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CAPTURING RAINWATER TO REPLACE IRRIGATION WATER FOR
                   LANDSCAPES: RAIN HARVESTING AND RAIN GARDENS
                                   Rose Mary Seymour
_______________________________________________________________________________________
AUTHOR: Public Service Assistant, Department of Biological and Agricultural Engineering, The University of Georgia – Griffin Campus,
1109 Experiment St, Griffin, GA 30223.
REFERENCE: Proceedings of the 2005 Georgia Water Resources Conference, held April 25-27, 2005, at the University of Georgia. Kathryn
J. Hatcher, editor, Institute of Ecology, The University of Georgia, Athens, Georgia.
____________________________________________________________________________________________________________________
_____________________________________________________________________________________________________________________________________________________________________

     Abstract. Capturing rainwater and using it for                                                                       potable water supplies. However, landscape irrigation
landscape watering needs is a reasonable and realistic way                                                                does not require potable water quality. Areas of Georgia
to reduce the use of potable water for landscape irrigation.                                                              get an average of 114-165 cm (45-65 inches) of water per
This option has until recently not been given much                                                                        annum. Captured rainwater is of suitable quality to be
consideration in humid climates such as Georgia.                                                                          used for irrigation if the rainwater falls on relatively clean
However, today water conservation is a critical issue for                                                                 impermeable areas or landscaped areas.
Georgia’s growing population.                                                                                                  Water captured on site and used for landscape
     For many irrigated landscapes, harvesting of                                                                         irrigation also reduces the volume of stormwater runoff, a
rainwater is a valuable alternative. An irrigation system                                                                 valuable water quality benefit. Utilizing captured
coupled with a rain harvest system provides a source of                                                                   rainwater for irrigation results in infiltration which
irrigation water for all but the longest dry periods, and it                                                              provides a couple of benefits. Nutrients and other
reduces the amount of stormwater that moves offsite.                                                                      pollutants are removed as water moves through the soil,
Capturing stormwater during a storm and holding it on                                                                     and groundwater is recharged. The water quality and
site to be used later for irrigation has many advantages. In                                                              conservation advantages of capturing rainwater for
Georgia, enough stormwater can be captured to                                                                             landscape irrigation makes it a viable alternative
significantly reduce or eliminate the need for potable                                                                    technology that needs to be considered in better site
water use in landscapes.                                                                                                  design.
     Harvesting and storing rainwater for irrigation uses is                                                                   This paper discusses two methods of utilizing
only one method to make better utilization of rainwater                                                                   captured rainwater onsite as a substitute for irrigation in
for landscapes. Rain gardens and bioretention areas are                                                                   urban landscapes. The first method is to capture rainwater
intentional low areas where runoff water from impervious                                                                  in a cistern, tank or pond applied through watering hoses
surfaces is diverted and contained so that the runoff will                                                                or irrigation systems. The second method is the use of
infiltrate into the soil. Rain gardens are most often a                                                                   rain gardens or bioretention areas to capture rainwater
feature in a residential or small landscape. The purpose of                                                               onsite as a part of a landscape design.
a rain garden is to create a more natural flow keeping
stormwater on site to infiltrate and reducing the amount of
stormwater that runs into streets and storm drains.                                                                                     BACKGROUND AND RELATED WORK
Bioretention areas serve a similar function to rain gardens
but tend to be located in larger commercial landscaped                                                                    Rainwater Harvesting and Storage Systems
settings. They collect rainwater from roofs of commercial                                                                      An irrigation system coupled with a rain harvest
buildings and/or parking lots.                                                                                            system provides a source of irrigation water for all but the
                                                                                                                          longest dry periods, and it reduces the amount of
                                     INTRODUCTION                                                                         stormwater that moves offsite. Capturing stormwater
                                                                                                                          during a storm and holding it on site to be used later for
     In the US, outdoor water use is about 30 % on                                                                        irrigation has many advantages. In Georgia, enough
average of total residential potable water use (Vickers,                                                                  stormwater can be captured to significantly reduce or
2001). The greatest demand for outdoor water use occurs                                                                   eliminate the need for potable water use in landscapes.
during the hottest driest months of summer adding                                                                         Distributing and applying captured rainwater does not
significantly to municipal peak water use periods. In                                                                     require the kind of plumbing code restrictions that
Georgia, outdoor water use is a major component of the                                                                    graywater use does. Capturing the stormwater and
total demand for urban areas.                                                                                             applying it back to the soil is beneficial because it
     In Georgia’s efforts to develop a water plan, water for                                                              maintains the health of green spaces and the infiltrated
landscape irrigation will most likely be low in priority for                                                              irrigation water can provide recharge to groundwater.
