Prepared by Deborah
J. Kratzer, Kratzer Environmental
Services
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Table of Contents
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Goal of the ERI
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The goal of the ERI is
to provide a planning tool containing resource information, data and maps
that can be used as part of the Master Plan, as a reference when reviewing
development proposals, and as a guide in other township activities in order
to better protect the township’s natural resources and the overall health and
welfare of the community. |
Methods
Funding for the project was obtained from the
Lower Delaware Wild and
The ERI is intended for preliminary
assessments of projects and cannot
substitute for on-site testing and evaluations. Data sets have various accuracies; most GIS
data layers have an accuracy of + 40 feet, but some are
accurate to only + 166.7 feet, while one has an accuracy of +
4 feet. GIS data sources require a
“disclaimer” printed on each map.
When
new or updated information becomes available, or new issues emerge, updates should
be appended to the ERI.
General
Description and Land Use
Recent
changes can be seen in land use maps created from aerial photographs taken in
1986 and 1995. Of 900 changes in land
use, over 500 of these changes may be characterized as impacts to natural
habitats. These include (in order of
frequency) a change from agriculture to residential use; from forest to
residential; from wetlands to residential; forest to agriculture; and wetland
to agriculture.
Climate
and Meteorology
Climate
is a major factor in determining the kinds of plants and animals found in an
ecosystem. NJ has a temperate climate because it has mild average temperatures, four
seasons, and rainfall distributed throughout the year. Since this region is surrounded by land, it
can be characterized as having a continental type of climate with minimal
influence from the
In
Flemington, annual precipitation for the period 1926-2000 has averaged 46.42
inches. On average, the fall months are
usually the driest, although record rainfalls are more likely to occur then,
due to tropical storms. An average of 40
to 50 inches of snow falls annually (about 10” of snow equals 1” of rain),
which may occur between October and April.
9 or
earlier). The first frost in fall is around October 13th (in
one year out of 10, the first frost may be October 2 or earlier). The exact dates vary within the county as
well as from one year to another.
Air Quality
Several
air pollutants rank among the highest risks to human health, including
ground-level ozone, particulate matter, radon, secondhand tobacco smoke, and
volatile organic compounds (VOCs). Air
pollution is estimated to have medium to medium-high socioeconomic impact, and also
impacts ecological quality.
On hot
summer days, when pollutant levels are worst, winds in NJ are usually blowing
from the southwest, carrying air pollution from the
Of the six Clean Air Act Criteria Pollutants, (ozone, sulfur
dioxide, carbon monoxide, nitrogen dioxide, particulate matter, and lead) NJ is
now in compliance with all except for ozone.
Air
toxics include a long list of many different types of compounds from heavy
metals to volatile organic compounds (VOCs) such as benzene. Although the trend of pollutant
concentrations is downward from 1996 to 2000, many of them still exceed the
NJDEP health benchmarks.
Pollution
that is deposited on land or water from the air is called atmospheric deposition. The major pollutants of concern are sulfur
dioxide (SO2), nitrogen oxides (NOx), mercury (Hg), and
volatile organic compounds (VOCs). In
addition, the presence of these pollutants changes the pH of the precipitation
which can harm plants and aquatic life.
2001 data from Washington Crossing show that rainfall had a mean pH
value of 4.3 (normal rainfall has a pH of about 5.6). Trends show that concentrations of SO2
and VOCs are improving, while NOx and pH remain about the same. Mercury
levels have decreased, but are still present at levels far higher than natural
levels.
Radon is a
radioactive gas that is naturally occurring in NJ rocks, soil and ground water,
and a common concern in
Geologic history
Five hundred million years ago, the
land that is now NJ was at the bottom of a warm tropical sea, close to the
equator. About 400 million years ago,
During the Triassic Period (245 to
208 million years ago), flashfloods eroded the mountains to the east and south
of what is now Kingwood, dropping mud and silt in extensive floodplain
deposits, gradually filling the valleys.
