldwin) - Segment within the boundaries of Baldwin 	FW2-NT(C1)

Lake Wildlife Management Area

BARCLAY BROOK (Redshaw Corners) - Entire length		FW2-NT

BEAVER BROOK

(Cokesbury) - Source to Reformatory Road bridge		FW2-TP(C1)

(Annandale) - Reformatory Rd. bridge to Raritan River, 	FW2-TM

South Branch

BEDEN BROOK (Montgomery) - Entire length				FW2-NT

BIG BEAR BROOK (West Windsor) - Entire length			FW2-NT

BIG BROOK (Vanderberg) - Entire length				FW2-NT

BLACK BROOK (Polktown) - Entire length				FW2-TP(C1)

BLACK RIVER - See LAMINGTON RIVER

BLACKBERRY CREEK

(Oceanport) - Source to a line beginning on the 		SE1

easternmost extent of Gooseneck Point and bearing approximately 162
degrees True North to its terminus on the westernmost extent of an
unnamed point of land in the vicinity of the western extent of Cayuga
Ave. in Oceanport.

(Oceanport) - Creek below the line described above		SE1(C1)

BLUE BROOK (Mountainside) - Entire length				FW2-NT

BOULDER HILL BROOK (Tewksbury) - Entire length			FW2-TP(C1)

BOUND BROOK (Dunellen) - Entire length				FW2-NT

BRANCHPORT CREEK

(Long Branch) - Source to a line beginning on the 		FW2-NT/SE1

northernmost extent of an unnamed point of land lying north of Pocano
Ave. in Oceanport and bearing approximately 055 degrees True North to
its terminus on the westernmost extent of the northern bulkhead at the
lagoon located between France Rd. and Lori Rd. in Monmouth Beach

(Monmouth Beach) - Creek below line described above	SE1(C1)

BUDD LAKE (Mt. Olive)							FW2-NT(C1)

BURNETT BROOK (Ralston) - Entire length				FW2-TP(C1)

BUSHKILL BROOK

(Flemington) ( Source and tributary downstream to		FW2-TM

Rt. 31 Bridge

(Flemington) ( Rt. 31 bridge downstream to South		FW2-NT

Branch Raritan River

CAPOOLONG (CAKEPOULIN) CREEK (Sydney) - Entire length	FW2-TP(C1)

CEDAR BROOK (Spotswood) - Entire length				FW2-NT

CHAMBERS BROOK (Whitehouse) - Entire length			FW2-NT

CHEESEQUAKE STATE PARK WATERS (S. Amboy) - Fresh 	FW2-NT(C1)

waters within the park upstream of the limits of tidal influence

CLAYPIT CREEK

(Navesink) - Source to widening of the Creek near 		FW2-NT/SE1

Linden Ave. and just north to the Locust Ave. bridge in Navesink

(Navesink) - Widening of Creek to Navesink River		SE1(C1)

COLD BROOK (Oldwick) - Entire length					FW2-TP(C1)

CRAMERS CREEK (Hamden) - Entire length				FW2-NT

CRANBURY BROOK (Old Church) - Entire length			FW2-NT

CRUSER BROOK (Montgomery) - Entire length			FW2-NT

CUCKELS BROOK (Bridgewater) - Entire length			FW2-NT

DAWSONS BROOK (Ironia) - Entire length				FW2-TP(C1)

DEEP RUN (Old Bridge) - Entire length					FW2-NT

DEVILS BROOK (Schalks) - Entire length				FW2-NT

DRAKES BROOK 

(Ledgewood) - Source downstream to Hillside Avenue 	FW2-TM(C1)

bridge

(Flanders) - Hillside Avenue bridge to confluence 		FW2-NT(C1)

with the South Branch Raritan River

  TRIBUTARY (Mt. Olive) - Source downstream to Central 		FW2-TP(C1)

Railroad bridge

DUCK POND RUN (Port Mercer) - Entire length			FW2-NT

DUKES BROOK (Somerville) - Entire length				FW2-NT

ELECTRIC BROOK (Schooley's Mtn.) - Entire length			FW2-TP(C1)

FLANDERS BROOK (Flanders) - Entire length				FW2-TP(C1)

FLANDERS CANAL (Flanders) - Entire length				FW2-NT(C1)

FROG HOLLOW BROOK (Califon) - Entire length			FW2-TP(C1)

GANDER BROOK (Manalapan) - Entire length				FW2-NT

GLADSTONE BROOK (St. Bernards School) - Entire length		FW2-TP(C1)

GREAT DITCH (S. Brunswick) - That portion of Great Ditch 		FW2-NT(C1)

and its tributaries within Pigeon Swamp State Park

GREEN BROOK

(Watchung) - Source to Rt. 22 bridge				FW2-TM

(Plainfield) - Rt. 22 bridge to Bound Brook			FW2-NT

GUINEA HOLLOW BROOK (Tewksbury)				FW2-TP(C1)

HACKLEBARNEY BROOK (Hacklebarney) - Entire length		FW2-TP(C1)

HEATHCOTE BROOK (Kingston) - Entire length			FW2-NT

HERZOG BROOK (Pottersville) - Entire length				FW2-TP(C1)