The primary components of a rain harvesting system          required a dual distribution system which made it more
are the collection area, the transport system, filtration,       expensive than non-reuse potable water systems.
storage, delivery and distribution. The collection area can      However, the untreated stormwater reuse system was
be primarily impervious or a mix of green spaces and             comparable in cost to the treated stormwater reuse system.
impervious surfaces. Areas with bare soil should not be          The untreated stormwater reuse system was 23 % more
collection areas because of the sediment that is entrained       costly on a per dwelling unit basis than a conventional
in the runoff.                                                   non-reuse water supply system.
     Water is transported from the collection areas to                Mitchell, Mein and McMahon (1996) evaluated the
storage through a combination of pipes and open                  integrated reuse of stormwater and treated wastewater and
channels. Storage can be an open pond or a storage tank          found they could half the water supply demand with the
of some kind. Storage tanks can be buried or above               installation of an integrated reuse system. Courtney
ground and can be made from many different kinds of              (1997) modeled the operating policy of the University of
materials. The storage tank material is not critical if the      Colorado’s automatic irrigation systems and used the
water is being used for landscape irrigation. Before             simulation model to estimate the amount of stormwater
entering the irrigation system suspended materials must be       runoff that could be used for irrigation. The campus is
removed. Some settling will occur in storage, but further        about 60 % impervious. Results showed that much of the
filtration may be needed. The degree of filtration is            stormwater could be infiltrated through irrigation already
dependent on the amount of debris in the captured water          in use on the campus.
and the irrigation equipment.                                         Researchers have looked at less centralized reuse
     In some locations with enough elevation change,             systems. Hermann et al. (1996) determined that rainwater
gravity may be sufficient for delivery of water to               harvesting from residential roofs into storage tanks could
irrigation applicators, but this is typically not the case for   provide 30-50 % of the residential water demand while
pressurized irrigation systems. Low volume, low pressure         also reducing heavy metals in the stormwater not
microirrigation systems are best suited for many small           harvested by 5-25 %. Karpiscak, Foster and Schmidt
landscape water distribution systems. Microirrigation            (1990) give a detailed discussion of graywater reuse and
systems will require less storage volume for the same area       stormwater reuse for a single residence in Tucson, AZ.
than sprinkler applicators. Harvested rainwater can also be      Todd and Vittori (1997) provide several case studies on
siphoned from a tank and hand applied with hoses or              successful designs of rainwater harvesting systems.
watering cans.                                                        Heaney, Wright and Sample (2000) developed a
     If the surface the rainwater is captured from is fairly     model for an individual residential property utilizing
inert and clean, the quality of the stormwater will be           harvested rainwater for landscape irrigation.        They
suitable for irrigation without a lot of treatment to the        described a method for evaluating the efficacy of on-site
water. The water does not contain the detergents and             capture of stormwater for landscape irrigation use. They
chemicals that graywater has.                                    used this model for cities around the US including
     A rain harvesting system will add some capital and          Atlanta. Using average monthly weather data for Atlanta,
operating costs as compared to using municipal water for         for a typical 140 square meter (1500 square foot) home
irrigation, but if municipal water costs continue to rise and    with a garage on a 929 square meter (10,000 square foot)
water utilities set up conservation fee structures, the          lot, the storage tank size that would use the most
payback period for rainwater harvesting could become             stormwater for irrigation was sized at 26.5 cubic meters
minimal. Installing a rain harvest system is less expensive      (936 cubic feet). This study did not do an economic cost
if it is a part of the initial design and construction of a      benefit analysis of rainwater harvesting versus use of
building. Usually retrofit rain harvest systems are more         municipal water for irrigation.
