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New Haven River Watch was formed in 1993 under the
auspices of The New Haven River Anglers Association in collaboration with
Otter Creek River Watch. The New Haven River is 58 miles long and has a
drainage basin of 113 miles. The upper parts of the river consist of
deciduous growth and the lower part of the river flows through residential
areas and farmland. The streambed characteristics of the upper part of the
river consist of broken dolomitic limestone and gravelly rubble while the
lower part is mainly of sandy-clay consistency. The tributaries are, Muddy
Branch, Notch Brook, Baldwin Brook, Beaver Brook, Beaver Meadow Brook,
Dowingville Brook, Cobb Hill Brook, Lincoln Gap Brook and Pecott Brook.
The ph readings on the river range from 6.0 and 7.7. All parameters taken
indicate a clean, clear, well-oxygenated and well-buffered system. The
dissolved oxygen ranges from 9.3 to10.3 mg/l parts per million. The total
phosphorus, a primary algal nutrient is relatively low as well as the
turbidity and conductivity. It is the mission of NHRW to accumulate base
line data that may help identify any trends occurring on the river.
Historically NHRW has tested 11 sites on either four or five occasions
during the summer months. These sites chosen were determined to be popular
areas for swimming since most sites were very accessible from the road.
The site numbers are determined by the length in miles from the confluence
of the New Haven River at Otter Creek just below River Bend Campgrounds.
The collection and accumulation of data is the simplest part of a complex
process involving detail lab work and protocols. The data gathered from
year to year is only but a snapshot of the river morphology. Valuable
field records along with GIS flow charts help to give an insight on how
this data is interpreted. In the summer of 2000 a total of forty water
samples were gathered on four test dates at eleven sites on the river. The
upper stretches of the New Haven River above site 15.5 sustained extensive
damage as a result of the 1998 flood. The bridge below this site remained
under repair for the summer and was not passable by motor vehicle.
Consequently volunteers were able to accumulate one water sample at the
first site before the bridge repair was undertaken. A total of 24 out of
40 sites (60%) sampled for ecoli bacteria were in violation of the
acceptable state standards of 77 colonies/100ml. In 1998 (in 99 testing
did not occur) 67% of the sites were in violation due to higher than usual
water flows. In 2000 this may also be evident for the test dates of 6/28 &
8/12 where higher than normal flows (96 & 199cfs) for those dates resulted
in a total of 18 of 21 violations of state standards. Because of the
dynamics of rivers, high water flows are generally linked to higher ecoli
counts and phosphorous levels do to non point source run off. Conversely
extreme low water flows (1995 drought) resulted in some of the highest
counts of ecoli bacteria on the New Haven since the River Watch program
started. This may be in part due low water flows and a high dilution rate.
Unfortunately due to poor protocol testing procedures in 1999, New Haven
River Watch was not able to accumulate verifiable ecoli data in the
drought year of 1999) for interesting comparisons to the test results for
the year of 1995.
River Watch Network studies indicate that when total phosphorus levels
exceed .05 milligrams per milliliter in the water column impacts are
likely and when they do exceed a level of .1 milligrams per milliliter
impacts are certain. Phosphorous is essential for the growth of organisms
and the discharge of high quantities of phosphorous may lead to excessive
photosynthetic organisms. Algae blooms may effect water quality in rivers
resulting in extreme situations the possibility of eutrophication. In 2000
no recorded levels of phosphorous exceeded .04milligrams per milliliter on
the New Haven River. All phosphorous data recorded was well within
acceptable limits that would not impact the river.
New Haven River Watch will continue to closely monitor ecoli bacteria
test results and trends. These trends are very difficult to extrapolate
since from year to year weather conditions and uses along the New Haven
River change in varying degrees. One trend has emerged since the
collection of the data in 1993. Higher readings for ecoli bacteria are
generally located in the lower stretches of the New Haven River starting
at the Munger Street bridge site (5.0) and continuing with sites 2.0, .5,
& 0.0 which is near at the confluence of the New Haven River and Otter
Creek. The geo mean from these test sights corroborates this trend. High
ecoli counts from these four sites in part may be attributed to
agricultural run off from non point sources. Geo mean results from sites
10.5 and 15.0 with 25 samplings and geo mean readings of 137 and139 colony
counts of ecoli merit a closer examination of the data in the future.
In 2001, The New Haven River Watch group will continue to monitor 11
test sites on 4-5 test dates during the summer months. Bimonthly reports
at the Bristol town offices will be forthcoming. The town of Bristol and
the community has embraced the mission of the New Haven River Watch group.
It is paramount that a positive relationship and a mission of longevity
continue. The New Haven River Watch is a proactive organization and not a
reactive one. Citizens are encouraged to talk with their state district
environmental enforcement officer if they have any serious concerns with
health and safety issues regarding their recreational use of the river.
Ultimately it is the State of Vermont's responsibility to protect the
public in cases of egregious harm. This was evident in the summer of 2000
on the White River and the town of Bethel's failed sewage treatment
facility. In the future, the surrounding towns of the New Haven River
watershed should consider assisting The New Haven River Watch and the
Addison County River Watch Collaborative financially with small annual
monetary considerations, possibly incorporated from the annual general
fund budget. The valuable information of collecting data and publishing
reports has been used in varying capacities from formatting town plans to
measuring impacts of development near river ecosystems. River Watch
organizations are consistently challenged with limited financial budgets
would endure with more secure financial stability.
Peter Diminico coordinator for New Haven River Watch |