Difference between revisions of "Water quality"
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===STEP stormwater practice effluent quality monitoring results=== | ===STEP stormwater practice effluent quality monitoring results=== | ||
The whisker plot figures show effluent stormwater effluent quality monitoring results from STEP monitoring projects over a 25-year period (1997 - 2021) for sites within Greater Toronto Area regions and municipalities. Median concentrations of Total Suspended Solids (TSS) in untreated stormwater and oil and grit separator (OGS) outlet locations were found to typically exceed 30 mg/L. Median TSS concentrations at stormwater detention pond and chamber system outlet locations was found to be below 30 mg/L, but exceeded the guideline value in 36% of the monitored storm events. Median TSS concentrations at bioretention, permeable pavement and infiltration trench outlet locations were all below 30 mg/L. TSS concentration in effluent from bioretention was found to exceed 30 mg/L in only 15% of the monitored storm events, and in only 12% of monitored events for permeable pavements. | The whisker plot figures to the right show effluent stormwater effluent quality monitoring results from STEP monitoring projects over a 25-year period (1997 - 2021) for sites within Greater Toronto Area regions and municipalities. Median concentrations of Total Suspended Solids (TSS) in untreated stormwater and oil and grit separator (OGS) outlet locations were found to typically exceed 30 mg/L. Median TSS concentrations at stormwater detention pond and chamber system outlet locations was found to be below 30 mg/L, but exceeded the guideline value in 36% of the monitored storm events. Median TSS concentrations at bioretention, permeable pavement and infiltration trench outlet locations were all below 30 mg/L. TSS concentration in effluent from bioretention was found to exceed 30 mg/L in only 15% of the monitored storm events, and in only 12% of monitored events for permeable pavements. | ||
Click on the links below for LID BMP-specific pages and figures. | Click on the links below for LID BMP-specific pages and figures. |
Revision as of 17:53, 20 March 2023
Overview[edit]
Improvements in the quality of stormwater runoff is one of the primary benefits of low impact development strategies. Although some chemical changes occur inside the practices, much of the pollution reduction of low impact development strategies comes from runoff reduction. i.e. diverting excess water through infiltration or evapotranspiration.
Nutrients[edit]
Plants (including algae) require three macro nutrients to grow: Nitrogen, potassium, and phosphorus. Of these three, phosphorus is the often the "growth-limiting" nutrient. i.e. the local environment may have an abundance of nitrogen and potassium, but algae won't develop unless phosphorus is available too. See Phosphorus page for more on phosphorus. See Additives page for guidance on filter media additives to enhance retention of phosphorus and other types of pollutants in Bioretention, Bioswale, Stormwater Planter and Stormwater Tree Trench facilities.
STEP stormwater practice effluent quality monitoring results[edit]
The whisker plot figures to the right show effluent stormwater effluent quality monitoring results from STEP monitoring projects over a 25-year period (1997 - 2021) for sites within Greater Toronto Area regions and municipalities. Median concentrations of Total Suspended Solids (TSS) in untreated stormwater and oil and grit separator (OGS) outlet locations were found to typically exceed 30 mg/L. Median TSS concentrations at stormwater detention pond and chamber system outlet locations was found to be below 30 mg/L, but exceeded the guideline value in 36% of the monitored storm events. Median TSS concentrations at bioretention, permeable pavement and infiltration trench outlet locations were all below 30 mg/L. TSS concentration in effluent from bioretention was found to exceed 30 mg/L in only 15% of the monitored storm events, and in only 12% of monitored events for permeable pavements.
Click on the links below for LID BMP-specific pages and figures.
- Bioretention: Performance
- OGS: Performance
- Permeable pavements: Performance
- Infiltration Trench: Performance
- Rainwater Harvesting: Performance
- Green Roof: Performance
Note: The water quality performance data was collected by the Sustainable Technologies Evaluation Program (STEP). Disclaimer: STEP cannot guarantee the validity of the information found here. While we use reasonable efforts to include accurate and up to date information, we make no guarantees as to the accuracy of the content and assume no liability for an error or omission in the content).
Heavy metals[edit]
The heavy metals noted as particularly harmful to aquatic ecosystems are:
- Chromium(Cr),
- Copper (Cu),
- Lead (Pb), and
- Zinc (Zn)[3]
Laboratory experiments on bioretention media have demonstrated that the organic matter significantly improves retention of lead (Pb), copper (Cu), and zinc (Zn) [4]. This research also found that extended detention of the stormwater in the cell did not improve this water quality benefit.
Cores of media were extracted from five 10 year old bioretention cells in Queensland, Auz and tested for a suite of heavy metals: “Although trace amounts of several heavy metals (most prominently Mn and Zn) were found in most of the basins, all heavy metal levels found in the soil were either below detectable limits, or within acceptable limits based on legislated health-based investigation levels.”[5]
External Links[edit]
- Environment Canada on Phosphorus and Excess Algal Growth
- Lake Simcoe phosphorus reduction strategy
- Canadian LID BMP Database
References[edit]
- ↑ Canadian Council of Ministers of the Environment. 2002. Canadian water quality guidelines for the protection of aquatic life: Total particulate matter. In: Canadian environmental quality guidelines, 1999, Canadian Council of Ministers of the Environment, Winnipeg. https://ccme.ca/en/res/total-particulate-matter-en-canadian-water-quality-guidelines-for-the-protection-of-aquatic-life.pdf
- ↑ Ministry of the Environment and Energy. 1994. WATER MANAGEMENT POLICIES GUIDELINES - PROVINCIAL WATER QUALITY OBJECTIVES OF THE MINISTRY OF ENVIRONMENT AND ENERGY. July, 1994. Reprinted February 1999. ISBN 0-7778-8473-9 rev. https://dr6j45jk9xcmk.cloudfront.net/documents/3016/moeprovincialwaterqualityobjectivesen.pdf
- ↑ Feng W, Hatt BE, McCarthy DT, Fletcher TD, Deletic A. Biofilters for Stormwater Harvesting: Understanding the Treatment Performance of Key Metals That Pose a Risk for Water Use. Environ Sci Technol. 2012;46(9):5100-5108. doi:10.1021/es203396f.
- ↑ Gülbaz S, Kazezyilmaz-Alhan CM, Copty NK. Evaluation of Heavy Metal Removal Capacity of Bioretention Systems. Water Air Soil Pollut. 2015;226(11). doi:10.1007/s11270-015-2640-y.
- ↑ Lucke T, Nichols PWB. The pollution removal and stormwater reduction performance of street-side bioretention basins after ten years in operation. Sci Total Environ. 2015;536:784-792. doi:10.1016/j.scitotenv.2015.07.142.