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I.
Introduction:
Purpose
of Study: The Earthplace (formerly NCEA) Harbor Watch/River
Watch (HW/RW) Program has been funded by the Connecticut Department
of Environmental Protection (CT DEP) to conduct a fourth and
fifth year water quality monitoring study on the Norwalk River
for the period of July 2002 through June 2004. HW/RW will
collect and analyze water samples for both fecal coliform
bacteria and Escherichia coli (E. coli) bacteria at ten sites
along the main stem of the Norwalk River and the Sivermine
River (one site).
Background:
From June 1998 through May 1999, HW/RW conducted a first-year
water quality monitoring study in the Norwalk River Watershed.
This study was funded by the CT DEP and was intended to provide
water quality information in support of the Norwalk River
Watershed Initiative. The purpose of the study was to obtain
data on the levels of fecal coliform bacteria, oxygen levels
and conductivity at selected locations in the Norwalk River
and in its major tributaries (Silvermine River, Comstock Brook
and Cooper Pond Brook). The study also included the collection
of benthic macroinvertebrates at two Norwalk River sampling
sites and one reference site (Saugatuck River). The study
indicated that fecal coliform bacteria levels frequently exceeded
the state's water quality criterion for Class B water at a
number of sites along the Norwalk River. Most sites met the
dissolved oxygen level CT DEP criterion for Class B waters.
The first year study also showed that conductivity levels
were consistently higher in the upper reaches of the watershed
than in the lower watershed. Based upon the water quality
data collected and the results of the benthic macroinvertebrate
sampling, HW/RW determined that the water quality in the Norwalk
River Watershed was moderately impaired.
At
the conclusion of the first year of study and during the time
when a second year monitoring scope of work document was being
finalized with the CT DEP, HW/RW was successful in obtaining
short-term funding to support continued water quality monitoring.
The Norwalk Harbor Management Commission's Water Quality Committee
and the Norwalk Shellfish Commission provided funding for
water quality monitoring during July and August 1999. Data
collected during this two-month period indicated that fecal
coliform bacteria levels continued to exceed the CT DEP Class
B river bacteria criterion at selected sites in the Norwalk
River Watershed.
The
first year's monitoring effort analyzed only for fecal coliform
bacteria for which the State's Water Quality Standards provides
a criterion for meeting Class B rivers. For the purposes of
this second year study, E. coli bacteria levels were also
reported. E. coli is one of the two bacteria components of
the fecal coliform bacteria group, and it is a more specific
indicator of fecal material arising from humans and other
warm-blooded animals. For recreational waters the US EPA recommends
the use of E. coli because it is a better indicator of a human
health risk from water contact than fecal coliform bacteria.
The
CT DEP and HW/RW executed a contract for the second year funding
in September 1999; the second year monitoring period was from
September 1, 1999 through November 30, 2000. Prior to sampling
for E. coli, HW/RW was required to amend its Quality Assurance
Project Plan (QAPP); as a result, HW/RW only sampled for fecal
coliform bacteria in September and in October. HW/RW was authorized
to begin testing for E. coli bacteria in November 1999. Sampling
took place at 12 sites along the Norwalk River. Monthly reports
were prepared and submitted to the CT DEP and disseminated
to the Norwalk, Ridgefield, Redding, and Wilton health departments
and conservation commissions, the City of Norwalk's Harbor
Commission's Water Quality Subcommittee, and the Norwalk River
Watershed Action Plan Advisory Committee.
Funding
was then made available by the CT DEP to continue testing
on the Norwalk River for a third summer (April 1 to September
30, 2001) based on a continuing interest by Norwalk River
Watershed Advisory Committees and the CT DEP. The same testing
protocols used in 2000 by HW/RW were again used under the
original QAPP which was extended on April 25, 2001 to September
30, 2001 by the EPA's Office of Environmental Measurement
and Evaluation.
