Stormwater Non-Potable Uses and Impacts on Urban Infrastructure

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COLLABORATION, INNOVATION, RESULTS. Stormwater Non-Potable Uses and Impacts on Urban Infrastructure Robert Pitt, Leila Talebi, and Ryan Bean University of Alabama, Tuscaloosa Shirley Clark Penn State Harrisburg Tuesday, December 6, 2011 www.werf.org/forum11 Long History of Stormwater Beneficial Uses (example from 7 th Century B.C., Kamiros, Rhodes) Temple and cistern at top of hill Cistern tank at temple Jug filling area next to cistern 1

Objectives Study U.S. and international practices of beneficial uses of urban stormwater runoff; Illustrate the range of technologies being used in developing and in developed countries; Identify different components of stormwater systems, treatment and recycling systems; Review possible uses of the harvested runoff for U.S. conditions. Representative Case Studies of Stormwater Beneficial Use Examined Asia (Singapore, Japan, Thailand, Indonesia, Philippines, Bangladesh, China, South Korea, and India) Africa (South Africa, Kenya, and Tanzania) Europe (Germany and Ireland) Australia (South Australia, Queensland, Victoria, and New South Wales) North America (U.S. Virgin Islands, Florida, Hawaii, Washington, New York, Maryland, California, Missouri, Oregon, Washington, D.C., and North Carolina) Rainwater jars in Thailand Park over stormwater harvesting tanks at Docklands, Melbourne Cistern at NRDC, Santa Monica office Cistern at Wash. U., St. Louis 2

Treatment Method Reuse Purpose Washington Seattle, King Street Center Sediment trap/sand filtration Chlorination Advanced Treatment UV Disinfection Irrigation Toilet flushing Fire fighting Air conditioning New York Maryland California Battery Park City; Solaire Annapolis; Philip Merrill Building Santa Monica; SMURFF Heavily Urbanized Developing Countries In Water Stressed Areas Most concerned with harvesting as much runoff as possible, with minimal concern related to water quality. Not only is roof runoff harvested, but also runoff from all urban areas, as maximum volumes are needed to augment the poor quality and poorly available local sources. The water is stored in large ponds, or injected to shallow aquifers. These improve the water quality to some extent, greatly depending on the storage conditions. 3

Developing Countries with Large Rural Populations Most of the runoff harvesting schemes focus on collecting roof runoff for storage in tanks near homes. The water is used for all domestic purposes and for irrigation of food subsistence crops during dry weather. The storage tanks are therefore relatively large to provide seasonal storage. Developed Countries with Large Urban Populations in Water Stressed Areas In most cases, the runoff is collected from roofs and stored in large tanks adjacent to buildings where the water is used for non potable uses. In some rural cases, the water is used for all domestic water uses. In large development water harvesting projects, runoff is collected from all areas and undergoes some pretreatment before storage in large (usually underground) storage tanks. The water then undergoes very sophisticated water treatment before use. In many cases, this highly treated harvested runoff is still restricted to non potable uses. 4

WHO Example Regulations for Stormwater Beneficial Uses Roof water harvesting Coliform Bacteria E. coli. <10 cfu/100 ml Chlorine >0.2 and <5 mg/l Turbidity Not relevant Surface Runoff E. coli.<10 cfu/100 ml >0.2 and <5 mg/l <15 NTU New South Wales (Australia) Nonpotable residential uses <1 cfu/100 ml 1 mg/l Cl 2 residual after 30 minutes 2 NTU Public access public uses <10 cfu/100 ml 1 mg/l Cl 2 residual after 30 minutes, 2 NTU Current Stormwater Beneficial Uses in the U.S. Many of the U.S. stormwater harvesting projects are either part of a LEED certified project, and/or to help reduce stormwater discharges to combined sewer systems. The collected water is not used for potable uses, but mostly for irrigation uses, and sometimes for toilet flushing or for fire suppression. 5

Continuous Simulations Using Long Term Rain Records to Develop Performance Curves for Roof Runoff Storage in Tanks for Later Irrigation Calculation of irrigation opportunities of landscaping around the homes using WinSLAMM. The following is a typical input screen for a water tank (this example screen is for a 35 gallon rain barrel). Comparison of East Coast vs. Central U.S. Roof Runoff Harvesting Potential for Medium Density Residential Areas (about 17% roof areas and 60% landscaping areas) Region annual rain fall (in) maximum roof runoff control (%) Central 33.5 90.6 0.72 East Coast 53.0 60.1 2.00 storage tank size for max roof runoff control (ft 3 storage/ft 2 roof area) The Central U.S. area has a higher potential level of control compared to the East Coast because the evapotranspiration (ET) demands better match the rain fall pattern. The Southwest U.S. area is challenging due to large mismatches in timing of ET/irrigation requirements and availability of rains (would need very large tanks for longterm storage). 6

