This project is being done in cooperation with the
Chester County Water Resources
Authority.
NEED FOR THE PROJECT
The Stream Conditions of Chester County Biological Monitoring
Network has been used to collect biological and chemical data from 51
sites on the major streams in the County since 1970. The data
from 1981-97 had not been formally analyzed and reported. An analysis
of the data using biometric techniques was needed to provide the County
with information on the current and past surface-water-quality
conditions. This information is needed in support of the County's
Landscapes Program. Since the Stream Conditions of Chester County
Biological Monitoring Network was established in 1970, Chester County
has continued to undergo rapid urbanization as agricultural land is
converted to residential, commercial, and industrial areas. These
changes in land use have caused many changes in the stream systems
including streamflow, sedimentation, nutrients loads, and pesticides
concentrations. The effect urbanization has had on surface-water quality
can be documented in the biological samples collected over the past 27
years. In addition,
new methods of analyzing macroinvertebrate data have been developed
since the data from 1970-80 were analyzed. These new techniques need to
be applied to the data so that an evaluation of the County's
surface-water quality can be made to determine the affects of past
environmental and land use practices.
PROJECT OBJECTIVES
APPROACH
Literature review
A literature search was conducted to
obtain the latest information available on the evaluation of water
quality using benthic macroinvertebrate data. This included current
methods being used by the U.S. Environmental Protection Agency,
state and local governments, and other federal agencies.
Data base creation
A new data base
was created to store the data generated from the identification of
macroinvertebrate samples. The Stream Conditions of Chester County
Biological Monitoring Network has generated a large amount of data that
is now available in a flexible interactive data base. This data base
is compatible with software used to analyze the data.
Trend analysis
Brillouin's Diversity Index was calculated at all stations for
1981-97. The Stream Conditions of Chester County Biological Monitoring
Network has used Brillouin's Diversity Index as the main method of
evaluation. Brillouin's Diversity index is based on the different kinds
of organisms (taxa) present in a community and their relative
abundances. In general, diversity is high if a community has many taxa
and their abundances are evenly distributed; diversity is low if the
taxa are few and their abundances are unevenly distributed.
Brillouin's Diversity Index is retained as measure of
water-quality for this study. Kendall's tau test for trend was
applied to the Brillouin's Diversity Index values. Hilsenhoff's Biotic
Index will be calculated at all stations from 1981-97. Hilsenhoff's
Biotic Index was calculated back to 1981 so that it can be compared
to Brillouin's Diversity Index. Hilsenhoff's Biotic Index is based on
tolerance values assigned to individual organisms. The tolerance values
used were obtained from the New York State Department of
Environmental Conservation macroinvertebrate rankings.
Organisms are given a tolerance value based on their ability to
withstand organic pollutants. Chemical results for selected
parameters were evaluated for trends using Kendall's tau
test at each station from 1981-97.
Calculation of biometrics Data
Data analysis used a multimetric approach. Each metric measures a
different part of community structure and has a different response to
environmental stress. The mulitimetric approach increases the
chance that an environmental stress will be detected. The following
metrics were calculated: Brillouin's Diversity Index, Hilsenhoff's Biotic
Index, taxa
richness, percent dominate taxa (relative abundance), and EPT
(Ephemeroptera, Plecoptera, Trichoptera) taxa, percent EPT. The classification
system developed by The New York State Department of Environmental
Conservation was used to determine functional feeding groups and
assign IBI and tolerant-facultative-intolerant values. The metrics were
calculated on the data for 1981-97.
Analysis of chemical data
Results from bottom-sediment sampling for
metals and pesticides were compared with USEPA or other available
standards. Trends in
biological measures were compared to chemical values to determine if
relations are present between them.
Rating of sites
Using the information
from all the biometrics calculated, streams or portions of streams that
are considered of high quality or biologically stressed are
identified.
REPORTS RESULTING FROM THIS PROJECT
FACT SHEETS:
Reif, A.G., 2002, Assessment of stream quality using biological indicies at selected sites in the
Schuylkill River Basin,
Chester County, Pennsylvania, 1981-97: U.S. Geological Survey Fact Sheet FS-114-02, 4 p.
[ PDF file ]
Reif, A.G., 2002, Assessment of stream quality using biological indicies at selected sites in the
Big Elk and Octoraro
Creek Basins, Chester County, Pennsylvania, 1981-97: U.S. Geological Survey Fact Sheet FS-115-02, 4 p.
[ PDF file ]
Reif, A.G., 2002, Assessment of stream quality using biological indicies at selected sites in the
Delaware River Basin,
Chester County, Pennsylvania, 1981-97: U.S. Geological Survey Fact Sheet FS-116-02, 4 p.
[ PDF file ]
Reif, A.G., 2002, Assessment of stream quality using biological indicies at selected sites in the
Brandywine Creek Basin,
Chester County, Pennsylvania, 1981-97: U.S. Geological Survey Fact Sheet FS-117-02, 4 p.
[ PDF file ]
Reif, A.G., 2002, Assessment of stream quality using biological indicies at selected sites in the
Red Clay and White Clay Creek Basins,
Chester County, Pennsylvania, 1981-97: U.S. Geological Survey Fact Sheet FS-118-02, 4 p.
[ PDF file ]

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