Recently,
additional 319 funding was allocated to continue the HW/RW
testing regime on the Norwalk River for twenty-three months
beginning July 2002 and ending June 30, 2004. The same testing
protocols will be used be used to support the recently granted
Total Maximum Daily Load (TMDL) status given to the Norwalk
River by CT DEP. The existing QAPP (expires on September 30,
2002) will be extended to the end of the new contract period
or June 30, 2004. The June 2002 research was done by HW/RW
prior to the beginning of the new contract period of July
2002 in order to maintain continuity for the summer months
of 2002. The Silvermine River (Site SM3) was the only tributary
to be added back to the testing schedule because of strong
interest in a trout habitat restoration project undertaken
by the Norwalk River Watershed Initiative during 2001/2002.
Although
a draft of the monthly report is submitted to the CT DEP for
review and comments prior to its distribution, Harbor Watch/River
Watch is solely responsible for the collection, analysis and
interpretation of the water quality data that is reported
in these monthly reports.
II
Methods and Procedures:
Water
monitoring is carried out under protocols of an EPA approved
and revised EPA Quality Assurance Project Plan (QAPP) re-approved
from September 2002 through September 2004. Monitoring teams
leave the Nature Center in Westport between 9:30AM and 10:00AM,
and return in early afternoon. Each team is comprised of an
experienced leader and one or two trained volunteers. Water
samples are collected at 10 (Figure A1) of the original 23
monitoring sites within the watershed (QAPP Appendix A1.1).
These sites, which represent the more impacted areas, were
selected in concert with the CT DEP for study, because results
from the first year's study consistently demonstrated elevated
fecal coliform bacteria counts. In addition to focusing monitoring
efforts at these sites, it was determined to analyze for both
fecal coliform and E. coli bacteria.
The
following tests are run in situ: dissolved oxygen (QAPP
Appendix A3.1) and conductivity (QAPP Appendix A3.5). Water
and air temperatures, as well as general observations and
storm events are also recorded at each site visit. Observations
are recorded (QAPP Appendix 5) on the HW/RW Data Sheet.
Upon
return to the lab, fecal coliform and E. coli bacteria membrane
filtration tests (QAPP Appendix A3.10) are performed and analyzed
according to Standard Methods, 20th edition (9222D & 9222G)
and recorded (QAPP Appendix 5) on the HW/RW bacteria log.
The frequency of which water quality monitoring for bacteria
concentrations occurs is separated into two seasonal testing
periods. For the period when the three wastewater treatment
plants (WTP) are required to disinfect their wastewater effluent
(May 1st to September 30th) monitoring is done four times
per month. For the period when effluent disinfection is not
required (October 1st to April 30th) monitoring is done monthly.
E.
coli bacteria will be evaluated using the criteria published
in the CT DEP Surface Water Quality Standards, 12/17/02. The
CT DEP E. coli criterion for Class AA, A, and B water is established
at three levels (Table1).
Table
1: CT DEP criterion for E. coli bacteria levels as applied
to recreational use, effective 12/17/02.
Designated
Use |
Class |
Indicator |
Criteria |
|
|
|
|
Recreation |
|
|
|
Designated
Swimming |
AA,
A, B |
Escherichia
coli |
Geometric
Mean less than 126/100; Single Sample Maximum 235/100 |
Non-designated
Swimming |
AA,
A, B |
Escherichia
coli |
Geometric
Mean less than 126/100; Single Sample Maximum 410/100 |
All
Other Recreational Uses |
AA,
A, B |
Escherichia
coli |
Geometric
Mean less than 126/100; Single Sample Maximum 576/100 |
The
Norwalk River is suitable for non-designated swimming, because
people swim in some of the deeper sections of the river. The
report will focus on E. coli bacteria levels, because it is
the indicator bacteria of choice by the CT DEP. Fecal coliform
bacteria levels are reported on Table B1 only as additional
data for those who may be interested.
III
Results:
NR1=Post
Road, Norwalk, SM3=James St., Norwalk, NR4=Glover Ave., Norwalk,
NR6=Wolfpit Road, Wilton, NR9=School Road, Wilton, NR13=Branchville
Station, Ridgefield/Wilton, NR15=Stonehenge Road, Ridgefield,
NR20=Fox Hill Condos, Ridgefield, NR21=Farmingville Road,
Ridgefield.
-
On 4/22 seven days after a light rainfall of 0.24 all
Norwalk River monitoring sites met the CT DEP E. coli
single sample maximum (SSM) of 410 CFU/100 mLs (Table
2b, Figure 1).