expensive and may not fit in as well with the building
design or overall site design.                                   Rain Gardens and Bioretention Areas
                                                                      Another excellent way to use captured rain water for
Previous Research on Rainwater Harvesting                        landscape water needs is a rain garden or bioretention
    Research has investigated the reuse of stormwater at         area. Rain gardens and bioretention areas are intentional
the neighborhood or community scale and results                  low areas where runoff water from impervious surfaces is
indicated that this kind of reuse is economically feasible.      diverted and contained so that the runoff will infiltrate
Mallory and Boland (1970) used a hydrologic and                  into the soil.
economical optimization model to evaluate the cost                    Rain gardens are most often a feature in a residential
effectiveness of reuse of stormwater in communities using        or small landscape. The purpose of a rain garden is to
large detention ponds for storage. They evaluated                create a more natural flow keeping stormwater on site to
untreated stormwater and stormwater treated to be potable        infiltrate and reducing the amount of stormwater that runs
for reuse. The untreated stormwater reuse systems                into streets and storm drains. A rain garden collects
stormwater runoff and filters it through soils and plant        very helpful when they capture the runoff from these. A
roots. The plants in the rain garden are designed to be an      rain garden should be at least 3 meters (10 feet) from a
attractive landscape feature. Bioretention areas serve a        house or other building foundation. Land that has more
similar function to rain gardens but tend to be located in      than a 12 % slope will likely need additional soil brought
larger commercial landscaped settings. They collect             in and equipment to move the soil for the rain garden.
rainwater from roofs of commercial buildings and/or                  There are some other situations in which rain gardens
parking lots.                                                   are not suitable. A rain garden capturing runoff with a
     The predominate features of rain gardens are that they     high sediment load or runoff that might be contaminated
are an integral part of the landscape and water infiltrates     with hydrocarbons and other chemicals will not last for
into the soil. Water should stand in a rain garden no longer    very long before toxicity or clogging makes the rain
than 48 hours after the rain stops. Rain gardens should not     garden ineffective. For example, if a homeowner does a
increase mosquito populations because mosquitoes cannot         lot of car maintenance in a certain location on the
complete their breeding cycle in this length of time.           driveway, runoff from the driveway should not be directed
     Several states have included specifications for the        to a rain garden. The chemicals may be toxic to the plants
design of rain gardens or bioretention areas in their           as well as contaminating the soil in the rain garden.
stormwater management design manuals (Maryland
Department of the Environment, NC Department of                 Conjunctive Rain Harvesting – Rain Garden Systems
Environment and Natural Resources, Atlanta Regional                  Rain harvesting tanks combined with rain gardens or
Commission). Hunt and White (2001) provide a thorough           bioretention areas can be an even better on-site
discussion of the design process and appropriate uses of        stormwater reduction system than the use of either system
bioretention areas and rain gardens. Bannerman and              independently.       Both rainwater harvesting and rain
Considine (2003) have developed an outstanding guide for        gardens must have some overflow mechanism for larger
homeowners on do-it-yourself rain gardens. The Clean            volume storms or long-term rainfall patterns. Creating a
Water Campaign (2003) published a guide for                     rain garden downstream of a rainwater harvesting
homeowners on creating rain gardens in Georgia with             overflow can capture much of the overflow and make use
appropriate plants for Georgia’s climate.                       of that additional stormwater for infiltration. Landscape
     Because this is such a new stormwater management           and building designs can readily accommodate this
practice, the ability of various rain garden and bioretention   combination of stormwater best management practices
area designs to remove pollutants has not been verified         (BMPs) and be economical if this is a consideration in the
completely, but studies are on-going. Bioretention areas        initial design. Retrofitting a combination of the two
provide treatment by adsorbing metals and phosphorus in         BMPs at an established site may be more difficult and
organic matter, biomass and soil, by killing harmful            costly, but can still be workable.
pathogens and by reducing sediments and nitrogen as
captured stormwater infiltrates. However, too much
sediment load can create a soil crust destroying the                                CONCLUSIONS
infiltration mechanism.
