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| Bioretention practices have been shown to reduce runoff volume through both means of evapotranspiration and infiltration. The primary body of research is separated into bioretention practices either with underdrains and those without (therefore, relying solely on full infiltration into underlying soils). Volumetric performance improves when: | | Bioretention practices have been shown to reduce runoff volume through both means of evapotranspiration and infiltration. The primary body of research is separated into bioretention practices either with underdrains and those without (therefore, relying solely on full infiltration into underlying soils). Volumetric performance improves when: |
| * Native soils have high infiltration capacity and facility is designed for full infiltration, without an underdrain; | | * Native soils have high infiltration capacity and facility is designed for full infiltration, without an underdrain; |
| * Size of the impervious drainage area relative to the facility permeable footprint area (i.e., I:P area ratio) is kept within recommended range of 5:1 (HSG C and D soils) to 20:1 (HSG A and B soils); | | * Size of the impervious drainage area relative to the facility permeable footprint area (i.e., I:P area ratio) is kept within recommended range of 5:1 (HSG C and D soils) to 20:1 (HSG A and B soils). |
| * Perforated pipe or outlet connection is elevated above the bottom of the practice in the underdrain cross-section; and/or | | * Perforated pipe or outlet connection is elevated above the bottom of the practice in the underdrain cross-section; |
| * A flow restrictor (e.g., orifice, valve) is installed on the underdrain or storm sewer outlet pipe. | | * A flow restrictor (e.g., orifice, valve) is installed on the underdrain or storm sewer outlet pipe. |
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| !'''LID Practice''' | | !'''LID Practice''' |
| !'''Location''' | | !'''Location''' |
| !'''<u><span title="Note: Runoff reduction estimates are based on differences in runoff volume between the practice and a conventional impervious surface over the period of monitoring." >Runoff Reduction*</span></u>''' | | !'''<u><span title="Note: Runoff reduction estimates are based on differences in runoff volume between the practice and a conventional impervious surface over the period of monitoring." >Runoff Reduction*</span></u>''' |
| !'''Reference''' | | !'''Reference''' |
| |- | | |- |
| |rowspan="4" style="text-align: center;" | Bioretention without underdrain | | |rowspan="4" style="text-align: center;" | Bioretention without underdrain |
| | |style="text-align: center;" |China |
| | |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on SWMM and RECARGA models applied to generate the runoff reduction percentages of a bioretention installation near one of China's and expressway service area.">85 to 100%*</span></u>''' |
| | |style="text-align: center;" |Gao, ''et al.'' (2018)<ref>Gao, J., Pan, J., Hu, N. and Xie, C., 2018. Hydrologic performance of bioretention in an expressway service area. Water Science and Technology, 77(7), pp.1829-1837.</ref> |
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| |style="text-align: center;" |Connecticut | | |style="text-align: center;" |Connecticut |
| |style="text-align: center;" |99% | | |style="text-align: center;" |99% |
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| |style="text-align: center;" |Emerson and Traver (2004)<ref>Emerson, C., Traver, R. 2004. The Villanova Bio-infiltration Traffic Island: Project Overview. Proceedings of 2004 World Water and Environmental Resources Congress (EWRI/ASCE). Salt Lake City, Utah, June 22 – July 1, 2004. https://ascelibrary.org/doi/book/10.1061/9780784407370</ref> | | |style="text-align: center;" |Emerson and Traver (2004)<ref>Emerson, C., Traver, R. 2004. The Villanova Bio-infiltration Traffic Island: Project Overview. Proceedings of 2004 World Water and Environmental Resources Congress (EWRI/ASCE). Salt Lake City, Utah, June 22 – July 1, 2004. https://ascelibrary.org/doi/book/10.1061/9780784407370</ref> |
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| |style="text-align: center;" |China | | |rowspan="12" style="text-align: center;" | Bioretention with underdrain |