HICKORY RUN (Califon) - Entire length					FW2-TP(C1)

HOCKHOCKSON BROOK (Colts Neck) - Entire length		FW2-TM

HOLLAND BROOK (Readington) - Entire length			FW2-NT

HOLLOW BROOK (Pottersville) - Entire length				FW2-TP(C1)

HOOKS CREEK LAKE (Cheesequake State Park)			FW2-NT(C1)

HOOPSTICK BROOK (Bedminister) - Entire length			FW2-NT

INDIA BROOK (NORTH BRANCH, RARITAN RIVER)

(Randolph) - Entire length						FW2-TP(C1)

IRELAND BROOK (Paulus Corners) - Entire length			FW2-NT

IRESICK BROOK (Spotswood) - Entire length				FW2-NT

KRUEGER'S BROOK - (Flanders) - Entire length			FW2-TP(C1)

LAMINGTON RIVER (BLACK RIVER)

(Succasunna) - Source to Rt. 206 bridge				FW2-NT(C1)

(Milltown) - Rt. 206 bridge to confluence with Rinehart 	FW2-TM(C1)

Brook

(Pottersville) - Confluence with Rinehart Brook to 		FW2-TP(C1)

Camp Brady bridge, Bedminister

(Vliettown) - Camp Brady bridge to Rt. 523 bridge		FW2-TM

(Burnt Mills) - Rt. 523 to North Branch, Raritan River		FW2-NT

  TRIBUTARY (Ironia) - Source downstream to, but not		FW2-TP(C1)

including, Bryant Pond

LAWRENCE BROOK

(Deans) - Source to the intake of the New Brunswick 		FW2-NT

Water Department at Weston's Mill Dam

(New Brunswick) - Weston's Mill Dam to Raritan River		SE1

LEDGEWOOD BROOK (Ledgewood) - Entire length			FW2-TP(C1)

LITTLE BROOK (Califon) - Entire length					FW2-TP(C1)

LITTLE SILVER CREEK

(Shrewsbury) - Source to a line beginning on the 		FW2-NT/SE1

eastern bank of that unnamed lagoon located between Wardell Ave. and
Oakes Rd. in Rumson and bearing approximately 171 degrees T (True North)
to its terminus on the south shore of Little Silver Creek

(Rumson) - Creek below line described above			SE1(C1)

LOMERSON BROOK - See HERZOG BROOK

MANALAPAN BROOK

(Jamesburg) - Source to Duhernal Lake dam, except 		FW2-NT

tributary described separately below

(Tennent) - That portion of the tributary at Tennent 		FW2-NT(C1)

along the boundary of Monmouth Battlefield State Park

MATCHAPONIX BROOK (WEAMACONK CREEK)

(Mount Mills) - Entire length, except segments 			FW2-NT

described below

(Freehold) - The brook and tributaries within the 		FW2-NT(C1)

boundaries of Monmouth Battlefield State Park

MCGELLAIRDS BROOK

(Englishtown) - Entire length, except tributary described 	FW2-NT

separately below

(Freehold) - Tributary within Monmouth Battlefield 		FW2-NT(C1)

State Park

MCVICKERS BROOK (Mendham) - Entire length			FW2-TM(C1)

MIDDLE BROOK (Greater Cross Roads) - Entire length		FW2-NT

MIDDLE BROOK

  EAST BRANCH (Springdale) - Entire length				FW2-TM

  WEST BRANCH (Martinsville) - Entire length				FW2-NT

  MAIN STEM (Bound Brook) - Confluence of East and West 	FW2-NT

branches to Raritan River

MILFORD BROOK (Lafayette Mills) - Entire length			FW2-NT

MILLSTONE RIVER (Hightstown) - Entire length			FW2-NT

MINE BROOK (Mine Brook) - Entire length				FW2-NT

  TRIBUTARIES

(East of Mine Mt.) - Entire length					FW2-TP(C1)

(South of Mine Mt.) - Source downstream to Douglass		FW2-TP(C1)

Road Bridge

MINE BROOK (Colts Neck) - Entire length				FW2-NT

MULHOCKAWAY CREEK (Pattenburg) - Entire length		FW2-TP(C1)

NAVESINK RIVER

(Red Bank) - Source to a line starting at a point at the 	SE1

northeast end of Blossom Cove, bearing approximately 142 degrees T (True
North), through navigational aid C23 to the south bank near Riverview
Hospital

(Rumson) - River southeast of the line described above, 	SE1(C1)

except segment described below

(Monmouth Beach) - All water south and east of a line 	SE1

beginning on the northwesternmost point of land on Raccoon Island (in
the vicinity of the western extent of Highland Ave.) in Monmouth Beach,
and bearing approximately 056 degrees T (True North) to the southernmost
point of a small unnamed island, and then bearing approximately 091
degrees T (True North) to its terminus on the northernmost point of land
located at the northern extent of Monmouth Parkway in Monmouth Beach and
all waters south of a line beginning on the western shoreline (just east
of Monmouth Parkway in Monmouth Beach) and bearing approximately 081
degrees T (True North), intersecting Channel Marker Flashing Red 4 and
Channel Marker Flashing Red 2 and terminating on the eastern shoreline
of the Galilee section of Monmouth Beach.