     Bioretention areas often do not sufficiently remove             Both rainwater harvesting and rain gardens lead to at
nitrate-nitrogen. Hunt, Jarrett and Smith (2003) evaluated      least a partial restoration of the pre-development
a design variation on a typical bioretention area by            hydrology of an impervious urban area by increasing
creating an anaerobic zone in the soil below the surface of     infiltration of stormwater. At the same time, both of these
the bioretention area. The purpose of the anaerobic zone        BMPs replace irrigation water needs that may previously
was to provide conversion of more nitrate-nitrogen to           have been met with potable municipal water or well water.
nitrogen gas. Hunt, Jarrett and Smith (2003) did not find       These two alternatives for landscape water supply are
that the anaerobic zone had a significant effect on nitrate-    win-win strategies that can be used in both commercial
nitrogen reduction.                                             and residential site design to improve water quality and
     Rain gardens typically do well in natural depression       reduce the need for potable water use in landscape
areas of the landscape. If the area is already a natural        irrigation.
depression, runoff will tend to move towards it. However,
rain gardens are not appropriate where the seasonal high
water table is within 60 cm (24 inches) of the soil surface                      LITERATURE CITED
because the high water table will inhibit infiltration. Rain
gardens should not be placed over the top of a septic           Atlanta Regional Commission. 2001. Georgia
system. While they should not be next to building                 Stormwater Management Manual Volume 2: Technical
foundations, rain gardens next to impervious features of          Handbook.
the landscape such as driveways, patios and sidewalks are
Bannerman, R. and E. Considine. 2003. Rain Gardens A          Vickers, Amy. 2001. Handbook of Water Use and
  How-to Manual for Homeowners. http://clean-                   Conservation. WaterPlow Press. Amy Vickers &
  water.uwex.edu/pubs/raingarden/rgmanual.pdf.                  Associates, Inc.
Clean Water Campaign. 2003. Rain Gardens for Home
  Landscapes. Clean Water Campaign Brochure.
Courtney, B.A. 1997. An integrated approach to urban
  irrigation: the role of shading, scheduling, and directly
  connected imperviousness. MS Thesis. Department of
  Civil, Environmental, and Architectural Engineering.
  University of Colorado. Boulder, CO.
Heaney, J.P., L. Wright and D. Sample. 2000.
  Stormwater storage-treatment-reuse systems. In
  Innovative Urban Wet-Weather Flow Management
  Systems. Ed. By R. Field, J.P. Heaney and R.Pitt.
  Technomic Publishing Co., Inc. pp. 301-328.
Hermann, T., U. Schmida, U. Klaus and V. Huhn. 1996.
  Rainwater utilization as component of urban drainage
  schemes: hydraulic aspects and pollutant retention. In
  Proc. Of the 7th Int. Conf. Urban Stor Dranaige.
  Hannover, Germany. IAHR/IAWQ Joint Committee
  Urban Storm Drainage.
Hunt, W.F., A. R. Jarrett and J.T. Smith. 2003.
  Optimizing bio-retention design to improve
  denitrification in commercial site runoff. Unpublished
  paper found in the Stormwater Wetland and Bio-
  retention Design Workshop Manual. Workshop in
  Lenoir, NC. April 15, 2003.
Hunt, W. F. and N White. 2001. Designing Rain Gardens
  (Bioretention Areas). NC Cooperative Extension
  Bulletin No. AG-588-3. NC Cooperative Extension
  Service.
Karpiscak, M.M., K.E. Foster and N. Schmidt. 1990.
  Residential water conservation: Casa Del Agua. Water
  Resources Research. 26(6):939-948.
Mallory, C.W. and J. J. Boland. 1970. A system study of
  storm runoff problems in a mew town. Water Resources
  Bulletin. 6(6):980-989.
Maryland Department of the Environment. 1998.
  Maryland Stormwater Design Manual. Baltimore, MD.
  Maryland Department of the Environment – Water
  Management Administration.