The sediments became rock under the pressure of each successive layer of
mud, silt or sand. Dinosaurs walked on
these mudflats, leaving footprints that occasionally became fossilized.
Roughly 200 million years ago, the
supercontinent broke apart, and the
If additional sediments were laid
down after that time, they have since been eroded away.
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Bedrock
Name |
Thick- ness |
Physical
character of rocks |
%
of Twp. |
|
Trl - Lockatong Formation |
3,800 ft. |
dolomitic or silty
argillite, mudstone, sandstone, siltstone, and minor silty
limestone |
29% |
|
Trlr - Red Bed Lockatong Formation |
dolomitic or silty
argillite, mudstone, sandstone, siltstone, and minor silty
limestone, occasionally red |
6% |
|
|
JTrp - |
6,200 ft. |
siltstone
and shale |
49% |
|
JTrpg – Passaic Formation Gray bed |
sandstone,
siltstone and shale |
14% |
|
|
Jd - Diabase and granophyre
|
|
diabase,
medium- to coarse-grained |
2% |
|
Trs - |
6,000 ft. |
sandstone,
mudstone, silty mudstone, argillaceous siltstone,
and shale |
.06% |
Physiography and
Topography
Kingwood is within the
Today’s topography resulted from
relatively recent erosion from a nearly flat plain. The elevation ranges from 90 feet above mean
sea level (adjacent to the
Soils
The
soil is the unconsolidated mineral
material on the immediate surface of the earth and which serves as the medium
for growth of land plants. The
characteristics of each soil type have developed over time (usually many
thousands of years). Soil is a basic
resource for food production, in addition to its essential role in collecting
and purifying water before it enters the ground water. However, soil itself can be a pollutant as
dust in the air or as sediment in water.
The US Department of Agriculture Natural
Resources Conservation Service (USDA NRCS) made soil surveys in 1974 to
determine soil characteristics and capabilities and to help people understand
soils and their uses (accurate within about 5 acres).
There are
56 different map units are present in Kingwood. The ERI includes maps and a
table of several important characteristics of these soils. Depth to high water table is shown below as
an example. When viewed together, most
soils in Kingwood have limitations from at least one of the following
factors: poor drainage, high water
table, shallow bedrock or steep slopes.
The 1974 Soil Survey report also placed an emphasis on limitations of
the ground water.
Water
Surface water is water that is visible above the ground surface,
such as creeks, rivers, ponds, lakes, and wetlands. Ground
water 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. An aquifer
is a water-bearing rock or rock formation where water is present in usable
quantities. Water is constantly recycled through the hydrologic cycle.
The Aquifers in
The
aquifers in
The Stockton,
Lockatong, and Passaic formations are characterized by several layers of
extensively fractured rocks (water-bearing units) that typically are 1 to 10
feet thick interbedded with layers of sparsely fractured rocks (confining
units) that typically are 30 to 100 feet thick.
These geologic formations extend thousands of feet below ground, but the
density of fractures decreases with depth.
Water-bearing, interconnected fractures are present only from the land
surface to a depth of about 500 feet.
For this reason, wells extended beyond 500 feet usually do not increase
well productivity (the extra storage provided by the greater length of the well
bore-hole may be necessary, however, to supply enough water for the well’s
intended use). The aquifer consists of
the whole 500 foot thick sequence of water bearing units and confining
units.
The
argillite rocks of the Lockatong formation and diabase rocks are among the
poorest (lowest yielding) aquifers in NJ due to the scarcity of fractures.
Movement
of ground water is usually quite slow, on average; ranging from about one foot
per day to perhaps ½ inch per month.
However, ground water in Kingwood, because it is present in fractures,
can potentially move much more quickly.
The rates of movement in large fractures may approach those observed in
surface streams. A contaminant could
travel quickly through fractures, with little soil contact to allow for
filtration or degradation of pollutants.
Thus, a well located on a large fracture might have a very good yield,
but may be highly susceptible to contamination.