NESHANIC RIVER (Reaville) - Entire length				FW2-NT

NORTON BROOK (Norton) - Entire length				FW2-TP(C1)

OAKDALE CREEK (Chester) - Entire length				FW2-TP(C1)

OAKEYS BROOK (Deans) - Entire length				FW2-NT

OCEANPORT CREEK

(Fort Monmouth) - Source to a line beginning on the 		FW2-NT/SE1

easternmost extent of Horseneck Point and bearing approximately 140
degrees T (True North) to its terminus on the westernmost extent of an
unnamed point of land located at the westernmost extent of Monmouth
Boulevard in Oceanport

(Oceanport) - Creek downstream of line described above	SE1(C1)

PARKERS CREEK

(Fort Monmouth) - Source to a line beginning on the 		FW2-NT/SE1

easternmost extent of Horseneck Point and bearing approximately 000
degrees T (True North) to its terminus on Breezy Point on the Little
Silver side (north) side of the creek

(Fort Monmouth) - Creek downstream of line 			SE1(C1)

described above

PEAPACK BROOK (Gladstone) - Entire length				FW2-TP(C1)

PETERS BROOK (Somerville) - Entire length				FW2-NT

PIGEON SWAMP (Pigeon Swamp State Park) - All waters 		FW2-NT(C1)

within the boundaries of Pigeon Swamp State Park

PIKE RUN (Belle Meade) - Entire length					FW2-NT

PINE BROOK (Clarks Mills) - Entire length				FW2-NT

PINE BROOK (Cooks Mill) - Entire length				FW2-TM

PLEASANT RUN (Readington) - Entire length				FW2-NT

PRESCOTT BROOK (Stanton Station) - Entire length			FW2-TM

RAMANESSIN (HOP) BROOK (Holmdel) - Entire length		FW2-TM

RARITAN BAY - Entire drainage						FW2-NT/SE1

RARITAN RIVER

  NORTH BRANCH (Also see INDIA BROOK)

(Pleasant Valley) - Source to, but not including, 		FW2-TP(C1)

Ravine Lake

(Far Hills) - Ravine Lake dam to Rt. 512 bridge			FW2-TM

(Bedminister) - Rt. 512 bridge to confluence with 		FW2-NT

South Branch, Raritan River

  SOUTH BRANCH RARITAN RIVER

(Mt. Olive) - Source to the dam that is 390 feet 			FW2-NT(C1)

upstream of the Flanders-Drakestown Road bridge and the two tributaries
which originate north and east of the Budd Lake Airfield

(Mt. Olive) - Dam to confluence with Turkey Brook		FW2-TM(C1)

(Middle Valley) - Confluence with Turkey Brook to		FW2-TP(C1)

Rt. 512 bridge

 (Califon) - Rt. 512 bridge to downstream end of		FW2-TM

Packers Island, except segment described separately, below

(Ken Lockwood Gorge) - River and tributaries within 		FW2-TM(C1)

Ken Lockwood Gorge Wildlife Management Area

(Neshanic Sta.) - Downstream end of Packers 			FW2-NT

Island to confluence with North Branch, Raritan River

  TRIBUTARIES, SOUTH BRANCH RARITAN RIVER

(Long Valley) - Entire length					FW2-TP(C1)

(S. of Hoffmans) - Entire length					FW2-TP(C1)

(S. of Schooley(s Mt.) - Entire length				FW2-TP(C1)

  MAIN STEM RARITAN RIVER

(Bound Brook) - From confluence of North and South 		FW2-NT

Branches to Landing Lane bridge in New Brunswick and all freshwater
tributaries downstream of Landing Lane bridge.

(Sayreville) - Landing Lane bridge to Raritan Bay 		SE1

and all saline water tributaries

RINEHART BROOK (Hacklebarney) - Entire length			FW2-TP(C1)

ROCK BROOK (Montgomery) - Entire length				FW2-NT

ROCKAWAY CREEK

  NORTH BRANCH

(Mountainville) - Source to Rt. 523 bridge			FW2-TP(C1)

(Whitehouse) - Rt. 523 bridge to confluence with 		FW2-TM

South Branch

  SOUTH BRANCH (Whitehouse) - Entire length			FW2-TM

  MAIN STEM (Whitehouse) - Confluence of North and 		FW2-NT

South Branches to Lamington River

ROCKY RUN - (Lebanon) - Entire length				FW2-TP(C1)

ROUND VALLEY RESERVOIR (Clinton)					FW2-TP

ROYCE BROOK (Manville) - Entire length				FW2-NT

SANDY HOOK BAY (Sandy Hook)					SE1

SHREWSBURY RIVER

(Little Silver) - Source to Rt. 36 highway bridge			SE1(C1)

(Highlands) - Rt. 36 bridge to Sandy Hook Bay			SE1

SIDNEY BROOK (Grandin) - Entire length				FW2-NT

SIMONSON BROOK (Griggstown) - Entire length			FW2-NT

SIX MILE RUN

(Franklin Church) - Entire length, except segment 		FW2-NT

described below

(Hillsborough) - Segment within the boundaries of 		FW2-NT(C1)