Mitchell, V.G., R.G. Mein and T.A. McMahon. 1996.
  Evaluating the resource potential of stormwater and
  wastewater: an Australian perspective. In Proc. Of the
  7th Int. Conf. Urban Stor Dranaige. Hannover,
  Germany. IAHR/IAWQ Joint Committee Urban Storm
  Drainage.
North Carolina Department of Environment and Natural
  Resources. 1997. Stormwater Best Management
  Practices Manual. Raleigh, NC. North Carolina
  Department of Environment and Natural Resources –
  Division of Water Quality. 85 pp.
Todd, W.P. and G. Vittori. 1997. Texas Guide to
  Rainwater Harvesting. Texas Water Development
  Board. Second Edition. Austin, TX.

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Capturing Rainwater to Replace Irrigation Water

  • 1. CAPTURING RAINWATER TO REPLACE IRRIGATION WATER FOR LANDSCAPES: RAIN HARVESTING AND RAIN GARDENS Rose Mary Seymour _______________________________________________________________________________________ AUTHOR: Public Service Assistant, Department of Biological and Agricultural Engineering, The University of Georgia – Griffin Campus, 1109 Experiment St, Griffin, GA 30223. REFERENCE: Proceedings of the 2005 Georgia Water Resources Conference, held April 25-27, 2005, at the University of Georgia. Kathryn J. Hatcher, editor, Institute of Ecology, The University of Georgia, Athens, Georgia. ____________________________________________________________________________________________________________________ _____________________________________________________________________________________________________________________________________________________________________ Abstract. Capturing rainwater and using it for potable water supplies. However, landscape irrigation landscape watering needs is a reasonable and realistic way does not require potable water quality. Areas of Georgia to reduce the use of potable water for landscape irrigation. get an average of 114-165 cm (45-65 inches) of water per This option has until recently not been given much annum. Captured rainwater is of suitable quality to be consideration in humid climates such as Georgia. used for irrigation if the rainwater falls on relatively clean However, today water conservation is a critical issue for impermeable areas or landscaped areas. Georgia’s growing population. Water captured on site and used for landscape For many irrigated landscapes, harvesting of irrigation also reduces the volume of stormwater runoff, a rainwater is a valuable alternative. An irrigation system valuable water quality benefit. Utilizing captured coupled with a rain harvest system provides a source of rainwater for irrigation results in infiltration which irrigation water for all but the longest dry periods, and it provides a couple of benefits. Nutrients and other reduces the amount of stormwater that moves offsite. pollutants are removed as water moves through the soil, Capturing stormwater during a storm and holding it on and groundwater is recharged. The water quality and site to be used later for irrigation has many advantages. In conservation advantages of capturing rainwater for Georgia, enough stormwater can be captured to landscape irrigation makes it a viable alternative significantly reduce or eliminate the need for potable technology that needs to be considered in better site water use in landscapes. design. Harvesting and storing rainwater for irrigation uses is This paper discusses two methods of utilizing only one method to make better utilization of rainwater captured rainwater onsite as a substitute for irrigation in for landscapes. Rain gardens and bioretention areas are urban landscapes. The first method is to capture rainwater intentional low areas where runoff water from impervious in a cistern, tank or pond applied through watering hoses surfaces is diverted and contained so that the runoff will or irrigation systems. The second method is the use of infiltrate into the soil. Rain gardens are most often a rain gardens or bioretention areas to capture rainwater feature in a residential or small landscape. The purpose of onsite as a part of a landscape design. a rain garden is to create a more natural flow keeping stormwater on site to infiltrate and reducing the amount of stormwater that runs into streets and storm drains. BACKGROUND AND RELATED WORK Bioretention areas serve a similar function to rain gardens but tend to be located in larger commercial landscaped Rainwater Harvesting and Storage Systems settings. They collect rainwater from roofs of commercial An irrigation system coupled with a rain harvest buildings and/or parking lots. system provides a source of irrigation water for all but the longest dry periods, and it reduces the amount of INTRODUCTION stormwater that moves offsite. Capturing stormwater during a storm and holding it on site to be used later for In the US, outdoor water use is about 30 % on irrigation has many advantages. In Georgia, enough average of total residential potable water use (Vickers, stormwater can be captured to significantly reduce or 2001). The greatest demand for outdoor water use occurs eliminate the need for potable water use in landscapes. during the hottest driest months of summer adding Distributing and applying captured rainwater does not significantly to municipal peak water use periods. In require the kind of plumbing code restrictions that Georgia, outdoor water use is a major component of the graywater use does. Capturing the stormwater and total demand for urban areas. applying it back to the soil is beneficial because it In Georgia’s efforts to develop a water plan, water for maintains the health of green spaces and the infiltrated landscape irrigation will most likely be low in priority for irrigation water can provide recharge to groundwater.