In 1995, the Kingwood
Township Planning Board contracted Robert Hordon to analyze ground water data
from the argillite formation of
Ø
Depth: Well depths ranged from 100 to 800 feet,
averaging 399 feet. Newer wells are
being drilled hundreds of feet deeper than 30 years ago.
Ø
Yield: Well yields ranged from 0.125 gpm (one pint
per minute) to 100 gpm. The mean
(average) was 9 gpm and the median (middle value) was 5 gpm. Current yields are less than half of historic
yields.
Ø
Drawdown
during pump test: Drawdowns varied from 0 feet to 699 feet. The mean was 222 and median drawdown was 190
feet. These numbers are very high, and
provide evidence that the argillite is a poor aquifer.
Ø
Nitrate-nitrogen: Nitrate-nitrogen values were available for
105 of the wells. Many were below the
detection limit, but the highest was 6.41 mg/L (the criteria for
nitrate-nitrogen is 10 mg/L, however, any value over the natural background
level of 2 mg/L is indicative of pollution, possibly from septics
or fertilizer use). Hordon used the Trela-Douglas dilution model to estimate the lot size
required to allow infiltration of precipitation for maintaining a
nitrate-nitrogen concentration less than 10 mg/L. This model and other nitrate dilution models
can be used to predict future nitrate levels under various planning scenarios.
Recharge
Ground water recharge is defined as water added to an aquifer (for example,
precipitation that seeps into the ground).
A ground water recharge area
is the land area that allows precipitation to seep into the saturated
zone. These areas are generally at
topographically high areas with discharge areas at lower elevations, commonly
at streams or other water bodies (i.e. the ground water returns to surface
water). Most ground water flows through
the shallow layers of soil and weathered bedrock to the nearest stream. A smaller percentage penetrates deeper and
recharges the aquifer.
NJ
Geological Survey developed a method which estimates g round water recharge
(but not aquifer recharge), and is useful for evaluating the relative effect of
present and future land uses on recharge areas.
There were a number of assumptions made for the calculations and model
inputs which limit the accuracy of the method, such as the calculated ground
water recharge includes any water entering the ground (lesser amounts actually
enter the aquifer) and wetlands and water bodies were eliminated from analysis,
because the direction of flow between ground water and surface water is
site-specific and also varies seasonally, and this level of detail was beyond
the scope of the study (these areas were assumed to provide no recharge or
discharge and others. Keeping these
limitations in mind, the method estimated recharge rates from 1 to 16 inches
per year in Kingwood, for estimated average annual subsurface recharge. This represents 2 to 34% of precipitation.
Other
studies estimate that of this amount, only between 6 - 20% reaches the aquifer. Using these estimates, Kingwood may have
usable recharge of 0.06 to 3.2 inches of water added to ground water per
year. While it is unknown at this time
which figure is closer to actual conditions in Kingwood, the general principle
is this: Recharge is limited. Therefore, if withdrawals of ground water are
greater than the recharge amounts, the aquifer would experience a continuous
net reduction in the available water supply.
Ground Water Quality
Pollution, such as nitrates, bacteria, metals,
pesticides and antibiotics, can enter ground water via non-point sources
(including septic systems and runoff from fields and roads), point sources
(including discharge pipes), and rain.
The NJ Comparative Risk Project (2003) identified a number of possible
human health risks from drinking water, including lead (which, when present, is
usually from the plumbing (NJDEP, 2004)), radon, arsenic, MTBE, nitrates, and
waterborne pathogens.
The NJ Private Well Testing Act
(N.J.S.A. 58:12A-26 et seq.) became effective in September 2002. The PWTA requires mandatory statewide private
well testing upon the sale of a house. A
report summarizing the first year of data generated by the PWTA revealed that,
out of 25 wells sampled in Kingwood Township, 6 wells (24%) exceeded a maximum
contaminant level for a primary drinking water standard (2 for bacteria, 1 for
nitrate, and 3 for arsenic) (compared to average exceedance
rate of 8% statewide and 11% in Hunterdon County). The report also concluded that: 1.) certain
geologic formations in the Piedmont region contain layers that may leach
arsenic into the ground water as it passes through, and 2.) wells drilled into
bedrock aquifers are more susceptible to fecal coliform contamination than
wells in the coastal plain. In time, the
data from the PWTA can be used to determine water quality trends and
assessments of the safety of private well sources.