Six Mile Run State Park

SOUTH RIVER

(Old Bridge) - Duhernal Lake to intake of the Sayreville 	FW2-NT

Water Department

(Sayreville) - Below the intake of the Sayreville Water 		SE1

Department

SPOOKY BROOK (Bound Brook)						FW2-NT

SPRUCE RUN

(Glen Gardner) - Source to, but not including, Spruce 		FW2-TP(C1)

Run Reservoir

(Clinton) - Spruce Run Reservoir dam to Raritan River, 	FW2-TM

South Branch

SPRUCE RUN RESERVOIR (Union) - Reservoir and tributaries	FW2-TM(C1)

STONY BROOK (Washington) - Entire length				FW2-TP(C1)

STONY BROOK

(Hopewell) - Entire length, except that segment 		FW2-NT

described below

(Syndertown) - Brook and tributaries within Amwell 		FW2-NT(C1)

Lake Wildlife Management Area

STONY BROOK (Watchung) - Entire length				FW2-NT

SUN VALLEY BROOK (Mt Olive) - Entire length			FW2-TP(C1)

SWIMMING RIVER (Red Bank) - Swimming River Reservoir 		FW2-NT/SE1

dam to the Navesink River

TANNERS BROOK (Washington) - Entire length			FW2-NT(C1)

TEETERTOWN BROOK (Lebanon) - Entire length			FW2-TP(C1)

TEN MILE RUN (Franklin) - Entire length				FW2-NT

TENNENT BROOK (Old Bridge) - Entire length				FW2-NT

TEPEHEMUS BROOK (Manalapan) - Entire length			FW2-NT

TOWN NECK CREEK

(Little Silver) - Source to a line beginning on the 		FW2-NT/SE1

easternmost extent of the unnamed point of land located just east of
Paag Circle on the south bank of Town Neck Creek and bearing
approximately 095 degrees True North and terminating on Silver Point

(Little Silver) - Creek below line described below		SE1(C1)

TROUT BROOK (Hacklebarney) - Entire length				FW2-TP(C1)

TURKEY BROOK (Mt. Olive) - Entire length				FW2-TP(C1)

TURTLEBACK BROOK (Middle Valley) - Entire length			FW2-NT

WALNUT BROOK (Flemington) - Entire length				FW2-TM

WEAMACONK CREEK - See MATCHAPONIX BROOK

WEMROCK BROOK

(Millhurst) - Entire length, except that segment 			FW2-NT

described below

(Monmouth Battlefield State Park) - Those segments 		FW2-NT(C1)

of the brook and its tributaries within the boundaries of Monmouth
Battlefield State Park

WEMROCK POND (Monmouth Battlefield State Park)			FW2-NT(C1)

WILLOUGHBY BROOK (Buffalo Hollow) - Entire length		FW2-TP(C1)

WILLOW BROOK (Holmdel) - Entire length				FW2-NT

YELLOW BROOK (Colts Neck) - Entire length				FW2-NT

(g)  The surface water classifications in Table 5 are for waters of the

Wallkill River Basin:

TABLE  5

Waterbody									Classification

BEARFORT WATERS (Wawayanda)					FW2-NT(C1)

BEAVER RUN (Wantage) - Entire length				FW2-NT

BLACK CREEK

(McAfee) - Source to Rt. 94 bridge, except those 		FW2-TM

tributaries described separately, below

(Vernon) - Rt. 94 bridge to Pochuck Creek			FW2-NT

  TRIBUTARIES

(Hamburg) - Three tributaries to Black Creek which 		FW1(tm)

orginate in the Hamburg Mtn. Wildlife Management Area from their sources
to the Management Area boundaries

(Rudeville) - Triburaries within the Hamburg Mtn. 		FW2-TM(C1)

Wildlife Management Area not classified as FW1, above

(McAfee) - Entire length						FW2-TP(C1)

(Vernon Valley) - Entire length					FW2-NT

CLOVE CREEK (Colesville) - Entire length				FW2-TM

CLOVE BROOK

(Wantage) - Source to, but not including, Clove Acres 	FW2-TM

Lake, except those tributaries described separately below

(Sussex) - Clove Acres Lake to Papakating Creek		FW2-NT

(High Point) - Those portions of the two northernmost 		FW1(tp)

tributaries located entirely within High Point State Park boundaries,
immediately east of Lake Marcia

FRANKLIN POND CREEK

(Hardyston) - Source to, but not including, Franklin Pond	FW2-TP(C1)

(Hamburg Mtn.) - Tributaries within the Hamburg Mtn.		FW2-TM(C1)

Wildlife Management Area

GLENWOOD BROOK (Glenwood) - Outlet of Glenwood Lake 	FW2-TM

to State line

HAMBURG CREEK

(Hamburg Mtn.) - Source to Rt. 517 bridge, Rudeville,		FW2-TM

except tributary described separately below

(Hardistonville) - Rt. 517 bridge to Wallkill River			FW2-NT

(Hamburg Mtn.) - The third tributary just southwest of 		FW1

Hamburg Mtn. flowing toward the Wallkill River and located entirely
within the Hamburg Mtn. Wildlife Management Area