| |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on SWMM and RECARGA models applied to generate the runoff reduction percentages of a bioretention installation near one of China's and expressway service area.">85 to 100%*</span></u>''' | | |- |
| |style="text-align: center;" |Gao, ''et al.'' (2018)<ref>Gao, J., Pan, J., Hu, N. and Xie, C., 2018. Hydrologic performance of bioretention in an expressway service area. Water Science and Technology, 77(7), pp.1829-1837.</ref> | | |style="text-align: center;" |Ontario |
| | |style="text-align: center;" |64% |
| | |style="text-align: center;" |CVC (2020)<ref> Credit Valley Conservation. 2020. IMAX Low Impact Development Feature Performance Assessment. https://sustainabletechnologies.ca/app/uploads/2022/03/rpt_IMAXreport_f_20220222.pdf</ref> |
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| |rowspan="8" style="text-align: center;" | Bioretention with underdrain | | |style="text-align: center;" |Ontario |
| | |style="text-align: center;" |66% |
| | |style="text-align: center;" |STEP (2019)<ref> Sustainable Technologies Evaluation Program. 2019. Improving nutrient retention in bioretention. https://sustainabletechnologies.ca/app/uploads/2019/06/improving-nutrient-retention-in-bioretention-tech-brief.pdf</ref> |
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| |style="text-align: center;" |Texas | | |style="text-align: center;" |Texas |
| |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on differences in runoff volume between the practice and a conventional impervious surface over the period of monitoring.">82%*</span></u>''' | | |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on differences in runoff volume between the practice and a conventional impervious surface over the period of monitoring.">82%*</span></u>''' |
| |style="text-align: center;" |Mahmoud, ''et al.'' (2019)<ref>Mahmoud, A., Alam, T., Rahman, M.Y.A., Sanchez, A., Guerrero, J. and Jones, K.D. 2019. Evaluation of field-scale stormwater bioretention structure flow and pollutant load reductions in a semi-arid coastal climate. Ecological Engineering, 142, p.100007. https://www.sciencedirect.com/science/article/pii/S2590290319300070</ref> | | |style="text-align: center;" |Mahmoud, ''et al.'' (2019)<ref>Mahmoud, A., Alam, T., Rahman, M.Y.A., Sanchez, A., Guerrero, J. and Jones, K.D. 2019. Evaluation of field-scale stormwater bioretention structure flow and pollutant load reductions in a semi-arid coastal climate. Ecological Engineering, 142, p.100007. https://www.sciencedirect.com/science/article/pii/S2590290319300070</ref> |
| | |- |
| | |style="text-align: center;" |China |
| | |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on SWMM and RECARGA models applied to generate the runoff reduction percentages of a bioretention installation near one of China's and expressway service area.">35 to 75%*</span></u>''' |
| | |style="text-align: center;" |Gao, ''et al.'' (2018)<ref>Gao, J., Pan, J., Hu, N. and Xie, C., 2018. Hydrologic performance of bioretention in an expressway service area. Water Science and Technology, 77(7), pp.1829-1837.</ref> |
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| | |style="text-align: center;" |Ohio |
| | |style="text-align: center;" |36 to 59% |
| | |style="text-align: center;" |Winston ''et al.'' (2016)<ref>Winston, R.J., Dorsey, J.D. and Hunt, W.F. 2016. Quantifying volume reduction and peak flow mitigation for three bioretention cells in clay soils in northeast Ohio. Science of the Total Environment, 553, pp.83-95.</ref> |
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| | |style="text-align: center;" |Ontario |
| | |style="text-align: center;" |90% |
| | |style="text-align: center;" |STEP (2015)<ref> Sustainable Technologies Evaluation Program. 2015. Performance Comparison of Surface and Underground Stormwater Infiltration Practices. https://sustainabletechnologies.ca/app/uploads/2016/08/BioVSTrench_TechBrief__July2015.pdf</ref> |
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| | |style="text-align: center;" |Ontario |
| | |style="text-align: center;" |91 to 96% |