The NJ
Geological Survey (NJGS) and the United States Geological Survey (USGS) are also
involved in ground water monitoring and protection.
Known Contaminated
Sites
The Known Contaminated Sites List for NJ 2001 are those sites and
properties within the state where contamination of soil or ground water has
been identified or where there has been, or there is suspected to have been, a
discharge of contamination (note some may have been fully remediated,
and new sites may not be included).
These include Magnesium Elekrton Inc., Barbertown Garage, DeRewal Chemical Company,
There are 15 Underground Storage
Tanks listed by NJDEP (8 within Kingwood, 7 within shared watersheds), 9
require no further action, 4 are assigned to a program, and 2 are awaiting
assignment. In addition, the
Ground Water Level
Monitoring
The ground water level is the distance from the land surface (i.e. top
of well casing) to the water in a well.
Ground water level monitoring is critical for determining the current
state of the ground water, identifying trends and predicting ground water
drought. Kratzer Environmental Services
initiated ground water monitoring in one well in the Lockatong aquifer in March
1998. The well selected is located in
the Lockatong argillite geology, in Cain’s Run (also known as Warsaw Creek)
watershed. Preliminary data suggests
that it takes only 4-12 hours for precipitation to begin to recharge this well,
demonstating minimal water-filtration capacity and
vulnerability to ground water contamination from surface pollution sources.
Seasonal variation in this well is
about 11 feet.
Watersheds
A watershed (or basin) is the land area
within the confines of a drainage divide in which all surface runoff will drain
into a river, river system, or body of water.
Watershed management is the
process of managing and protecting all of the water resources within the area
of a watershed, rather than on a site-specific basis.
All of
Surface Water Quality
Standards
Surface
water classifications are names assigned by the NJDEP to group waters
according to designated uses (designated uses include potable water,
propagation of fish and wildlife, recreation, agricultural and industrial
supplies, and navigation) and water quality criteria. The criteria
are numerical targets for constituent concentrations (such as toxic pollutants)
or narratives that describe in-stream conditions to be attained, maintained or
avoided, so that the specified uses are protected for the different use
classifications.
The entire length of Warford Creek
has been adopted as a Category One (C1) designation. NJDEP proposed an upgrade to C1
classification for a number of streams in 2003, including Little
Nishisakawick Creek, Lockatong Creek, Nishisakawick and Wickecheoke
Creek. The C1 designation provides
additional protections that help prevent water quality degradation and discourage
development where it would impair or destroy natural resources and
environmental quality.
Point Source Pollution
Point source pollution refers to
discernible, confined, and discrete conveyance.
There is only one such discharge existing within
Nonpoint source or NPS pollution is any
man-made or man-induced activity, factor, or condition, other than a point
source, from which pollutants are or may be discharged. When water flows off impervious surfaces,
such as buildings, homes, parking lots and roads and through storm drains and
ditches, this type of Nonpoint source pollution is known as stormwater. As the velocity of water increases, the
amount that can infiltrate into the soil and ground water is reduced and
scouring and erosion increase.
In February
2004, the NJDEP instituted new stormwater management requirements that emphasize
increasing ground water recharge and reducing nonpoint
source pollution.
Wetlands
Wetlands are 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. Hydric soils (see wetlands map) are those soils that are wet long enough to periodically produce anaerobic conditions, thereby influencing the growth of plants.
For this GIS data layer, NJDEP
mapped all freshwater wetland polygons greater than 1 acre in area and all
linear freshwater wetland features greater than 10 feet in width. This dataset is intended to serve as a resource
for analysis rather than regulatory delineations. In addition, updates to the maps may be made
based on more in-depth analysis and field inspection for regulatory
purposes. In the map above, the maximum
transition area widths of 150 feet are mapped, because the GIS data does not
distinguish wetland values. Only an
official determination from NJDEP, called a Letter
of Interpretation (LOI) can verify the presence, absence, or boundaries of
freshwater wetlands and transition areas on a site.