HANFORD BROOK (Hanford) - Entire length within New Jersey	FW2-NT

LAKE LOOKOUT (Wawayanda)						FW1

LAKE LOOKOUT BROOK (Wawayanda) - Brook and tributaries 	FW1

from source in Newark City holdings, through the Wawayanda State Park,
to confluence with the outlet stream from Lake Wawayanda

LAKE RUTHERFORD (Wantage) - The Lake and its tributaries	FW1(tm)

LAUREL POND (Wawayanda) - Laurel Pond, including its 		FW1

outlet stream and tributaries, to the outlet stream from Lake Wawayanda

LIVINGSTON PONDS (Wawayanda) - The two northwestern 	FW2-NT(C1)

ponds which are within State Park lands

LIVINGSTON PONDS BROOK (Wawayanda State Park) - 		FW2-TP(C1)

Source downstream to State line

LONG HOUSE BROOK

(Upper Greenwood Lake) - Source to State line, except 	FW2-NT

segment described below

(Upper Greenwood Lake) - Segment within the bounds 	FW2-NT(C1)

of Hewitt State Forest

LOUNSBERRY HOLLOW BROOK 

(Vernon Valley) - Outlet of Glenwood Lake to Pochuck 	FW2-TM

Creek

MUD POND OUTLET STREAM (Hamburg) - Outlet stream 		FW2-TP(C1)

from the Pond downstream to confluence with Hamburg Creek, including all
tributaries

PAPAKATING CREEK

  MAIN STEM

(Frankford) - Source to Rt. 629 bridge.				FW2-TM

(Pellettown) - Entire length of tributary				FW2-NT

(Wantage) - Rt. 629 bridge to Wallkill River			FW2-NT

  WEST BRANCH

(Wantage) - Entire length						FW2-NT

PARKER LAKE (Wawayanda)						FW2-NT(C1)

POCHUCK CREEK

(Vernon) - Source to State line, except segment 		FW2-NT

described separately below

(High Point) - Segment within State Park lands			FW2-NT(C1)

QUARRYVILLE BROOK - See WILLOW BROOK

RUTGERS CREEK (High Point) - The Cedar Swamp 			FW1

headwaters of the tributary to Rutgers Creek located entirely within the
High Point State Park boundaries just south of the State line

SAND HILLS BROOK

(Hamburg Mtn.) - The upstream portion of Sand Hills 		FW1

Brook, including the pond at its headwaters, located entirely within the
boundaries of the Hamburg Mtn. Wildlife Management Area

(Hamburg) - Brook and tributaries beyond Management 	FW2-NT

Area boundaries

SAWMILL POND BROOK

(W. Milford) - Entire length, except segment described 	FW2-NT

separately below

(Wawayanda) - Segment within the boundaries of 		FW2-NT(C1)

Wawayanda State Park

SPARTA GLEN BROOK (Sparta) - Entire length			FW2-TP(C1)

SPRING BROOK (Maple Grange) - Entire length			FW2-TP(C1)

TOWN BROOK (Vernon) - Entire length					FW2-TM

WALLKILL RIVER

(Sparta) - Source to confluence with Sparta Glen Brook	FW2-NT

(Franklin) - Sparta Glen Brook to, but not including,		FW2-TM

Franklin Pond

(Wantage) - Outlet of Franklin Pond to State line		FW2-NT

  TRIBUTARIES

(Sparta) - Lake Saginaw dam downstream to Wallkill River	FW2-TP(C1)

(Hamburg Mtn.) - The first tributary, just south of 		FW1(tm)

Hamburg Mtn., flowing toward the Wallkill River and located entirely
within the Hamburg Mtn. Wildlife Management Area

(Ogdensburg) - Tributary from the outlet of Heaters 		FW2-TP(C1)

Pond to the confluence with the Wallkill River

WANTAGE BROOK (Wantage) - Entire length				FW2-NT

WAWAYANDA CREEK

(Vernon) - State line to Pochuck Creek, except 			FW2-TM

unnamed tributary described below

  TRIBUTARIES

(Wawayanda) - Source to State line				FW2-NT

(Wawayanda State Park) - Segments within State 		FW2-NT(C1)

Park boundaries, except Livingston Ponds Brook as noted above

WAWAYANDA LAKE (Wawayanda)					FW2-TM(C1)

WHITE LAKE (Sparta)							FW2-TM

WILDCAT BROOK (Franklin) - Entire length				FW2-NT

WILLOW (QUARRYVILLE) BROOK (Wantage) - Entire length	FW2-TM

(h)  FW1 waters are listed in Table 6 by tract within basins:

Table  6

ATLANTIC COASTAL PLAIN BASIN

ALLAIRE STATE PARK	MANASQUAN RIVER WATERSHED

Those portions of the first and second southerly tributaries to the
Manasquan River, which are west of Hospital Rd. and are located entirely
within the boundaries of Allaire State Park

The easterly tributary to Mill Run upstream of Brisbane Lake, located
entirely within the boundaries of Allaire State Park