  • 2. The primary components of a rain harvesting system required a dual distribution system which made it more are the collection area, the transport system, filtration, expensive than non-reuse potable water systems. storage, delivery and distribution. The collection area can However, the untreated stormwater reuse system was be primarily impervious or a mix of green spaces and comparable in cost to the treated stormwater reuse system. impervious surfaces. Areas with bare soil should not be The untreated stormwater reuse system was 23 % more collection areas because of the sediment that is entrained costly on a per dwelling unit basis than a conventional in the runoff. non-reuse water supply system. Water is transported from the collection areas to Mitchell, Mein and McMahon (1996) evaluated the storage through a combination of pipes and open integrated reuse of stormwater and treated wastewater and channels. Storage can be an open pond or a storage tank found they could half the water supply demand with the of some kind. Storage tanks can be buried or above installation of an integrated reuse system. Courtney ground and can be made from many different kinds of (1997) modeled the operating policy of the University of materials. The storage tank material is not critical if the Colorado’s automatic irrigation systems and used the water is being used for landscape irrigation. Before simulation model to estimate the amount of stormwater entering the irrigation system suspended materials must be runoff that could be used for irrigation. The campus is removed. Some settling will occur in storage, but further about 60 % impervious. Results showed that much of the filtration may be needed. The degree of filtration is stormwater could be infiltrated through irrigation already dependent on the amount of debris in the captured water in use on the campus. and the irrigation equipment. Researchers have looked at less centralized reuse In some locations with enough elevation change, systems. Hermann et al. (1996) determined that rainwater gravity may be sufficient for delivery of water to harvesting from residential roofs into storage tanks could irrigation applicators, but this is typically not the case for provide 30-50 % of the residential water demand while pressurized irrigation systems. Low volume, low pressure also reducing heavy metals in the stormwater not microirrigation systems are best suited for many small harvested by 5-25 %. Karpiscak, Foster and Schmidt landscape water distribution systems. Microirrigation (1990) give a detailed discussion of graywater reuse and systems will require less storage volume for the same area stormwater reuse for a single residence in Tucson, AZ. than sprinkler applicators. Harvested rainwater can also be Todd and Vittori (1997) provide several case studies on siphoned from a tank and hand applied with hoses or successful designs of rainwater harvesting systems. watering cans. Heaney, Wright and Sample (2000) developed a If the surface the rainwater is captured from is fairly model for an individual residential property utilizing inert and clean, the quality of the stormwater will be harvested rainwater for landscape irrigation. They suitable for irrigation without a lot of treatment to the described a method for evaluating the efficacy of on-site water. The water does not contain the detergents and capture of stormwater for landscape irrigation use. They chemicals that graywater has. used this model for cities around the US including A rain harvesting system will add some capital and Atlanta. Using average monthly weather data for Atlanta, operating costs as compared to using municipal water for for a typical 140 square meter (1500 square foot) home irrigation, but if municipal water costs continue to rise and with a garage on a 929 square meter (10,000 square foot) water utilities set up conservation fee structures, the lot, the storage tank size that would use the most payback period for rainwater harvesting could become stormwater for irrigation was sized at 26.5 cubic meters minimal. Installing a rain harvest system is less expensive (936 cubic feet). This study did not do an economic cost if it is a part of the initial design and construction of a benefit analysis of rainwater harvesting versus use of building. Usually retrofit rain harvest systems are more municipal water for irrigation. expensive and may not fit in as well with the building design or overall site design. Rain