Volume 2-05, Chapter 3 - City of Wichita
Volume 2-05, Chapter 3 - City of Wichita Volume 2-05, Chapter 3 - City of Wichita
Section 3.3.3 - Alum Treatment 3.3.3.1 General Description The process of alum (aluminum sulfate) treatment provides treatment of stormwater runoff from a piped stormwater drainage system entering a wet pond or basin by injecting liquid alum into storm sewer lines on a flow-weighted basis during rain events. When added to runoff, liquid alum forms nontoxic precipitates of aluminum hydroxide [Al(OH) 3 ] and aluminum phosphate [AlPO 4 ]. However, alum will lower the pH of receiving waters and must be closely monitored to avoid adverse impacts on aquatic life. The alum precipitate or “floc” formed during coagulation of stormwater combines with phosphorus, suspended solids, and heavy metals and removes them from the water column. Once settled, the floc is stable in sediments and will not re-dissolve due to changes in redox potential or pH under conditions normally found in surface water bodies. Laboratory or field testing may be necessary to verify feasibility and to establish design, maintenance, and operational parameters, such as the optimum coagulant dose required to achieve the desired water quality goals, chemical pumping rates, and pump sizes. The capital construction costs of alum stormwater treatment systems is less independent of watershed size and more dependent on the number of outfall locations treated. Estimated annual operations and maintenance (O&M) costs include chemical, power, manpower for routine inspections, equipment renewal, and replacement costs. Ferric chloride has also been used for flow-proportional injection for removing phosphorus and other pollutants. Although ferric chloride is less toxic to aquatic life than alum, it has a number of significant disadvantages. Ferric chloride dosage rates are dependent on the pollutant concentrations in the stormwater runoff, unlike alum. Ferric chloride does not form a floc that settles out suspended pollutants. And, once settled, ferric chloride may be released from sediments under anaerobic conditions. 3.3.3.2 Pollutant Removal Capabilities Alum treatment has consistently achieved a 85 to 95% reduction in total phosphorus, 90 to 95% reduction in orthophosphorus, 60 to 70% reduction in total nitrogen, 50 to 90% reduction in heavy metals, 95 to 99% reduction in turbidity and TSS, 60% reduction in BOD, and >99% reduction in fecal coliform bacteria compared with raw stormwater characteristics. The following design pollutant removal rates are achievable reduction percentages for planning purposes derived from sampling data, modeling and professional judgment. In a situation where a removal rate is not deemed sufficient, additional controls may be put in place at the given site in a series or “treatment train” approach. Actual removal rates will depend on the specific installation design. • Total Suspended Solids – 90% • Total Phosphorus – 80% Page 3 - 158 Volume 2, Technical Guidance
Section 3.3.3 - Alum Treatment • Total Nitrogen – 60% • Heavy Metals – 75% • Fecal Coliform – 90% 3.3.3.3 Design Criteria and Specifications Alum treatment systems are fairly complex, and design details are beyond the scope of this manual. However, further information can be obtained by contacting local municipalities and engineers who have designed and implemented successful systems. The following are general guidelines for alum treatment systems: • Injection points should be 100 feet upstream of discharge points; • Alum concentration is typically 10 μg/l; • Alum treatment systems may need to control pH; • For pond design, the required size is approximately 1% of the drainage basin size, as opposed to 2-5% of the drainage basin area for a standard detention pond; • The local jurisdiction may require that the facility be placed in a reserve and/or establishment of a drainage easement the facility, which is accessible from a public road or other accessible easement. When required, the drainage easement should be at least 20 feet wide, provide a minimum traversable width of 15 feet, have a maximum slope of no more than 10%, and be appropriately stabilized to withstand maintenance equipment and vehicles. 3.3.3.4 Inspection and Maintenance Requirements Regular inspection and maintenance is critical to the effective operation of stormwater management facilities. An operation and maintenance plan is required and shall include: 1. “Covenants for Permanent Maintenance of Stormwater Management Facilities” (also called the “Maintenance Covenants”). An example covenants document can be found in Volume 3. 2. “Inspection Checklist and Maintenance Guidance” for each type of stormwater facility that is located on the property. Templates for each stormwater management facility can be found in Volume 3 of this manual. These templates can be amended slightly for use in more customized O&M plans. 3. As-built drawings must accurately identify the location and layout of the facility, and also clearly identify reserves and access easements. All stormwater management facilities must be maintained in accordance with the O&M Plan. Volume 2, Technical Guidance Page 3 - 159
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Section 3.3.3 - Alum Treatment<br />
• Total Nitrogen – 60%<br />
• Heavy Metals – 75%<br />
• Fecal Coliform – 90%<br />
3.3.3.3 Design Criteria and Specifications<br />
Alum treatment systems are fairly complex, and design details are beyond the scope <strong>of</strong> this<br />
manual. However, further information can be obtained by contacting local municipalities and<br />
engineers who have designed and implemented successful systems. The following are<br />
general guidelines for alum treatment systems:<br />
• Injection points should be 100 feet upstream <strong>of</strong> discharge points;<br />
• Alum concentration is typically 10 μg/l;<br />
• Alum treatment systems may need to control pH;<br />
• For pond design, the required size is approximately 1% <strong>of</strong> the drainage basin size, as<br />
opposed to 2-5% <strong>of</strong> the drainage basin area for a standard detention pond;<br />
• The local jurisdiction may require that the facility be placed in a reserve and/or<br />
establishment <strong>of</strong> a drainage easement the facility, which is accessible from a public road<br />
or other accessible easement. When required, the drainage easement should be at least<br />
20 feet wide, provide a minimum traversable width <strong>of</strong> 15 feet, have a maximum slope <strong>of</strong> no<br />
more than 10%, and be appropriately stabilized to withstand maintenance equipment and<br />
vehicles.<br />
3.3.3.4 Inspection and Maintenance Requirements<br />
Regular inspection and maintenance is critical to the effective operation <strong>of</strong> stormwater<br />
management facilities. An operation and maintenance plan is required and shall include:<br />
1. “Covenants for Permanent Maintenance <strong>of</strong> Stormwater Management Facilities” (also<br />
called the “Maintenance Covenants”). An example covenants document can be found in<br />
<strong>Volume</strong> 3.<br />
2. “Inspection Checklist and Maintenance Guidance” for each type <strong>of</strong> stormwater facility that<br />
is located on the property. Templates for each stormwater management facility can be<br />
found in <strong>Volume</strong> 3 <strong>of</strong> this manual. These templates can be amended slightly for use in<br />
more customized O&M plans.<br />
3. As-built drawings must accurately identify the location and layout <strong>of</strong> the facility, and also<br />
clearly identify reserves and access easements.<br />
All stormwater management facilities must be maintained in accordance with the O&M Plan.<br />
<strong>Volume</strong> 2, Technical Guidance Page 3 - 159