BASS RIVER STATE FOREST	BASS RIVER WATERSHED

Tommy's Branch from its headwaters downstream to the Bass River State
Forest Recreation Area service road

Falkenburg Branch of Lake Absegami from its headwaters to the Lake

GREENWOOD FOREST	CEDAR CREEK WATERSHED

WILDLIFE MANAGEMENT 		Webbs Mill Branch and tributaries, located 

AREA		entirely within the Greenwood Forest Wildlife 	Management Area
boundaries

Chamberlain's Branch from its origins to a point 1000 feet west of Route
539

Those portions of the tributaries to Chamberlain's Branch originating
and wholly contained within the boundaries of the Greenwood Forest
Wildlife Management Area

WADING RIVER WATERSHED

Westerly tributary to the Howardsville Cranberry Bog Reservoir and other
tributaries that are located entirely within the boundaries of the
Greenwood Forest Wildlife Management Area

ISLAND BEACH STATE PARK	BARNEGAT BAY WATERSHED

All freshwater ponds in Island Beach State Park

LESTER G. MACNAMARA 	GREAT EGG HARBOR RIVER WATERSHED

WILDLIFE MANAGEMENT 	Hawkins Creek and tributaries and the next 

AREA	adjacent,northern stream and tributaries that enter the Great Egg
Harbor River, from their origins downstream to where the influence of
impoundment begins

TUCKAHOE PUBLIC FISHING 	See LESTER G. MACNAMARA WILDLIFE AND 

HUNTING GROUNDS 		MANAGEMENT AREA



WHARTON STATE FOREST	MULLICA RIVER WATERSHED

Deep Run and tributaries from their headwaters downstream to Springer's
Brook

Skit Branch and tributaries from their headwaters downstream to the
confluence with Robert's Branch

Tulpehocken Creek and tributaries from their sources downstream to the
confluence with Featherbed Branch

The westerly tributaries to Tulpehocken Creek and those natural ponds
within the lands bounded by Hawkins (Bulltown-Hawkins) Rd., Hampton Gate
(Tuckerton) Rd., and Sandy Ridge Rd.

Stream in the southeasterly corner of the Wharton State Forest, located
between Ridge Rd. and Seaf Weeks Rd. downstream to the boundaries of
Wharton State Forest

Brooks and tributaries to the Mullica River between and immediately to
the west of Tylertown and Crowleytown, from their headwaters downstream
to the head of tide at mean high water

The easterly branches of the Batsto River from Batsto Village upstream
to the confluence with Skit Branch

Gun Branch from its headwaters downstream to U.S. Route 206

DELAWARE RIVER BASIN

ALLAMUCHY STATE PARK	MUSCONETCONG RIVER WATERSHED

All those tributaries to Deer Park Pond and its outlet stream, that are
located entirely within the boundaries of Allamuchy State Park

PEQUEST RIVER WATERSHED

All tributaries that are located entirely within Allamuchy State Park
and flow into Allamuchy Pond

BELLEPLAIN STATE FOREST	EAST CREEK WATERSHED

All tributaries to Lake Nummi from their origins downstream to the Lake.

Those two tributaries to Savages Run and portions thereof downstream of
Lake Nummi, which are located entirely within the Belleplain State
Forest boundaries

A stream and its tributaries that originate just south of East Creek
Mill Rd., 1.2+ miles north-northeast of Eldora, and are located entirely
within the boundaries of Belleplain State Forest

WEST CREEK WATERSHED

The portion of the tributary to West Creek that originates about 0.9
miles southeast of Hoffman's Mill and is located entirely within the
boundaries of Belleplain State Forest

Eastern branch of the easterly tributary to Pickle Factory Pond from its
origin to its confluence with the western branch

Those tributaries to the stream which enter West Creek approximately 0.5
miles upstream of Hoffman's Mill and which are located entirely within
the boundaries of Belleplain State Forest

COLLIERS MILLS WILDLIFE 	CROSSWICKS CREEK WATERSHED

MANAGEMENT AREA		All tributaries to Lahaway Creek originating 

in the Colliers Mills Wildlife Management Area north-northeast of
Archers Corner, from their origins downstream to the boundaries of the
Colliers Mills Wildlife Management Area

DELAWARE WATER GAP 	DELAWARE RIVER WATERSHED

NATIONAL RECREATION	All tributaries to Flat Brook flowing from 

AREA	the Kittatinny Ridge and located entirely within the boundaries of
the Delaware Water Gap National Recreation Area

Rundle Brook upstream of Sussex County Route 615

Smith Ferry Brook



Donkey's Corner Brook

Sambo Island Brook and Pond

Coppermine Brook in Pahaquarry

Dunnfield Creek to Route I-80

DIX WILDLIFE MANAGEMENT 	MIDDLE MARSH CREEK WATERSHED

AREA		All fresh waters which originate in and 

are located entirely within the boundaries of the Dix Wildlife
Management Area

EDWARD G. BEVAN WILDLIFE 	MAURICE RIVER WATERSHED

MANAGEMENT AREA		Joshua and Pine Branches of Buckshutem 

Creek to their confluences with Buckshutem Creek

Gravelly Run downstream to the boundaries of the Edward G. Bevan
Wildlife Management Area