Kansas City Green Infrastructure Demonstration Project: Calculations of Water Harvesting Potential of Roof Runoff ET (inches/week) 2.00 1.50 1.00 0.50 0.00 Evapotranspiration per Month (typical turf grass) Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Irrigation needs (inches/week) 2.00 1.50 1.00 0.50 0.00 Supplemental Irrigation Needs per Month (typical turf grass) Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Rainfall (inches/week) 2 1.5 1 0.5 0 Monthly Rainfall Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Irrigation needs for the landscaped areas surrounding the homes were calculated by subtracting long term monthly rainfall from the regional evapotranspiration demands for turf grass. The expected per household water use (gallons/day) from cisterns for toilet flushing and outside irrigation (ET deficit only) for the Kansas City study area (6 homes per acre) is: January 113 gal/day/house July 428 February 243 August 479 March 126 September 211 April 175 October 71 May 149 November 71 June 248 December 71 Examples of water harvesting storage tanks in New Zealand and Australia (where they are experts in modern roof runoff harvesting): Warrumbungle National Park, NSW Siding Springs National Observatory, NSW Landcare National Research Laboratory, Auckland Winery near Heathcote, Victoria 7

Reductions in Annual Flow Quantity from Directly Connected Roofs with the Use of Rain Barrels and Water Tanks (Kansas City CSO Study Area) Percentage reduction in annual roof runoff 100 90 80 70 60 50 40 30 20 10 0 0.001 0.01 0.1 1 Rain barrel/tank storage (ft 3 per ft 2 of roof area) Cistern/Storage Tank Sizing vs. Performance Storage per house (ft 3 per ft 2 of roof area) Reduction in annual roof runoff (%) Number of 35 gallon rain barrels for 945 ft 2 roof Tank height size required if 5 ft D (ft) Tank height size required if 10 ft D (ft) 0.005 24 1 0.24 0.060 0.010 29 2 0.45 0.12 0.020 39 4 0.96 0.24 0.050 56 10 2.4 0.60 0.12 74 25 6.0 1.5 0.50 99 100 24 6.0 8

Millburn, NJ Dry well disposal of stormwater for groundwater recharge in conjunction with irrigation beneficial use For the past several years, the city of Millburn has required dry wells to infiltrate increased flows from newly developed areas. There are some underground water storage tanks now being installed to use stormwater for irrigation. Project supported by the U.S. EPA is investigating performance of this shallow groundwater recharge, including groundwater contamination potential, in conjunction with irrigation beneficial uses of the stormwater. Nine dry wells are being monitored in Millburn, NJ as part of EPA project for long term hydraulic performance, and six were monitored to examine surface and subsurface water quality conditions. 160 140 10/02/2009 10/12/2009 120 Depth (cm) 100 80 60 40 07/31/2009 08/02/2009 07/29/2009 07/31/2009 08/02/2009 08/06/2009 20 0 0 500 1000 1500 2000 20 Time (hr) 9

This major home restoration project included the installation of underground water storage tanks instead of dry wells. Homes in this neighborhood have summer water bills approaching $1k/month for landscape irrigation, so the economic benefits of irrigation using stormwater are very good. Conclusions The range of approaches being used for stormwater beneficial uses is vast, ranging from: Capturing any available runoff possible to augment scarce local supplies, To conserve already abundant water supplies. The methods used for storage and treatment vary greatly, from local clay jars to vast underground reservoirs. The uses of the harvested runoff also vary from irrigation and toilet flushing only, to all domestic water uses. 10

Conclusions (cont.) The safest beneficial uses of stormwater are mainly for purposes having low potentials for human contact, such as irrigation. Treatment varies from virtually none to very sophisticated water treatment systems Beneficial uses of stormwater are not effectively regulated at this time (most reuse regulations are based on beneficial uses of treated sanitary wastewaters, for example). Given the potential for beneficial uses of stormwater in many areas of the U.S., higher priority should be given to development of specific guidelines. Acknowledgments Water Environment Research Foundation (WERF) U.S. Environmental Protection Agency (EPA), Wet Weather Flow Research Program PARS Environmental, Inc. and Mel Singer, Millburn, NJ The City of Millburn, NJ, and Kansas City, MO Department of Civil, Construction, and Environmental Engineering, University of Alabama 11