-
On 5/6 three days after a moderate rainfall of 0.37 inches,
all sites met the CT DEP E. coli SSM (Table
2a, Figure 2).
-
On 5/13, two days after a light rainfall of 0.26 inches,
all sites met the CT DEP E. coli SSM (Table
2a, Figure 2).
-
On 5/20, four days after a light rainfall of 0.28 inches,
sites NR21, NR15 and NR13 all exceeded the CT DEP E. coli
SSM (Table
2a, Figure 2).
-
On
5/27, the same day of heavy rainfall of 1.03 inches, all
sites except NR9.5 and NR9 exceeded the CT DEP E. coli
SSM (Table
2a, Figure 2). A maximum E. coli value of 2840 CFU/100mLs
was observed at Site NR1.
-
During
the period when UV lights are turned on to disinfect the
effluent discharge from the two Ridgefield and the Georgetown
waste water treatment plants (May 1 through September
30) only two Sites NR9.5 and NR9 meet the CT DEP geomean
criterion of 126 CFUmLs for a Class B river (Table
2a, Figure 3a). The percent frequency of tests (4
to date) exceeding 410 CFU/100 mLs is over 10% for all
sites except Site NR9.5 and NR9 (Table
2a).
-
During
the period when disinfection is not required by the two
Ridgefield and the Georgetown waste water treatment plants
NPDES permit (October 1, through April 30) five of the
monitoring sites exceed the CT DEP geomean criterion (Table
2b, Figure 3b). The maximum geomean is 1154 CFU/100mLs
at Site NR21 (Table
2b). In addition, all sites exceeded the 10% frequency
limit of bacteria counts in excess of 410 CFU/100mLs (Table
2b).
-
Conductivity
geomeans range from 570 uS at Site NR21 to 510
uS at Site NR15 (Figure
4). After the confluence with Cooper Brook (just above
Site NR13) conductivity geomeans are reduced to 350 uS
and stay at or below this value for the balance of the
Norwalk River (Figure 4).
-
Dissolved oxygen means and all individual samples meet the
CT DEP criterion of 5 mg/L or greater at all sites on all
sampling dates (Figure
5).
Footnote:
Water quality on 4/22 is exceptionally good at Site NR21 (Table
2b, Figure 1). According to the Ridgefield WTP Manager
the UV lights were turned on in mid-April to test the system.
The observed fecal coliform count at the WTP discharge stream
was 14 CFU/100mLs on 4/22.
IV.
Discussion:
Rainfall
for April was 6.02 inches, which is well over the monthly
average of 4.0± inches. The HW/RW sampling date of 4/22 was
preceded by only one period of precipitation of 0.24 inches
on 4/14. May followed with a total of 2.71 inches which means
a dry summer may be on the way. The first three sampling days
in May 5/6, 5/13 and 5/20 were barely influenced by rainfall
(Figure 2).
As a result, the April and May test dates (with the exception
of 5/27) show the Norwalk River watershed with little stormwater
runoff impacting the system. Water quality, for all four dates
is generally fair (Figure
1, Figure
2, Table 2a, Table 2b).
Nevertheless,
rising water temperatures observed on 5/13 (19 ºC-20 ºC) and
on 5/20 (16 ºC-18 ºC) are beginning to provide a better environment
for E. coli bacteria (Table B1). This is a possible reason
for the observed increase in all bacteria counts on 5/13 and
5/20.
Heavy
rain of 1.03 inches on 5/27 (the day of testing) provides
a view of the Norwalk River watershed under heavy stormwater
runoff conditions. Observed bacteria counts exceed the SSM
of 410 CFU/100 mLs on all sites except Sites NR9.5 and NR9.
As problem sites become evident in the warming waters of the
Norwalk River it would appear that four northern sites: NR21,
NR23, NR15 and NR13, will be on the list for more detailed
evaluation by HW/RW, as well as the four southern sites NR6,
NR4, SM3 and NR1 (Figure
2).
Conductivity
values show wide ranges mS at sites NR21, NR20and NR15 and
narrow ranges below (downstream of Site NR13). The reason
for the wider conductivity ranges in the northern end of the
watershed is not known. It would appear that water from Cooper
Brook, Bennett Brook and Comstock Brook may have a stabilizing
effect on the river, as well as helping to lower conductivity
geomeans (Figure 4).
