River Characterization of the Assonet River

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River Characterization of the Assonet River Bridgewater State University Virtual Commons - Bridgewater State University Watershed Access Lab Projects Watershed Access Lab 2007 River Characterization of the Assonet River Recommended Citation Apponequet Regional High School, Lakeville, Massachusetts (2007). River Characterization of the Assonet River. In Watershed Access Lab Projects. Project 58. Available at: http://vc.bridgew.edu/wal_projects/58 This item is available as part of Virtual Commons, the open-access institutional repository of Bridgewater State University, Bridgewater, Massachusetts. Assonet River Characterization Study Apponequet Regional High School A major tributary of the Taunton River in southeastern Massachusetts Located in the Taunton River Watershed (562 square miles) The eastern portion of the Assonet sub- basin: 23.60 square miles • Played a part in the American Revolutionary War •Provided the necessary power for gristmills and sawmills • Sites were downstream from the sites we examined •Assonet provided for a minor port and the last ship sailed out of the Assonet River in 1902. Cedar Swamp Let Us Introduce Our Sites… All three sites are located on the third order segment From headwaters the sites are ordered Malbone St. Beechwood St., and Locust St. Surrounded by forest and medium residential land cover Collects drainage from the Cedar Swamp Site is near and a concrete bridge on a moderately used road Stream has been channelized near bridge during its construction Mixture of forest and medium density residential cover Located near an old stone bridge under a moderately used road – Rt. 79 Sand & Gravel Company and railroad tracks upstream from collection site Surrounded mix of forest cover, medium density residential and industrial use Runs parallel to Rt. 79 which is a heavy traffic area Also near residential housing Assonet River Discharge Malbone Beechwood Locust 80 70 60 50 40 30 Discharge (ft/s)Discharge 20 10 0 9/22/06 11/02/06 4/02/07 •Normal Values: Below 26 Degrees C •All 3 Sites fell BELOW Normal Values •Effected by: Erosion, Air Temp., Etc. •Locust has MOST canopy but HIGHEST temp. Large Surface Area, and Dam •Malbone and Beechwood About the same! Temperature Vs. Time, Assonet River, All Sites, April 3-4, 2007 10 Malbone Beechw ood Locust 9 8 7 Temperature Temperature (C) 6 5 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 100000 110000 120000 130000 140000 150000 160000 170000 180000 190000 200000 210000 220000 230000 Time (HHMMSS) •Normal Range: 6.5 to 8.0 mg/L •All 3 sites: BELOW normal range on all sampling dates •In Spring: •Locust had highest pH with 5.3 mg/L •Beechwood: 4.7 mg/L •Malbone: 4.5 mg/L pH vs Time, Assonet River, All sites, Nov3-4 5.50 5.30 Malbone Beechwood 5.10 Locust 4.90 pH 4.70 4.50 4.30 4.10 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 10000 100000 110000 120000 130000 140000 150000 160000 170000 180000 190000 200000 210000 220000 230000 Time (HHMMSS) pH vs. Time, Assonet River, All Sites, April 03, 2007 5.5 5.3 5.1 Malbone Beechw ood 4.9 Locust pH 4.7 4.5 4.3 4.1 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 10000 100000 110000 120000 130000 140000 150000 160000 170000 180000 190000 200000 210000 220000 230000 (HHMMSS) •Levels Vary due to Diff. Amounts of Aeration •Aeration: Adds Oxygen to water •More TURBULENCE More DISSOLVED OXYGEN •November 2, 2006 Sampling: •Malbone: 4mg/L Drains Wetlands •Beechwood: Medium with 6 mg/L •Locust: Highest with 12 mg/L DAM Dissolved Oxygen vs. time, Assonet river, All Sites, Nov.3-4, 2006 12 10 Beechwood 8 Malbone Locust 6 4 Dissolved Oxygen (mg/L) Oxygen Dissolved 2 0 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 10000 100000 110000 120000 130000 140000 150000 160000 170000 180000 190000 200000 210000 220000 230000 Time (HHMMSS) •Normal Values: 0.1-2.0 mg/L •All Values are below BDL of 0.1 mg/L, except: •Beechwood on Sept. 2, 2006 •As rainfall INC. Concentration DEC. •Nutrients are DILUTED •Nitrogen loads at our sites fluctuate according to discharge data. •Since there is high discharge, the load is higher. •Large drop b/w Beechwood and Locust DUCKWEED Concentration of Nitrogen/Nitrate, Assonet River, All Sites 2006-07 0.25 0.2 0.15 BDL 0.1 M al bone Beechwood 0.05 Locust 0 1 2 3 Concentration(mg/L) -0.05 -0.1 9/22/06 11/2/06 4/2/07 Nitrogen/Nitrates Load, Assonet River, 2006-07 18 16 Malbone Beechwood Locust 14 12 10 8 Loadkg/day 6 4 2 0 22-Sep 2-Nov 2-Apr Dates •Limiting Factor Least Available for Plant Growth •Essential Nutrient •Normal Values- 0.01 mg/L to less than 0.05mg/L •DUCKWEED Large Difference b/w Beechwood and Locust •On Graph all Values are BDL of 0.008 except: •Beechwood in Sept. + Nov. •Locust in Nov. •Phosphorus load followed discharge graph •Duckweed was again using up nutrients b/w sites Concentration for Reactive Phosphorous, Assonet River, 2006 0.05 0.045 0.04 Malbone Beechwood 0.035 Locust 0.03 0.025 0.02 Concentration mg/L Concentration 0.015 0.01 0.005 0 1 2 3 9/22/2006 11/2/2006 4/2/2007 •Beechwood: 275 organisms •Locust: 696 organisms •Used Hilsenhoff method to determine Family Biotic Index •Hilsenhoff Max10 •LARGE # of Hydropshchidae Intolerant organisms •FBI: Beechwood 4.73 GOOD •FBI: Locust: 4.44 Good •Water Quality GOOD •Load Varied b/w sites Based on discharge •Nitrogen and Phosphorus was very good in relation to amount of water! •Amount of Macros Allowed for Maximum Survival .
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