By Zhuo Li1, Robert W. Peters1, and Matthew Winslett2 1Department of Civil, Construction, and Environmental Engineering 2Facilities Management Department University of Alabama at Birmingham Alabama Water Resources Conference 2013 Orange Beach, AL September 5-6, 2013 Overview Significance of Water Conservation at UAB Site Description Estimation of Irrigation Water Needs Design of Rainwater Harvesting System Sensitivity Analysis Results and Discussion Conclusions Significance of Water Conservation at UAB Water Consumption at UAB (Winslett, 2011): 2008-2009: 697,920 ccf (522,080,416 gallons) 2009-2010: 659,271 ccf (493,168,956 gallons) Corresponding water and sewer costs at UAB: 2008-2009: $7,025,011 2009-2010: $6,907,892 An underground storage tank (UST) was installed in 2010 at the University Boulevard Office Building (UBOB). Study Investigation Study investigation at Texas A&M University (TAMU) For purpose of controlling storm runoff volume and landscape irrigation, Saour (2009) performed a feasibility study of implementing rainwater harvesting system (RHS). Uses an equation from TAMU to estimate water supply and demand Performed payback period with two scenarios of 20 and 14 years The results showed little effect on control of stormwater runoff volume This study is similar to the project at UAB but the project at UAB is not concerned about reduction of stormwater runoff. Site Description The Campus Green is bordered by Blazer Hall, the Dining Commons, the Campus Recreation Center, and Heritage Hall. Overall, the permeable and impermeable area are approximately 52% and 48%, respectively. Source: Google Map, 2013 Estimation of Irrigation Water Needs Effective precipitation The mean value (inches) of last five-year precipitation data is used for estimation purpose: Mean Precipitation Value from Year 2008-2012 7 Precipitation, (inches) 6 5 4 3 2 1 0 Month Source: Birmingham Weather Forecast Office, 2011 Estimation of Irrigation Water Needs Effective precipitation was estimated by Natural Resource Conservation Service (NRCS) curve number method (SCS,1986) Assuming antecedent moisture condition (AMC) II. Hydrologic soil type B (SCS, 1982) It was assumed that the measured value was used to calculate the runoff without considering estimation errors. Area Land Type Square Feet Acres Street and Roads (Paved Area) 220,000±11,000 5.1±0.25 Open Space (Grass and Trees) 469,000±24,000 10.8±0.55 Roof Area 207,000±10,000 4.8±0.23 Total 896,000±45,000 20.7±1.03 Estimation of Irrigation Water Needs Evapotranspiration The Blaney-Criddle formula (Blaney and Criddle, 1950) was used, and minimum crop factor of 0.6 was selected for turf . Mean Temperature from Year 2008-2012 Temperature, (°C) 30 25 20 15 10 5 0 Month Source: Birmingham Weather Forecast Office, National Weather Service, 2011 Estimation of Irrigation Water Needs Irrigation water needs= ETcrop – Pe (Brouwer and Heibloem, 1986). A well designed and operated irrigation can have efficiency ranges from 80% to 90 % (University of California Extension System, 2000). Estimated Irrigation Water Needs, (gallons) Irrigation Water Needs, (gallons) 1,000,000 800,000 600,000 400,000 200,000 0 -200,000 -400,000 Month Note: negative value indicates no additional water needs for irrigation beside rainwater Design of RHS at UAB The UAB Campus Recreation Center pumps the groundwater in order to avoid being flooded. The quantity of pumped groundwater is approximately 1.0 million gallons per year. Assuming in each month, equal quantities of groundwater are pumped, hence 85,000 gallons per month. Design of RHS at UAB Irrigation scheme Most installers usually assume an efficiency of 75% to 90% (The Texas Manual on Rainwater Harvesting, 2005). Assuming 90% efficiency: Month Irrigation Water Need, (gallons) Collectable Rainwater, (gallons) Groundwater, (gallons) January February March April May June July August September October November December 30,000 173046 30,000 439,619 93,172 819,852 296,129 594,586 30,000 598,105 233,124 30,000 569,382 496,473 706,713 488,373 889,563 396,947 531,192 662,736 444,396 521,548 487,601 535,050 85,000 85,000 85,000 85,000 85,000 85,000 85,000 85,000 85,000 85,000 85,000 85,000 Total 3,367,633 6,729,974 1,020,000 Design of RHS at UAB Tank size determination Refers to UST at UBOB and situation in this project, the tank size was determined to be 60,000 gallons, which are two 30,000 gallon tanks. Commercial water costs $3.21/CCF (Birmingham Water Works Board, 2013). Total water cost saving ~$ 13,284 Draco, Inc. Underground Water Tanks with Purpose of Landscape Irrigation Size of Tanks (gal) Diameters of Tank (ft) Price of polyethylene Tank, ($) 10,000 10 15,750 20,000 10 26,537 30,000 12 37,908 40,000 12 53,005 50,000 12 62,080 Source: www.darcoinc.com/ (Darco Inc., 2013) Tank Size Determination (Cont’d) Accessories and other cost 30000 gallon polyethylene tanks 2 HP Pump 60 GPM Filter Misc. such as landscaping, locating drains, connecting sprinklers, etc. Dig tank hole and