| | |style="text-align: center;" |TRCA (2014)<ref> Toronto and Region Conservation Authority. 2014. Performance Evaluation of a Bioretention System - Earth Rangers, Vaughan. Sustainable Technologies Evaluation Program. https://sustainabletechnologies.ca/app/uploads/2014/09/STEP-Bioretention-Report_2014.pdf</ref> |
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| |style="text-align: center;" |Virginia | | |style="text-align: center;" |Virginia |
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| |style="text-align: center;" |DeBusk and Wynn (2011)<ref>DeBusk, K.M. and Wynn, T.M., 2011. Storm-water bioretention for runoff quality and quantity mitigation. Journal of Environmental Engineering, 137(9), pp.800-808. https://www.webpages.uidaho.edu/ce431/Articles/DeBusk-ASCE-2011.pdf</ref> | | |style="text-align: center;" |DeBusk and Wynn (2011)<ref>DeBusk, K.M. and Wynn, T.M., 2011. Storm-water bioretention for runoff quality and quantity mitigation. Journal of Environmental Engineering, 137(9), pp.800-808. https://www.webpages.uidaho.edu/ce431/Articles/DeBusk-ASCE-2011.pdf</ref> |
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| |style="text-align: center;" |China | | |style="text-align: center;" |Maryland and North Carolina |
| |style="text-align: center;" |'''<u><span title="Note: Runoff reduction estimates are based on SWMM and RECARGA models applied to generate the runoff reduction percentages of a bioretention installation near one of China's and expressway service area.">35 to 75%*</span></u>''' | | |style="text-align: center;" |20 to 50% |
| |style="text-align: center;" |Gao, ''et al.'' (2018)<ref>Gao, J., Pan, J., Hu, N. and Xie, C., 2018. Hydrologic performance of bioretention in an expressway service area. Water Science and Technology, 77(7), pp.1829-1837.</ref> | | |style="text-align: center;" |Li ''et al.'' (2009) <ref>Li, H., Sharkey, L.J., Hunt, W.F., and Davis, A.P. 2009. Mitigation of Impervious Surface Hydrology Using Bioretention in North Carolina and Maryland. Journal of Hydrologic Engineering. Vol. 14. No. 4. pp. 407-415.</ref> |
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| |style="text-align: center;" |North Carolina | | |style="text-align: center;" |North Carolina |
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| |style="text-align: center;" |North Carolina | | |style="text-align: center;" |North Carolina |
| |style="text-align: center;" |33 to 50% | | |style="text-align: center;" |33 to 50% |
| |style="text-align: center;" |Hunt and Lord (2006). <ref>Hunt, W.F. and Lord, W.G. 2006. Bioretention Performance, Design, Construction, and Maintenance. North Carolina Cooperative Extension Service Bulletin. Urban Waterways Series. AG-588-5. North Carolina State University. Raleigh, NC.</ref> | | |style="text-align: center;" |Hunt and Lord (2006) <ref>Hunt, W.F. and Lord, W.G. 2006. Bioretention Performance, Design, Construction, and Maintenance. North Carolina Cooperative Extension Service Bulletin. Urban Waterways Series. AG-588-5. North Carolina State University. Raleigh, NC.</ref> |
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| |style="text-align: center;" |Maryland and North Carolina
| |
| |style="text-align: center;" |20 to 50%
| |
| |style="text-align: center;" |Li ''et al.'' (2009). <ref>Li, H., Sharkey, L.J., Hunt, W.F., and Davis, A.P. 2009. Mitigation of Impervious Surface Hydrology Using Bioretention in North Carolina and Maryland. Journal of Hydrologic Engineering. Vol. 14. No. 4. pp. 407-415.</ref>
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| |style="text-align: center;" |Ohio
| |
| |style="text-align: center;" |36 to 59%
| |
| |style="text-align: center;" |Winston ''et al.'' (2016). <ref>Winston, R.J., Dorsey, J.D. and Hunt, W.F. 2016. Quantifying volume reduction and peak flow mitigation for three bioretention cells in clay soils in northeast Ohio. Science of the Total Environment, 553, pp.83-95.</ref>
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| |rowspan="5" style="text-align: center;" | Bioretention with underdrain & liner | | |rowspan="5" style="text-align: center;" | Bioretention with underdrain & liner |
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| |style="text-align: center;" |15 to 34% | | |style="text-align: center;" |15 to 34% |