Surface Water Quality and Flow Monitoring
Surface
water quality data have been collected at sites on several streams and the
When
monitoring data show that streams exceed the surface water quality standards,
NJDEP has regulations for Total Maximum
Daily Loads (TMDLs) which set goals for reduction
in pollution loads (or inputs) for those parameters for those streams. Several streams in Kingwood will eventually
have TMDLs developed for fecal coliform, total
phosphorus, pH and/or dissolved oxygen.
Fish Consumption
Advisories
When toxic pollutants are present in surface
water, they are consumed by the organisms that live in the water. The process of bioaccumulation is when there is an increase in concentration of
certain fat-soluble chemicals, such as DDT and PCBs, in successively higher
trophic levels of a food chain or web.
This information is intended to help individuals make an informed choice
on the number of meals of fish to consume.
Species with restrictions due to PCBs and dioxin include American eel,
striped bass and channel catfish.
Species with restrictions due to mercury include largemouth and
smallmouth bass, chain pickerel, yellow and bullhead, sunfish and channel
catfish.
Humans arrived in NJ
at least 7,000 years ago. An
archeological study was done in 1996 at the site of the DeRewal Superfund
site. The study found more than 3,000
Native American artifacts, many dating back more than 1,000 years. Europeans first began settling NJ as early as
1620 and extensively and repeatedly cut the forests down to use the wood, until
only 14% of the land was forested in 1899.
The human population of NJ continued to grow, but the introduction of
coal in 1850 began to allow the woodlands to recover to about 36% forest as of
1987.
Habitat
fragmentation and habitat loss are the highest ranking stressors of statewide
ecological quality. Certain species that
require large expanses of intact habitat are becoming less common. Other factors which impact ecological health
include exotic species (e.g. the hemlock wooly adelgid
(an insect which causes the decline and death of hemlock trees) and exotic
diseases, overpopulations of deer and geese, and pollution.
The largest portion of land in
Wildlife
A variety of plant and animal species enjoy
The largest
herbivore living wild in NJ is the white-tailed deer. Although the deer is a large animal,
individuals tend to stay in a one square mile or less home range.
Biologists have estimated that
before the arrival of European settlers, there were about 8-11 white-tailed
deer per square mile. By the early
1900’s, NJ’s deer herd was reduced to a handful. However, the adaptability of deer to
human-altered habitats has resulted in the current overabundance of the
species. Studies have shown that deer
densities of over 10-15 per square mile have negative impacts on native
songbird and wildflower populations, while deer populations in excess of 20 per
square mile prevent tree regeneration.
For comparison, NJDEP’s hunting figures for Deer Management Zones 10 and
11 (which encompass Kingwood and some surrounding areas) show that between 28
and 34 deer per square mile are taken
by hunters each year, therefore populations are well over the ecological
carrying capacity.
Black bears are the largest
omnivores and coyotes are the largest carnivores found in
Endangered, Threatened
and Special Concern Species
The health of an area’s animal and plant
populations can be an indicator of the health and sustainability of the
environment for people. The decline or
disappearance of one (or more) species may signal the deterioration of the
habitat. Other species, and human health
and welfare, may soon follow. Preserving
the future of endangered and threatened species helps preserve our own species,
benefiting human health and quality of life by protecting watersheds,
preserving land in its natural state, and restoring wildlife habitat. Many people also place an intrinsic value on
all species.