backfill Concrete tank support Gravel around tank Piping to tank Electrical/controls Subtotal Costs Overhead 10% Engineering 15% Contingency 15% Total Source: UAB Facilities Management Department, 2012 Cost, ($) 37,908 585 70 8,500 8,000 4,000 25,000 12,000 10,000 106,063 10,606 15,909 15,909 148,488 Tank Size Determination (Cont’d) If use one 60,000 gallon tank: UST Cost The payback period = Water charge per year = $148,488+$ 37,908 $12,715 = 14.6 years Double costs if use two 30,000 gallon tanks If only use a 30,000 gallon tank : UST Cost The payback period = Water charge per year = $148,488 $ 12,458 = 11.9 years $163,584 $ 12,544 = 13 years If only use a 40,000 gallon tank: UST Cost The payback period = Water charge per year = The optimize tank size can be 30,000 gallons. The UAB Facilities Management Department performed a preliminary study that suggests using a 30,000 gallon tank. Smaller tank can make a little better payback but less of capacity for efficient irrigation which is not preferable. Design of RHS at UAB Sensitivity Analysis A sensitivity analysis was performed in order to explore the impact on tank size, payback period. The study investigated changes of±5%,±10% and ± 25% If the water supply can fully meet the demand, the tank size will be reduced. Otherwise, it will remain the same. Three scenarios were studied: Change of precipitation Change of ET ET and precipitation increase or decrease at same time Results and Discussion Sensitivity analysis shows no impact on tank size and overall payback period. With a decrease in precipitation or an increase in evapotranspiration, the payback period will be shorter. Overall, the designed rainwater harvesting can meet approximately 86% of the total irrigation water requirement. The ongoing research project on recovery of condensed water at UAB indicates good water quality that can be supplemented for irrigation. To reduce the payback period, concrete water storage tanks or other cheap material-made tanks can be alternatives to decrease the capital investment. The UST has a potential problem (algae formation) that can be controlled by disinfection and maintenance but leads to higher cost. Conclusion The study provides a general estimation involving a feasibility study of implementing a RHS at the UAB Campus Green. The estimation may be not highly accurate in some details but generally it is reasonable providing results similar to the study at TAMU and UAB Facilities Management Department. Based on the financial aspect, the payback period is a little long, ~12 years, indicating that rainwater harvesting is not economically viable for large scale implementation for irrigation purposes. However, in an effort to make the campus “greener”, the RHS may be a viable approach. Acknowledgements Sincere gratitude to Dr. Robert W. Peters for his valuable time. Thanks offered to Mr. Matt Winslett for his strong support by providing data need for this investigation. Thanks and appreciation to the Facilities Management Department of UAB funding this study. Thank you for your time. Questions? Mean Daily Percentage (p) of Annual Daytime Hours for Different Latitudes The latitude of Birmingham is 33°31' 14" N, rounded to 33°. Latitude South North Jul Jan Aug Feb Sep Mar Oct Apr Nov May Dec Jun Jan Jul Feb Aug Mar Sep Apr Oct May Nov Jun Dec 60 55 50 45 40 35 30 25 20 15 10 5 0 0.15 0.2 0.26 0.32 0.38 0.41 0.4 0.34 0.28 0.22 0.17 0.13 0.17 0.21 0.26 0.32 0.36 0.39 0.38 0.33 0.28 0.23 0.18 0.16 0.19 0.23 0.27 0.31 0.34 0.36 0.35 0.32 0.28 0.24 0.2 0.18 0.2 0.23 0.27 0.3 0.34 0.35 0.34 0.32 0.28 0.24 0.21 0.2 0.22 0.24 0.27 0.3 0.32 0.34 0.33 0.31 0.28 0.25 0.22 0.21 0.23 0.25 0.27 0.29 0.31 0.32 0.32 0.3 0.28 0.25 0.23 0.22 0.24 0.25 0.27 0.29 0.31 0.32 0.31 0.3 0.28 0.26 0.24 0.23 0.24 0.26 0.27 0.29 0.3 0.31 0.31 0.29 0.28 0.26 0.25 0.24 0.25 0.26 0.27 0.28 0.29 0.3 0.3 0.29 0.28 0.26 0.25 0.25 0.26 0.26 0.27 0.28 0.29 0.29 0.29 0.28 0.28 0.27 0.26 0.25 0.26 0.27 0.27 0.28 0.28 0.29 0.29 0.28 0.28 0.27 0.26 0.26 0.27 0.27 0.27 0.28 0.28 0.28 0.28 0.28 0.28 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 0.27 Adapted from: Brouwer and Heibloem, 1986 Warm Season Turf The grass type is warm season turf, which is suitable for growing during the warm climate season. A minimum proper crop factor of 0.6 was selected for calculation in order to conserve water. Source: The University of Arizona Cooperative Extension, 2000 Source:SCS, 1986 Land Use Area, acres CN Product, Area×CN Street and Roads (paved Area) Open Space (grass and trees) Total 5.1 98 494.9 10.8 61 657.2 15.9 1152.1 Steps of Calculating Effective Runoff Thus, the composite CN was computed as: 𝐶𝑁 = 1152.1 ÷ 15.9 = 72.5 The maximum possible retention for this area at AMC-II is: 𝑆 = 1000 ÷ 72.5 − 10 = 3.79 𝑖𝑛𝑐ℎ𝑒𝑠 The initial abstractions were estimated to be: 𝐼𝑎 = 0.2𝑆 = 0.2 × 3.8𝑖𝑛𝑐ℎ𝑒𝑠 = 0.76 𝑖𝑛𝑐ℎ𝑒𝑠 Because P>𝐼𝑎 , the depth of runoff (effective precipitation) was estimated as: 4.92 − 0.2 3.8 2 𝑃𝑒 = = 2.14 𝑖𝑛𝑐ℎ𝑒𝑠 4.92 + 0.8 3.8