NANTUXENT CREEK WATERSHED

Cedar and Mile Branches to Shaw's Mill Pond

DIVIDING CREEK WATERSHED

Those tributaries to Cedar Creek which originate in and are located
entirely within the boundaries of the Edward G. Bevan Wildlife
Management Area

Those portions of tributaries to Dividing Creek, located entirely within
the boundaries of the Edward G. Bevan Wildlife Management Area

FLATBROOK-ROY WILDLIFE 	FLAT BROOK WATERSHED

MANAGEMENT AREA		The tributary to Little Flat Brook which 

originates north of the Bevans-Layton Rd., downstream to the first pond
adjacent to the Fish and Game headquarters building

Two tributaries to Flat Brook which originate along Struble Rd. in
Stokes State Forest, downstream to the confluence with Flat Brook within
Flatbrook-Roy Wildlife Management Area boundaries

GLASSBORO WILDLIFE 	MAURICE RIVER WATERSHED

MANAGEMENT AREA		The portion of a branch of Little Ease Run 

situated immediately north of Stanger Avenue, and entirely within the
Glassboro Wildlife Management Area

First and second easterly tributaries to Little Ease Run north of
Academy Road

HIGH POINT STATE PARK 	CLOVE BROOK WATERSHED

AND STOKES STATE FOREST		The second and third northerly tributaries 

to Clove Brook, those tributaries to Steeny Kill Lake, Steeny Kill Lake,
and those downstream of the Lake which originate in High Point State
Park, downstream to the confluence with Clove Brook or to the boundaries
of High Point State Park

The northerly tributaries to Mill Brook due west of Steeny Kill Lake,
within the High Point State Park boundaries

FLAT BROOK WATERSHED

All surface waters of the Flat Brook drainage within the boundaries of
High Point State Park and Stokes State Forest except the following:

(1) Saw Mill Pond and Big Flat Brook downstream to the confluence with
Flat Brook; 

(2) Mashipacong Pond and its outlet stream (Parker Brook) to the
confluence with Big Flat Brook;

(3) Lake Wapalanne and its outlet stream to the confluence with Big Flat
Brook;

(4) Lake Ocquittunk and waters connecting it with Big Flat Brook;

(5) Stony Lake and its outlet stream (Stony Brook) downstream to the
confluence with the Big Flat Brook;

(6) Kittatinny Lake, that portion of its inlet stream outside the Stokes
State Forest boundaries, and its outlet stream, including the Shotwell
Camping Area tributary, to the confluence with Big Flat Brook;

(7) Deer Lake and its outlet stream to Lake Ashroe;

(8) Lake Ashroe, the portions of its tributaries outside the Stokes
State Forest boundaries, and its outlet stream to the confluence with
Big Flat Brook;

(9) Lake Shawanni and its outlet stream to the confluence with Flat
Brook;

(10) Crigger Brook and its tributary to the confluence with Big Flat
Brook

SHIMERS BROOK WATERSHED

The portion of Shimers Brook and its tributaries that are located within
the boundaries of High Point State Park

JOHNSONBURG NATURAL 	PEQUEST RIVER WATERSHED

AREA	Mud Pond and its outlet stream, Bear Creek, to the Erie-Lackawanna
Railroad trestle,north of Johnsonburg



LEBANON STATE FOREST	RANCOCAS CREEK WATERSHED

Deer Park Branch and tributaries near Buckingham, downstream to the
confluence with Pole Bridge Branch

Tributaries to the South Branch of Mount Misery Brook located entirely
within the boundaries of Lebanon State Forest

Cooper Branch and tributaries downstream to Pakim Pond and those
tributaries to Coopers Branch downstream of Pakim Pond that are located
entirely within the boundaries of Lebanon State Forest

Shinns Branch and tributaries located entirely within the boundaries of
Lebanon State Forest, from their sources to the forest boundary

Jade Run located entirely within the boundaries of Lebanon State Forest

MacDonalds Branch and tributaries located entirely within the boundaries
of Lebanon State Forest, from their sources to the forest boundary

MILLVILLE FISH AND GAME 	See EDWARD G. BEVAN WILDLIFE 

TRACT		MANAGEMENT AREA

PASADENA WILDLIFE 	RANCOCAS CREEK WATERSHED

MANAGEMENT AREA		The two easterly branches of the South Branch 

of Mount Misery Brook, located entirely within the boundaries of the
Pasadena Wildlife Management Area

PEASELEE WILDLIFE 	MAURICE RIVER WATERSHED

MANAGEMENT AREA		Middle Branch of Muskee Creek from its origin to the

boundaries of the Peaselee Wildlife Management Area

Cedar Branch of the Manumuskin River, from its origin to the boundaries
of the Peaselee Wildlife Management Area

Those portions of tributaries to Slab Branch located entirely within the
boundaries of the Peaselee Wildlife Management Area

WASHINGTON CROSSING 	STEELE RUN WATERSHED

STATE PARK		That portion of Steele Run, located within 

the boundaries of Washington Crossing State Park, to the confluence with
the westerly tributary

