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Modeling the effects of precipitation events on nutrient loading in Munroe Brook, Shelburne, VT VT EPSCoR Streams Project April 2009 Nichole Bushey & Meredith Simard Modeling vs. Monitoring • Crucial to address issues of water quality from a watershed perspective • Monitoring ▫ Provides information about the current state of the watershed ▫ Costly and time-consuming • Modeling ▫ Predicts changes resulting from future conditions ▫ Tests future alternative scenarios Watershed Details • Drains into Shelburne Bay • Watershed area: 1435.46 ha (3547.01 acres) • 85 ha high density urban • 121ha low density urban • 281 ha agriculture • Total stream length: 28.6 km (17.8 miles) Sampling Details • 12 sample sites named by tributary • T1 • T2 • M • Focus at M1 AVGWLF & PRedICT • ArcView Generalized Watershed Loading Function ▫ Monthly outputs of sediment and nutrient loads based on daily discharge ▫ Advantages: “Mid-Level” model Ease of use Less complex input datasets • Pollution Reduction Impact Comparison Tool ▫ Evaluates implementation of urban and rural pollution reduction strategies at watershed level Modeling Process • Locate and create input data • Simulate discharge and nutrient loads and compare with sample data from 2006 and 2007 sampling seasons ▫ Calibration • Scenarios ▫ Current status ▫ Future precipitation and temperature associated with climate change ▫ Future land management Calibrating the Model: Discharge Discharge (cms) Average Daily Discharge per Month 2006 0.6 Stream Gauge 0.4 Original Model Output 0.2 Calibrated Model Output 0 1 2 3 4 5 6 Month (June- Novem ber) Discharge (cms) Changed 630 ha of Row Crops to Golf Course to better match watershed landuse. Average Daily Discharge per Month 2007 0.6 Stream Guage 0.4 Original Model Output 0.2 Calibrated Model Output 0 1 2 3 4 Month (June- Novem ber) 5 6 Calibrating the Model: Nutrients 2007 Total Nitrogen: Modeled v. Actual Data TN Load (g/sec) 1 0.8 Actual Data 0.6 Original Model Output 0.4 Calibrated Model Output 0.2 0 1 2 3 4 5 Month (June-November) 2007 Total Phosphorus: Modeled vs. Actual Data TP Load (g/sec) 0.025 0.02 Actual Data 0.015 Original Model Output 0.01 Calibrated Model Output 0.005 0 1 2 3 4 Month (June-November) 5 6 6 Climate Change Scenarios: Parameters • Lower Emissions Scenario for 2069 ▫ Average annual temperature increase of 3.7°F ▫ 11% increase in winter precipitation • Higher Emissions Scenario for 2069 ▫ Average annual temperature increase of 5.8°F ▫ 16% increase in winter precipitation • Increase in frequency of droughts • Increase in likelihood and severity of heavy rainfall events • Increase in winter precipitation falling as rain and 25-50% decrease in snowfall by the end of the century • Increasing period of low streamflow due to higher temperature and increased evapotranspiration. Climate Change Scenarios: Hydrological Results Evapotranspiration predictions for 2069 12 ET (cm) 10 8 Current emissions 6 Low emissions 4 High emission 2 0 1 2 3 4 5 6 7 8 9 10 11 12 Month (January-December) Effects of climate change on discharge Discharge (cms) 0.7 0.6 0.5 Current emissions 0.4 Low emissions 0.3 High emissions 0.2 0.1 0 1 2 3 4 5 6 7 8 9 10 Month (January-December) 11 12 Total Phosphorus (g/sec) Climate Change Scenario: Nutrient Results Total Phosphorus Loading 0.09 0.08 0.07 0.06 0.05 0.04 0.03 0.02 0.01 0 Low Emission Scenario High Emission Scenario Current Emissions 1 2 3 4 5 6 7 8 9 10 11 12 Month (January - December) Total Nitrogen Loading Total Nitrogen (g/sec) 1 0.8 Low Emission Scenario 0.6 High Emission Scenario 0.4 Current Emissions 0.2 0 1 2 3 4 5 6 7 8 9 10 11 12 Month (January-December) Watershed Improvements Stream Bank Fencing Vegetated Buffers Rain Garden Vegetated Buffers 940m of stream length 1190m of stream length Rain Garden Installation 0.6 ha of rain gardens will drain just over 5 ha of impervious surface Stream Bank Fencing • Cows negatively impact: • water quality • streambank stability • Goal: Protect 300m of stream bank from livestock Improving our Study • Improve accuracy of landuse layer • Additional Input data ▫ Septic systems • Compare tributaries to whole watershed • Alternative and more comprehensive scenarios ▫ Climate change predictions based on multi-year averages ▫ Urban watershed management practices ▫ Further utilization of PRedICT software Acknowledgements • • • • Maeve McBride KathiJo Jankowski Meredith Curling (UVM) Bill Hoadley (LaPlatte Watershed Partnership)