+ Characterization of Miller Run and Conceptual Plan for Characterization of Miller Run and Conceptual Plan for Watershed Restoration UNIV 298 Spring 2009
+ Miller Run: An Overview
+ Miller Run Statistics 80% of Miller Run is owned by Bucknell. The runoff from the new housing developments also contribute to the stream. Length of Stream: 2,000m Percent Forest: 13.1% (The Grove and the Golf Course) Percent Urban: 37.5% (Buildings and Roads) Channelized: 75-100% 50% Rip-rap Source: streamstats.usgs.gov (2009)
+ Introduction to the Presentation Characterization of Miller Run The impairment of the stream: The Channel The Water Conceptual Plan Our Proposed Solutions The Costs of Our Proposed Solutions Conclusions What Miller Run Could Be Photo Courtesy of: http://www.facstaff.bucknell.edu
+ Project Goals Flood Control Storm Water Management Retention Infiltration Aesthetic Appeal Native Species Riparian Health Recreation Improve Ecological Health Year-Round Flow Miller Run Today Sewage Recycling Habitat- Diversity Water Quality Target Species Channel Sustainability Space for Migration Structure Renewal Environmental Education Watershed Management What Miller Run Could Be Learning and Teaching Photo Taken by Dina El-Mogazi at Wellesley College
+ The Characterization of Miller Run Miller Run Put Into Perspective
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+ EEE ZZ QQ VV NN LL GG MR 1 Z S A A O M MR 2 I B
Reach 1 + Cross Section B 0 0 5 10 15 20 Vertical (m) -1 -2 -3 -4 Horizontal from left bank (m) Cross Section I 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section M 0 -0.5 0 5 10 15 20 -1 Vertical (m) -1.5 -2 -2.5 -3 -3.5 -4 Horizontal from left bank (m)
Reach 2 + Cross Section O 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section S 0 0 5 10 15 20 -1 Vertical ( m ) -2 -3 -4 Horizontal from left bank (m) Cross Section Z 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m)
Reach 3 + Cross Section AA 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section GG 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section LL 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m)
Reach 4 + Cross Section NN 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section QQ 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section VV 0 -0.5 0 5 10 15 20 -1 Vertical (m) -1.5 -2 -2.5 -3 -3.5 -4 Horizontal from left bank (m)
Reach 5 + Cross Section XX 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m) Cross Section ZZ 0 0 5 10 15 20 Vertical (m) -1 -2 -3 -4 Horizontal from left bank (m) Cross Section EEE 0 0 5 10 15 20 -1 Vertical (m) -2 -3 -4 Horizontal from left bank (m)
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+ Hydrologic Issues Portions of Miller Run frequently go dry Water quickly enters and exits the system High sediment content: hinders life, destroys restoration structures Frequent Periods of Zero Flow 0.140 0.120 Discharge (m 3 /s) 0.100 0.080 0.060 0.040 0.020 0.000 6/4/2008 0:03 6/14/2008 0:03 6/24/2008 0:03 7/4/2008 0:03 7/14/2008 0:03 7/24/2008 0:03 Time
+ Methodology Established gauges upstream and downstream to measure the height of the water Used rating curve and Manning Equation to calculate discharge (flow of water over time) 1.8 1.6 1.4 Dow nstrream 1.2 Upstream Stage (ft) 1 Upstream: y = 1.3806x 0.2115 0.8 R 2 = 0.9822 0.6 Dow nstream: y = 1.5511x 0.211 R 2 = 0.933 0.4 0.2 0 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 Discharge (m 3 /s)
DOWNSTRE AM MR2 GAUGE CAMPUS UPSTREA M MR1 GAUGE
+ Flow
Discharge (m 3 /s) 0.2 0.4 0.6 0.8 1.2 0 1 2/7/09 17:00 2/7/09 23:00 2/8/09 5:00 February Snow Melt Hydrograph 2/8/09 11:00 2/8/09 17:00 2/8/09 23:00 Time 2/9/09 5:00 2/9/09 11:00 2/9/09 17:00 2/9/09 23:00 2/10/09 5:00 Downstream Upstream 2/10/09 11:00 2/10/09 17:00 2/10/09 23:00
Discharge (m 3 /s) 0.005 0.015 0.025 0.01 0.02 0.03 0 2/18/09 0:00 Feb 18 Snowmelt and Rain Event Hydrograph 2/18/09 6:00 2/18/09 12:00 2/18/09 18:00 2/19/09 0:00 2/19/09 6:00 Time 2/19/09 12:00 2/19/09 18:00 2/20/09 0:00 2/20/09 6:00 2/20/09 12:00 Upstream 2/20/09 18:00 2/21/09 0:00
+
Storm Pipes throughout campus responsible for the double peak
Upstream Discharge Lag Time For Small Rainfall Event 0.07 0.045 0.04 0.06 0.035 0.05 Discharge (m 3 /s) 0.03 Rainfall (in.) 0.04 0.025 0.02 0.03 0.015 0.02 0.01 0.01 0.005 0 0 3/26/2009 14:00 3/26/2009 16:00 3/26/2009 18:00 3/26/2009 20:00 3/26/2009 22:00 3/27/2009 0:00 3/27/2009 2:00 Discharge Rain Time
Downstream Discharge Lag Time For Small Rainfall Event 0.07 0.045 0.04 0.06 0.035 Discharge (m 3 /s) 0.05 0.03 Rainfall (in.) 0.04 0.025 0.02 0.03 0.015 0.02 0.01 0.01 0.005 0 0 3/26/09 14:00 3/26/09 16:00 3/26/09 18:00 3/26/09 20:00 3/26/09 22:00 3/27/09 0:00 3/27/09 2:00 Discharge Rain Time
Discharge (m 3 /s) 0.05 0.15 0.25 0.1 0.2 0 1/7/2009 9:00 1/7/2009 11:00 1/7/2009 13:00 Upstream Discharge Lag Time For Large Rainfall Event 1/7/2009 15:00 1/7/2009 17:00 Time 1/7/2009 19:00 1/7/2009 21:00 1/7/2009 23:00 1/8/2009 1:00 1/8/2009 3:00 Rain Discharge 0 0.05 0.1 0.15 0.2 0.25 Rainfall (in.)