Gardens and Bioretention Areas Another excellent way to use captured rain water for Previous Research on Rainwater Harvesting landscape water needs is a rain garden or bioretention Research has investigated the reuse of stormwater at area. Rain gardens and bioretention areas are intentional the neighborhood or community scale and results low areas where runoff water from impervious surfaces is indicated that this kind of reuse is economically feasible. diverted and contained so that the runoff will infiltrate Mallory and Boland (1970) used a hydrologic and into the soil. economical optimization model to evaluate the cost Rain gardens are most often a feature in a residential effectiveness of reuse of stormwater in communities using or small landscape. The purpose of a rain garden is to large detention ponds for storage. They evaluated create a more natural flow keeping stormwater on site to untreated stormwater and stormwater treated to be potable infiltrate and reducing the amount of stormwater that runs for reuse. The untreated stormwater reuse systems into streets and storm drains. A rain garden collects
  • 3. stormwater runoff and filters it through soils and plant very helpful when they capture the runoff from these. A roots. The plants in the rain garden are designed to be an rain garden should be at least 3 meters (10 feet) from a attractive landscape feature. Bioretention areas serve a house or other building foundation. Land that has more similar function to rain gardens but tend to be located in than a 12 % slope will likely need additional soil brought larger commercial landscaped settings. They collect in and equipment to move the soil for the rain garden. rainwater from roofs of commercial buildings and/or There are some other situations in which rain gardens parking lots. are not suitable. A rain garden capturing runoff with a The predominate features of rain gardens are that they high sediment load or runoff that might be contaminated are an integral part of the landscape and water infiltrates with hydrocarbons and other chemicals will not last for into the soil. Water should stand in a rain garden no longer very long before toxicity or clogging makes the rain than 48 hours after the rain stops. Rain gardens should not garden ineffective. For example, if a homeowner does a increase mosquito populations because mosquitoes cannot lot of car maintenance in a certain location on the complete their breeding cycle in this length of time. driveway, runoff from the driveway should not be directed Several states have included specifications for the to a rain garden. The chemicals may be toxic to the plants design of rain gardens or bioretention areas in their as well as contaminating the soil in the rain garden. stormwater management design manuals (Maryland Department of the Environment, NC Department of Conjunctive Rain Harvesting – Rain Garden Systems Environment and Natural Resources, Atlanta Regional Rain harvesting tanks combined with rain gardens or Commission). Hunt and White (2001) provide a thorough bioretention areas can be an even better on-site discussion of the design process and appropriate uses of stormwater reduction system than the use of either system bioretention areas and rain gardens. Bannerman and independently. Both rainwater harvesting and rain Considine (2003) have developed an outstanding guide for gardens must have some overflow mechanism for larger homeowners on do-it-yourself rain gardens. The Clean volume storms or long-term rainfall patterns. Creating a Water Campaign (2003) published a guide for rain garden downstream of a rainwater harvesting homeowners on creating rain gardens in Georgia with overflow can capture much of the overflow and make use appropriate plants for Georgia’s climate. of that additional stormwater for infiltration. Landscape Because this is such a new stormwater management and building designs can readily accommodate this practice, the ability of various rain garden and bioretention combination of stormwater best management practices area designs to remove pollutants has not been verified (BMPs) and be economical if this is a consideration in the completely, but studies are on-going. Bioretention areas initial design. Retrofitting a combination of the two provide treatment by adsorbing metals and phosphorus in BMPs at an established site may be more difficult and organic matter, biomass and soil, by killing harmful costly, but can still be workable. pathogens