WHITTINGHAM WILDLIFE 	PEQUEST RIVER WATERSHED

MANAGEMENT AREA		Northwesterly tributaries to the Pequest River, 

including Big Spring, located within the boundaries of the Whittingham
Wildlife Management Area southwest of Springdale, from their origins to
their confluence with the Pequest River

WORTHINGTON STATE 	DELAWARE RIVER WATERSHED

FOREST	Sunfish Pond and its outlet stream to the Delaware River.  All
unnamed waters located entirely within the boundaries of the Worthington
State Forest

DUNNFIELD CREEK WATERSHED

Dunnfield Creek to I-80

PASSAIC RIVER, HACKENSACK RIVER, NY HARBOR COMPLEX BASIN

A. S. HEWITT STATE FOREST	WANAQUE RIVER WATERSHED

Portions of Cooley Brook and tributaries which originate and are located
entirely within the boundaries of Hewitt State Forest

Surprise Lake

Portions of Green Brook and tributaries which originate and are located
entirely within the boundaries of Hewitt State Forest

West Pond

BERKSHIRE VALLEY	ROCKAWAY RIVER WATERSHED

WILDLIFE MANAGEMENT 		Stephens Brook north of the boundaries 

AREA		of the Berkshire Valley Wildlife Management Area

CITY OF NEWARK HOLDINGS 	PEQUANNOCK RIVER WATERSHED

AND WAWAYANDA STATE 		Cedar Pond and all tributaries

PARK

Hanks Pond and all tributaries

Tributary to Pequannock River at Green Pond Junction from its origin
downstream to Route 23

Tributary joining the main stem of the Pequannock River 3500+ feet
southeast of the Sussex-Passaic County line, near Jefferson from its
origin to about 2000 feet upstream of the pond

Pacack Brook and its tributaries upstream of Canistear Reservoir,
located entirely within the boundaries of the Newark watershed and
Wawayanda State Park

Cherry Ridge Brook and its tributaries north of Canistear Reservoir,
located entirely within the boundaries of the Newark watershed lands and
Wawayanda State Park

The southern branch of the easterly tributary to Canistear Reservoir

Pequannock River and tributaries upstream of the confluence with Pacack
Brook



The northwestern tributary to Oak Ridge Reservoir

The portion of the westerly tributary to Lake Stockholm Brook, from its
origins to about 1000 feet south of the Route 23 Bridge, located
entirely within the boundaries of the Newark watershed

Lud-Day Brook downstream to its confluence with the southwestern outlet
stream from Clinton Reservoir just upstream of the confluence of the
outlet stream and a tributary from Camp Garfield

Brook between Hamburg Turnpike and Vernon-Stockholm Road, downstream to
its confluence with Lake Stockholm Brook, north of Rt. 23

RARITAN RIVER BASIN		NONE

WALLKILL RIVER BASIN

CITY OF NEWARK HOLDINGS 	LAKE LOOKOUT BROOK WATERSHED

AND WAWAYANDA STATE 		Lake Lookout, Lake Lookout Brook and 

PARK		tributaries from its headwaters in the Newark City holdings,
downstream through the State-owned Wawayanda State Park to the
confluence with the outlet stream from Lake Wawayanda

HAMBURG MOUNTAIN 	SAND HILLS BROOK WATERSHED

WILDLIFE MANAGEMENT	The upstream portion of Sand Hills Brook, including
the pond at its headwaters, located entirely within the boundaries of
the Hamburg Mtn. Wildlife Management Area

BLACK CREEK WATERSHED

All those portions of three tributaries to Black Creek originating in
the Hamburg Mtn. Wildlife Management Area, from their origin downstream
to the Management Area boundaries

FRANKLIN POND CREEK WATERSHED

The first tributary to Franklin Pond Creek just south of Hamburg
Mountain, flowing toward the Wallkill River and located entirely within
the Hamburg Mtn. Wildlife Management Area

HAMBURG CREEK WATERSHED

The third tributary just southwest of Hamburg Mountain, which flows
toward the Wallkill River and is located entirely within the Hamburg
Mtn. Wildlife Management Area

HIGH POINT STATE PARK	CLOVE RIVER WATERSHED

Those portions of the two northernmost tributaries to Clove River which
are located entirely within the boundaries of High Point State Park, and
are immediately east of Lake Marcia

RUTGERS CREEK WATERSHED

The Cedar Swamp headwaters of the tributary to Rutgers Creek, located
entirely within the boundaries of High Point State Park, just south of
the New Jersey-New York state line

SUSSEX BOROUGH WATER 	LAKE RUTHERFORD WATERSHED

SUPPLY LAND		Lake Rutherford and tributaries, located

northwest of Colesville

WAWAYANDA STATE PARK	LAUREL POND WATERSHED

Laurel Pond, and its outlet stream and tributaries downstream to the
outlet stream from Lake Wawayanda

(i)  The following are the Outstanding National Resource Waters of the
State:

Table  7

1. FW1 Waters; and

2. PL Waters.

		

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 ADVANCE \d12 

7:9B-1.14(c) Surface Water Quality Criteria for FW2, SE and SC Waters

(Expressed as maximum concentrations unless otherwise noted)

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Substance							Criteria							Classifications

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