Discharge (m 3 /s) 0.05 0.15 0.25 0.1 0.2 0 1/7/09 9:00 1/7/09 11:00 1/7/09 13:00 Downstream Discharge Lag Time 1/7/09 15:00 For Large Rainfall Event 1/7/09 17:00 Time 1/7/09 19:00 1/7/09 21:00 1/7/09 23:00 1/8/09 1:00 1/8/09 3:00 Rain Discharge 0 0.05 0.1 0.15 0.2 0.25 Rainfall (in.)
Sediment
Discharge (m 3 /s) 0.2 0.4 0.6 0.8 1.2 0 1 2/6/2009 16:34 Upstream Discharge and Sediment 2/7/2009 4:34 2/7/2009 16:34 Concentration 2/8/2009 4:34 Time 2/8/2009 16:34 2/9/2009 4:34 2/9/2009 16:34 Sediment Discharge 2/10/2009 4:34 0 50 100 150 200 250 300 350 400 450 Sediment Concetration (PPM)
Discharge (m 3 /s) 0.2 0.4 0.6 0.8 1.2 0 1 2/6/09 16:00 Downstream Discharge and Sediment 2/7/09 4:00 2/7/09 16:00 Concentration 2/8/09 4:00 Time 2/8/09 16:00 2/9/09 4:00 2/9/09 16:00 Sediment Discharge 2/10/09 4:00 0 100 150 200 250 300 350 400 450 50 Sediment Concentration (PPM)
224 + Concentrations In Parts Per 18 Million 1798 117 625 521 371 270 253 606 205 2287
+ Water Quality Final Report
+ Water Chemistry Tests Used: Sondes were used to automatically record stream conditions such as temperature, pH, specific conductivity, and dissolved oxygen. Water samples were also taken manually during normal flow and high flow events, and analyzed for chemical composition. Two sites were sampled for each reading; MR-1 was upstream at the Art Barn crossing and MR-2 was downstream at Bucknell Hall.
Baseline Ion Concentrations + Upstream Site February 17, 2009 Downstream Site- February 17, 2009 Concentration Concentration Dissolved Solid (mg/L) Dissolved Solid (mg/L) Ammonium <10 Ammonium <10 Sulfate 34 Sulfate 48 Chloride 81.7 Chloride 47.9 Nitrate 1.9 Nitrate 1.98 Phosphorous <0.1 Phosphorous <0.1 Sodium 32.2 Sodium 21.9 Potassium 3.2 Potassium 2.8 Magnesium 9.7 Magnesium 9.9 Calcium 57.9 Calcium 53.5 Manganese 0.05 Manganese <0.03 Iron 0.2 Iron 0.23 Lead <0.01 Lead <0.01 Zinc <0.02 Zinc <0.02 Chromium <0.004 Chromium <0.004 Copper <0.04 Copper <0.04 Nickel <0.005 Nickel <0.005 Cadmium <0.001 Cadmium <0.001 Arsenic <0.005 Arsenic <0.005
+ Sodium, Chloride, and Potassium Fluctuations (February 7-9, 2009 Snowmelt) [Na + ] [Cl - ] Upstream (Art Barn) 100 Upstream (Art Barn) 300 Downstream (Hunt Hall) 90 Downstream (Hunt Hall) 250 80 70 [Na + ] (mg/L) [Cl - ] (mg/L) 200 60 50 150 40 100 30 20 50 10 0 0 0 5 10 15 20 25 30 35 40 45 50 0 5 10 15 20 25 30 35 40 45 50 Time (hr) Time (hr) [K + ] Negative Impacts: Surface runoff 12 and interflow carry high ion 10 Upstream (Art Barn) loads into the waterway from [K + ] (mg/L) 8 Downstream (Hunt Hall) road salts and fertilizers. 6 4 2 0 0 5 10 15 20 25 30 35 40 45 50 Time (hr)
Sulfate and Nitrate Fluctuations (February + 7-9, 2009 Snowmelt) Negative Impacts: [SO 4 2- ] 70 • Initial decrease is due 60 2- ] (mg/L) 50 to simple dilution. 40 30 Upstream (Art Barn) [SO 4 20 • Increase is due to an Downstream (Hunt Hall) 10 0 underground 0 5 10 15 20 25 30 35 40 45 50 contaminant located Time (hr) near the upstream site- probably fertilizer [NO 3 - ] accumulation or a 2.5 broken sewage line. 2.0 - ] (mg/L) 1.5 1.0 Upstream (Art Barn) [NO 3 Downstream (Hunt Hall) 0.5 0.0 0 5 10 15 20 25 30 35 40 45 50 Time (hr)
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