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Lake Pocotopaug Lake and Watershed Restoration Evaluation ...

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<strong>Lake</strong> <strong>Pocotopaug</strong> water quality was sampled on ten dates starting in April 2001. Two stations(LP-1 <strong>and</strong> LP-2, Figure 6) were sampled on each visit. At each site, samples were collected atthe surface (0-0.5 m) <strong>and</strong> near the bottom with the help of a Van Dorn sampler. Samples werecollected at the thermocline depth (usually 5-6 m) during periods of stratification. Water qualityvariables measured on site included pH, conductivity, <strong>and</strong> turbidity. Additionally, temperature<strong>and</strong> dissolved oxygen (DO) profiles were determined at 1 m interval depths at each site. SDTwas also determined, <strong>and</strong> a depth-integrated (~ 6 m) water sample was collected at each sitefor chlorophyll a analysis <strong>and</strong> phytoplankton identification <strong>and</strong> quantification. Sampling namingconvention was as follows:LP-1S or LP-2S – surface water samplesLP-1M or LP-2M – mid-depth (thermocline) water samplesLP-1B or LP-2B – bottom water samplesLP-1I or LP-2I – integrated water samplesChlorophyll samples were filtered through a 0.45 µm glass fiber filter within 12 hours fromcollection <strong>and</strong> frozen until spectrophotometric determination of chlorophyll a content. Thesurface, mid- <strong>and</strong> bottom depth water samples were collected <strong>and</strong> sent to an independentanalytical laboratory for determination of total <strong>and</strong> dissolved phosphorus, <strong>and</strong> alkalinity.Dissolved <strong>and</strong> total aluminum was sampled in May. Dissolved aluminum was measured at allthree water depths <strong>and</strong> total aluminum was measured at the surface <strong>and</strong> bottom. Also inAugust, dissolved iron was measured at all three depths. Arsenic, cadmium, chromium, copper,nickel, lead, <strong>and</strong> zinc were measured in May at the surface <strong>and</strong> bottom.Tributaries <strong>and</strong> storm water pipes were sampled during four dry weather <strong>and</strong> four wet weathervisits. The first visit occurred in May 2001, when all potential stations were located, identified,<strong>and</strong> described. Actual sampling of the stations on subsequent dates was contingent uponexisting conditions (i.e., whether the station was active or not) <strong>and</strong> budgetary constraints.Location of the water quality sampling stations is provided in Figure 6.A total of 60 samples were collected from tributaries <strong>and</strong> storm drains, not including QA/QCduplicates. Descriptions of the locations, corresponding VLSG sampling identifier, <strong>and</strong> drainageareas (VLSG 1992) are provided in Table 9.Tributary stations were not sampled when flow was too low to cause any appreciablecontaminant load to the lake. Water quality variables included temperature, pH, DO,conductivity <strong>and</strong> turbidity (determined in the field by ENSR personnel), suspended solids,alkalinity, chloride, total <strong>and</strong> dissolved phosphorus, nitrate nitrogen, ammonium nitrogen, <strong>and</strong>total Kjeldahl nitrogen, <strong>and</strong> alkalinity (determined by an independent analytical laboratory).Aluminum, arsenic, cadmium, chromium, nickel, lead, <strong>and</strong> zinc were analyzed once during dry<strong>and</strong> once during wet weather.<strong>Lake</strong> <strong>Pocotopaug</strong> <strong>Restoration</strong> <strong>Evaluation</strong> 23May 2002

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