| |style="text-align: center;" |<span class="plainlinks">[https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf STEP (2019)]</span> <ref>STEP. 2019. Comparative Performance Assessment of Bioretention in Ontari0. Technical Brief. https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf.</ref> | | |style="text-align: center;" |<span class="plainlinks">[https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf STEP (2019)]</span> <ref>STEP. 2019. Comparative Performance Assessment of Bioretention in Ontari0. Technical Brief. https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf.</ref> |
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| |style="text-align: center;" |Maryland
| |
| |style="text-align: center;" |49 to 58%
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| |style="text-align: center;" |Davis (2008). <ref>Davis, A.P. 2008. Field performance of bioretention: Hydrology impacts. Journal of hydrologic engineering, 13(2), pp.90-95. https://ascelibrary.org/doi/abs/10.1061/(ASCE)1084-0699(2008)13:2(90)</ref>
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| |style="text-align: center;" |Queensland, Australia | | |style="text-align: center;" |Queensland, Australia |
| |style="text-align: center;" |33 to 84% | | |style="text-align: center;" |33 to 84% |
| |style="text-align: center;" |Lucke and Nichols (2015). <ref>Lucke, T., & Nichols, P. W. B. 2015. The pollution removal and stormwater reduction performance of street-side bioretention basins after ten years in operation. Science of The Total Environment, 536, 784-792. doi:http://dx.doi.org/10.1016/j.scitotenv.2015.07.142</ref> | | |style="text-align: center;" |Lucke and Nichols (2015) <ref>Lucke, T., & Nichols, P. W. B. 2015. The pollution removal and stormwater reduction performance of street-side bioretention basins after ten years in operation. Science of The Total Environment, 536, 784-792. doi:http://dx.doi.org/10.1016/j.scitotenv.2015.07.142</ref> |
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| |style="text-align: center;" |Victoria, Australia | | |style="text-align: center;" |Victoria, Australia |
| |style="text-align: center;" |15 to 83% | | |style="text-align: center;" |15 to 83% |
| |style="text-align: center;" |Hatt ''et al.'' (2009). <ref>Hatt, B. E., Fletcher, T. D., & Deletic, A. 2009. Hydrologic and pollutant removal performance of stormwater biofiltration systems at the field scale. Journal of Hydrology, 365(3), 310-321. doi:http://dx.doi.org/10.1016/j.jhydrol.2008.12.001</ref> | | |style="text-align: center;" |Hatt ''et al.'' (2009)<ref>Hatt, B. E., Fletcher, T. D., & Deletic, A. 2009. Hydrologic and pollutant removal performance of stormwater biofiltration systems at the field scale. Journal of Hydrology, 365(3), 310-321. doi:http://dx.doi.org/10.1016/j.jhydrol.2008.12.001</ref> |
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| | |style="text-align: center;" |Maryland |
| | |style="text-align: center;" |49 to 58% |
| | |style="text-align: center;" |Davis (2008)<ref>Davis, A.P. 2008. Field performance of bioretention: Hydrology impacts. Journal of hydrologic engineering, 13(2), pp.90-95. https://ascelibrary.org/doi/abs/10.1061/(ASCE)1084-0699(2008)13:2(90)</ref> |
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| | colspan="2" style="text-align: center;" |'''<u><span title="Note: This estimate is provided only for the purpose of initial screening of LID practices suitable for achieving stormwater management objectives and targets. Performance of individual facilities will vary depending on site specific contexts and facility design parameters and should be estimated as part of the design process and submitted with other documentation for review by the approval authority." >Runoff Reduction Estimate*</span></u>''' | | | colspan="2" style="text-align: center;" |'''<u><span title="Note: This estimate is provided only for the purpose of initial screening of LID practices suitable for achieving stormwater management objectives and targets. Performance of individual facilities will vary depending on site specific contexts and facility design parameters and should be estimated as part of the design process and submitted with other documentation for review by the approval authority." >Runoff Reduction Estimate*</span></u>''' |