A search of
NJDEP Division of Parks and Forestry Natural
Heritage Database in November 2003 for rare species presently recorded in
Kingwood Township revealed the documented presence of two critically imperiled
bird species (red-shouldered hawk and vesper sparrow), one imperiled bird
(bobolink), one rare bird (Cooper’s hawk), one threatened and one rare reptile
(wood and map turtles, respectively), and one imperiled amphibian (long-tailed
salamander). Three imperiled or
critically imperiled invertebrates are found within the township (a mussel and
two damselflies), as well as 11 critically imperiled plants (pawpaw,
willow-leaf aster, Nebraska sedge, Meads’ sedge, green violet, wafer ash, Torrey’s mountain mint, coarse grass-like beaked rush,
Missouri gooseberry, beaked corn salad, narrow-leaved vervain)
and 8 imperiled plants (purple giant hyssop, Hitchcock’s sedge, hairy lipfern, wild comfrey, lowland fragile fern, rock
buttercup, veined skullcap, rock spike-moss).
The NJ Department of Environmental
Protection (NJDEP), Division of Fish and Wildlife, Endangered and Nongame
Species Program developed the Landscape
Project. The project’s goal is to
protect NJ’s biological diversity by maintaining and enhancing rare wildlife
populations within healthy, functioning ecosystems. The dataset was created by intersecting endangered,
threatened and rare animal species data with the 1995 Land Use / Land Cover
GIS layer. The resulting data layer
identifies, delineates and ranks (based on the conservation status of species
present) critical habitat statewide.
Each patch is coded for the number of special concern, state threatened,
state endangered and federally listed species present.
Natural Heritage
Priority Sites
These Natural
Heritage Priority Sites are considered some of the best and most viable
occurrences of endangered and threatened plant and animal species and
natural communities, but they do not cover all known habitats for
endangered and threatened species in
The ONLM
has also developed the Natural Heritage Grid Map, which provides a general
representation of the locations of rare plant species and natural
communities as of June 2002, including both historically and recently
documented habitat. The purpose of the
Grid Map is to document rare plant species and natural community habitat to
inform decision-makers who need to address the conservation of natural
resources. The map identifies
potentially sensitive areas, and indicates where custom database searches are
needed for land use decision-making. The
Grid Map does not include habitat for animal species, and not all areas have
been surveyed.
Exotic Species
Exotic species (also called alien or
introduced species) are a threat to natural areas. Exotic species are those that have been
introduced to an area intentionally or unintentionally by people; thus, they
are not part of the original natural community.
Some species adapt well to their
new environment and proliferate. They
compete with native species for space, nutrients and light, and can result in
the local elimination of native species.
As many as 25 percent of the plant species now present in NJ are exotic
plants. Some of these include the Norway
maple, garlic mustard, multiflora rose, Canada thistle, autumn olive and
Japanese honeysuckle. Native plants can
be susceptible to exotic diseases and insects, which they have not evolved
resistance to. Diseases have included
the chestnut blight fungus and Dutch elm disease. Exotic insects include the hemlock wooly adelgid, asian
longhorned beetle, gypsy moth, and pine looper. They weaken
their host trees, which often succumb to successive years of infestation, to
diseases carried by the insect pests, or other environmental stresses.
Historic
Resources
The area that
is now Kingwood has been inhabited by humans for thousands of years. The
Open
Space
Township residents approved the
establishment of a General Capital Fund and Open Space Tax to provide a stable
source of funding for the preservation of the township’s agricultural base,
rural character and natural resources.
The 2000 Open Space and
Recreation Plan established a goal of 2,100 acres of preserved open space,
or 9.2% of the township’s land area. To
date, about 1,200 acres have been preserved or 5.2% of the township (112 acres
owned by the Township; 433 acres owned or conservation easement owned by the
state, a non-profit or Bd of Ed; 651 acres of
preserved farmland).
Conclusion
This ERI
has summarized and presented the objective resource data available for
However,
the Township may use the information in this report to identify areas of
specific concern which require additional protection strategies, such as
further research and monitoring, public outreach and education, habitat
restoration, easements, volunteer projects, and/or revised or new
ordinances.
Important
Internet Resources
twp.kingwood.hunterdon.nj.us/environmental_commission.html
New Jersey Department
of Environmental Protection