The low value of 155 mS observed at Site NR4 on 5/6 can not
be explained (Figure 4).
Dissolved
oxygen means and all individual samples meet the CT DEP D.O.
criterion of 5 mg/L or more (Figure
5).
V.
Index of Figures, Tables and Appendices:
Table
1 CT DEP criterion for E. coli bacteria levels as applied
to recreational use, effective 12/17/02.
Table
2a May 6, 2004 to May 27, 2004 E. coli bacteria concentrations,
geometric means and % frequency exceeding 410 colonies /100
mL at 10 monitoring stations in the Norwalk River watershed
during the period of time when the two Ridgefield and one
Georgetown wastewater treatment facilities are required by
permit to disinfect sewage effluent.
Table
2b October 16, 2003 to April 22, 2004 E. coli bacteria
concentrations, geometric means and % frequency exceeding
410 colonies/100 mL at 10 sampling stations in the Norwalk
River Watershed during the period of time when the two Ridgefield
and one Georgetown wastewater treatment facilities are not
required by permit to disinfect sewage effluent.
Figure
1 E. coli bacteria concentrations and rainfall at 10 monitoring
sites in the Norwalk River Watershed on April 22, 2004.
Figure
2 E. coli bacteria concentrations and rainfall at 10 monitoring
sites in the Norwalk River Watershed during May 2004.
Figure 3a Geometric
means of E. coli bacteria concentrations at 10 monitoring
sites in the Norwalk River watershed during May 2004 (4 testing
days) when the two Ridgefield and one Georgetown wastewater
treatment facilities are required by permit to disinfect sewage
effluent.
Figure
3b Geometric means of E. coli bacteria concentrations
at 10 monitoring sites in the Norwalk River watershed from
October 16 trough April 22, 2004 (7 testing days) when the
two Ridgefield and one Georgetown wastewater treatment facilities
are not required to disinfect sewage effluent.
Figure
4 Conductivity values (µS) at 10 monitoring sites in the
Norwalk River watershed for April and May 2004.
Figure
5 Dissolved oxygen levels at 10 monitoring sites in the
Norwalk River Watershed for April and May 2004.
Appendix
A
Table
A1 Site identification, site location, GPS coordinates and
town for sampling and testing (headwaters to the mouth)
Figure
A2 Norwalk River testing sites (northern and southern watershed
maps)
Appendix
B
Table
B1 Station number (sampling site), date, time, air temperature,
water temperature, dissolved oxygen, conductivity, fecal coliform
bacteria, E. coli bacteria, rainfall, number of days prior
to sampling and QA/QC activity in March 2004.
Table
B2 Results of fecal coliform bacteria counts (colonies/100
mL) inter-laboratory services with the Norwalk Public Health
Laboratory (NPHL).
VI.
References:
Harris,
R. B. and P. J. Fraboni. Quality Assurance/Quality Control
Plan for the Norwalk River Watershed Monitoring Project (QA
No. CT00162) (re-approved October 2001 and extending to September
2002).
US
Environmental Protection Agency. 1986. Ambient Water Quality
Criteria for Bacteria, US EPA 440/5-84-002, Washington, DC.
Harris,
R. B. and P. J. Fraboni. 1999. Water Quality Data Final Report
for the Norwalk River Watershed (June 1998 -May 1999).
Harris,
R. B. and P. J. Fraboni.2000. Water Quality Data Final Report
for the Norwalk River Watershed (July 1999-September 2000).
Harris,
R. B. and P. J. Fraboni.2001. Water Quality Data Final Report
for the Norwalk River Watershed (July 2001 -September 2001).
CT
DEP, Water Quality Standard 12/17/02.
Water
Quality Data Report For The Norwalk River Watershed August
2002
Dick
Harris, Principal Investigator, Staff Scientist/Director of
the Harbor Watch/River WatchSubmitted Program - Earthplace,
Westport, CT Phone: (203) 227-7253.
Peter
Fraboni, Associate Director & QA/QC Officer for the Harbor
Watch/River Watch - Earthplace, CT, Westport Ct.
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