and by reducing sediments and nitrogen as captured stormwater infiltrates. However, too much sediment load can create a soil crust destroying the CONCLUSIONS infiltration mechanism. Bioretention areas often do not sufficiently remove Both rainwater harvesting and rain gardens lead to at nitrate-nitrogen. Hunt, Jarrett and Smith (2003) evaluated least a partial restoration of the pre-development a design variation on a typical bioretention area by hydrology of an impervious urban area by increasing creating an anaerobic zone in the soil below the surface of infiltration of stormwater. At the same time, both of these the bioretention area. The purpose of the anaerobic zone BMPs replace irrigation water needs that may previously was to provide conversion of more nitrate-nitrogen to have been met with potable municipal water or well water. nitrogen gas. Hunt, Jarrett and Smith (2003) did not find These two alternatives for landscape water supply are that the anaerobic zone had a significant effect on nitrate- win-win strategies that can be used in both commercial nitrogen reduction. and residential site design to improve water quality and Rain gardens typically do well in natural depression reduce the need for potable water use in landscape areas of the landscape. If the area is already a natural irrigation. depression, runoff will tend to move towards it. However, rain gardens are not appropriate where the seasonal high water table is within 60 cm (24 inches) of the soil surface LITERATURE CITED because the high water table will inhibit infiltration. Rain gardens should not be placed over the top of a septic Atlanta Regional Commission. 2001. Georgia system. While they should not be next to building Stormwater Management Manual Volume 2: Technical foundations, rain gardens next to impervious features of Handbook. the landscape such as driveways, patios and sidewalks are
  • 4. Bannerman, R. and E. Considine. 2003. Rain Gardens A Vickers, Amy. 2001. Handbook of Water Use and How-to Manual for Homeowners. http://clean- Conservation. WaterPlow Press. Amy Vickers & water.uwex.edu/pubs/raingarden/rgmanual.pdf. Associates, Inc. Clean Water Campaign. 2003. Rain Gardens for Home Landscapes. Clean Water Campaign Brochure. Courtney, B.A. 1997. An integrated approach to urban irrigation: the role of shading, scheduling, and directly connected imperviousness. MS Thesis. Department of Civil, Environmental, and Architectural Engineering. University of Colorado. Boulder, CO. Heaney, J.P., L. Wright and D. Sample. 2000. Stormwater storage-treatment-reuse systems. In Innovative Urban Wet-Weather Flow Management Systems. Ed. By R. Field, J.P. Heaney and R.Pitt. Technomic Publishing Co., Inc. pp. 301-328. Hermann, T., U. Schmida, U. Klaus and V. Huhn. 1996. Rainwater utilization as component of urban drainage schemes: hydraulic aspects and pollutant retention. In Proc. Of the 7th Int. Conf. Urban Stor Dranaige. Hannover, Germany. IAHR/IAWQ Joint Committee Urban Storm Drainage. Hunt, W.F., A. R. Jarrett and J.T. Smith. 2003. Optimizing bio-retention design to improve denitrification in commercial site runoff. Unpublished paper found in the Stormwater Wetland and Bio- retention Design Workshop Manual. Workshop in Lenoir, NC. April 15, 2003. Hunt, W. F. and N White. 2001. Designing Rain Gardens (Bioretention Areas). NC Cooperative Extension Bulletin No. AG-588-3. NC Cooperative Extension Service. Karpiscak, M.M., K.E. Foster and N. Schmidt. 1990. Residential water conservation: Casa Del Agua. Water Resources Research. 26(6):939-948. Mallory, C.W. and J. J. Boland. 1970. A system study of storm runoff problems in a mew town. Water Resources Bulletin. 6(6):980-989. Maryland Department of the Environment. 1998. Maryland Stormwater Design Manual. Baltimore, MD. Maryland Department of the Environment – Water Management Administration. Mitchell, V.G., R.G. Mein and T.A. McMahon. 1996. Evaluating the resource potential of stormwater and wastewater: an Australian perspective. In Proc. Of the 7th Int. Conf. Urban Stor Dranaige. Hannover, Germany. IAHR/IAWQ Joint Committee Urban Storm Drainage. North Carolina Department of Environment and Natural Resources. 1997. Stormwater Best Management Practices Manual. Raleigh, NC. North Carolina Department of Environment and Natural Resources – Division of Water Quality. 85 pp. Todd, W.P. and G. Vittori. 1997. Texas Guide to Rainwater Harvesting. Texas Water Development Board. Second Edition. Austin, TX.