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10/13/2011 ENVIRONMENTAL OVERSIGHT COMMITTEE Minutes
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10/13/2011 ENVIRONMENTAL OVERSIGHT COMMITTEE Minutes
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Mashpee_Meeting Documents
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ENVIRONMENTAL OVERSIGHT COMMITTEE
Meeting Document Type
Minutes
Meeting Date
10/13/2011
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Johns Pond Dissolved Oxygenm Temperature( g/1) or Tem P (C) <br /> Mashpee 0 5 10 15 20 25 <br /> MA-818 <br /> 2 <br /> Acreage: 337.7 4 — <br /> Maximum Depth: 62 ft 6 <br /> 2001 Secchi Dip: 12.7 ft 8 <br /> 10 <br /> Lake Association:None 12 <br /> 14 ♦—Temperature <br /> OVERVIEW 16 - — DO <br /> 8 ' <br /> Johns Pond is located in -` <br /> ., T. . <br /> western Mashpee just southeast <br /> ofAshumet Pond and the Mas- Dissolved Oxygen and Temperature <br /> sachusetts Military Reservation Johns Pond,2001 <br /> (MMR). Apublic paved boat ramp with an accompanying small parking lot is located on the northwest <br /> corner of the pond off of Hooppole Road. The pond drains into the Childs and Quashnet Rivers. Fish- <br /> eries surveys conducted during 1991 and 1992 recorded 11 species present and the pond is stocked <br /> annually in the spring and fall with brook and rainbow trout. <br /> WATER QUALITY <br /> Johns Pond was sampled in 1948, 1980, 1993, 1994, 1998,2001, and 2002. The 7/23/48 temperature <br /> profile showed stratification around 35 ft,with depressed dissolved oxygen(DO)concentrations below_50 ft <br /> and a minimum DO concentration of 6.4 ppm. hi 8/13/80 and the summer of 1994,temperature stratifica- <br /> tion occurred around 30 ft and DO concentrations'less than 1 ppm (i.e., anoxic conditions) were measured <br /> below 36 ft. The 2001 PALS readings are consistent with the 1980 and 1994 samplings, but DO and <br /> temperature concentrations were not measured below 10 in(33 ft). Surface TP concentrations from the 2001 <br /> PALS snapshot(see below)are below the current Cape Cod"impacted" threshold,while the chlorophyll a <br /> and TN concentrations exceed their thresholds. A Carlson TSI based on a surface chlorophyll a concentra- <br /> tion places the pond in the middle of the mesotrophic category. <br /> Although the surface concentrations do not indicated impacts,it is clear from a comparison of historic <br /> and recent DO profiles that deep water quality has become impaired over the last 50 years. The rise in TN, <br /> TP, and alkalinity concentrations observed in the deep samples (see below)are consistent with anoxic con- <br /> ditions allowing sediment -bound nutrients to be released into overlying waters. Monitoring from MMR <br /> studies(HAZWRAP, 1994)suggests that anoxic conditions develop early in the summer,but additional DO <br /> monitoring on a biweekly schedule during the surnmer or two is recommended to resolve how persistent the <br /> anoxia is. It is also recommended that annual monitoring of the pond continue, and that more refined <br /> monitoring and a characterization of nutrient loads to and within the lake be considered in the future. Johns <br /> Pond presents as an impacted lake with existing water quality problems. <br /> 2001 PALS Snapshot Results <br /> Depth pH Chlorophyll a Alkalinity Total Phosphorus Total Nitrogen _ <br /> meters µg/L as m CaCO3/L µ mg/L <br /> 0.5 6.8 3.67 8.0 4.0 0.32 <br /> 3 6.75 3.20 8.0 4.0 0.36 <br /> 91 6.431 6.65 1 8.11 7.4 0.32 <br /> _181 6.441 3.851 26.71 26.9 1.20 <br />
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