Table L‐2: BMP Summary Matrix A B C D E F G Standard 2 1 2 BMP Type Best Management Practice 3 4 Source Control and Non‐Structural BMPs Street Sweeping 5 6 Semi‐annual Catch Basin Cleaning11 7 No Application of Fertilizers Containing Phosphorus12 No sand zone for deicing 8 Designate as Low Salt Zone 9 Illicit Discharge Review 10 Review of bird habitat impacts 11 12 Structural Pretreatment BMPs Deep Sump Catch Basin 13 Oil Grit Separator 14 Proprietary Separator 15 Sediment Forebay 16 Vegetated Filter Strip 17 Open Graded Friction Course 18 19 Treatment BMPs 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 6/8/2010 Handbok Reference DEP J K Standard 4 L Standard 5 M Standard 6 N Standard 7 O P Q R Discharges to or Higher Pollutant Re‐ near Critical Loading development Areas 8 Recharge 2‐Yr Storm 10‐Yr Storm 100‐Yr Storm Applicability MassDEP Removal Credit9, 10 n/a n/a n/a ● ● 0% ‐ 10% Varies w/frequency Total Nitrogen Total Phosphorous Metals (Cu, Pb, Zn, Cd) Pathogens Insufficient Data 20% 10% Insufficient Data Insufficient Data ● ● ● ○ ● ● ● 25% 25% Varies 25% 10% ‐ 45% (Width 25' ‐ 50') ● ● ○ ○ ○ no no Varies no no no MassDOT (DEP) yes Extended Dry Detention Basin Wet Basin Constructed Wetlands MassDOT (DEP) MassDOT (DEP) yes yes ● ● ● ● Constructed Stormwater Wetland Gravel Wetland Filtration BMPs MassDOT (DEP) MassDOT (DEP) yes yes ● ● ● ● MassDOT (DEP) MassDOT MassDOT yes Varies no no MassDOT (DEP) MassDOT (DEP) yes yes MassDOT (DEP) MassDOT (DEP) yes yes ○ ○ ○ ○ MassDOT (DEP) MassDOT (DEP) MassDOT (DEP) MassDOT (DEP) MassDOT (DEP) no yes yes yes yes ○ ○ ○ ○ 1 ○ ○ ○ ○ MassDOT (DEP) DEP MassDOT (DEP) DEP MassDOT no no no no no ● ● ● DEP MassDOT (DEP) DEP DEP MassDOT n/a n/a n/a n/a n/a MassDOT n/a ○ ○ ● ● ● ● ● ○ ● ○ ● 90% with vegetated filter strip or equivalent ○ ○ ● ● 50% w/sediment forebay 80% w/sediment forebay ○ ○ ● ● ● 80% w/sediment forebay 80% w/sediment forebay ○ ○ ● ● ● ● ● ● 80% w/sediment forebay Varies ● ● 80%10 80%10 ● ● ● ● ● ● ● 3 ● 4 ○ ○ 5 ○ ● ● 10% ‐ 90% 10% ‐ 90% ● 6, 5 ●5 ●5 ●5 ●5 ● 6 ○ ● ● ● 50% ‐ 60% 60% ‐ 70% 85% ‐ 90% 0.9 40% ‐ 70% 40% ‐ 70% 85% ‐ 90% ≤ 90% MassDOT assumes comparable to inflitration trench MassDOT assumes comparable to inflitration trench ○ 5% ‐ 50% 44%10 Insufficient Data ● Insufficient Data ● Requires product‐specific evaluation ‐ see discussion in Section 5.0 Insufficient Data Insufficient Data ● Insufficient Data ● ● 30% ‐ 50% 30% ‐ 90% 40% ‐ 90% Insufficient Data ● 15% ‐ 50% 10% ‐ 50% 10% ‐ 30% 30% ‐ 70% 30% ‐ 50% 30% ‐ 75% < 10% 40% ‐ 90% ● ● 20% ‐ 55% 20% ‐ 55% 40% ‐ 60% 40% ‐ 60% 20% ‐ 85% 20% ‐ 85% ≤ 75% ≤ 75% Stormwater Treatment Basins Sand or Organic Filter Proprietary Media Filter Media Filter Drain Compost Amended Vegetated Filter Strip Conveyance BMPs Drainage Channel Grassed Channel (Biofilter Swale) Water Quality Swale Dry Swale Wet Swale Infiltration BMPs Dry Well Infiltration Basin Infiltration Trench Leaching Catch Basin/Leaching Basin Subsurface Structure Other BMPs Dry Detention Basin Green Roof7 Porous Pavement Rain Barrel/Cistern7 Outlet Sediment Trap Accessories Level Spreader Check Dam Outlet Structure Catch Basin Insert Flow Splitter Impoundment Structures: Suggested Design Considerations for Small Dams Legend ● ○ Applicable May be applicable with careful design Selection Priority for MassDOT Applications ● Strongly recommended for treatment of Pollutant of Concern (POC) ● Recommended for treatment of POC Recommended with caution for treatment of POC ● Site specific evaluation required ● ○ ○ ○ ● ● ● ● ● ● ● 0% 50% w/pretreatment ● ● 70% w/pretreatment 70% w/pretreatment ● ● ● ● ● 80% 80% w/pretreatment 80% w/pretreatment 80% if offline w/pretreatment 80% ● ● ● ● ○ ● ● ● ● 0% n/a 80% n/a ○ 25%12 ● ● Varies Varies ○ ● ● 20% ‐ 40% 10% ‐ 50% 50% ‐ 90% Requires product and media‐specific evaluation ‐ see discussion in Section 5.0 Insufficient data Insufficient data ‐121% 65% ‐ 85%12 75% ‐ 85%12 85% ‐ 90%12 80% ‐ 90%12 Notes: With careful design for small sites Not suitable for areas near cold water fisheries May be used to reduce temperatures of runoff Not suitable for vernal pools or bathing beaches; may be used as pretreatment for other critical 5 6 7 8 9 10 11 12 Insufficient Data Insufficient Data Insufficient Data Insufficient Data Insufficient Data Insufficient Data Insufficient Data 20% ‐ 90% 20% ‐ 90% Insufficient Data ● ● ● 10% ‐ 30% 30% ‐ 50% n/a Insufficient Data n/a Insufficient Data n/a n/a n/a Requires product and media‐specific evaluation ‐ see discussion in Section 5.0 n/a n/a 1 2 3 4 S Pollutant Removal Efficiencies ‐ MassDEP Stormwater Handbook11 TSS Removal MassDOT (DEP) MassDOT (DEP) DEP MassDOT (DEP) MassDOT (DEP) MassDOT Bioretention Area/Rain Garden I Standard 3 Peak Discharge Rate Control Pretreatment Required? n/a H Recommended for cold‐water fisheries May only be used for runoff from nonmetal roofs within Zone II or IWPA Not applicable for roadways Additional pretreatment may be required under certain design conditions; see DEP Handbook Volume 1, Chapter 1, Table RR See Table 5‐2 for Pollutant Removals from EPA Performance Analysis Removal rates for selected BMPs estimated by MassDOT Removal Rates based on Residual Designation App. D ‐ only for areas not treated by other BMPs Removal Rates based on Residual Designation App. D ‐ applicable to entire developed area with no phosphorus fertilizer applied < 10% T U Other Pollutants of Concern pH Thermal modifications/ Temperature Chloride Table L‐3: Design BMP Pollutant Removal Rates BMP Type Best Management Practice Street Sweeping Structural Pretreatment BMPs Deep Sump Catch Basin Oil Grit Separator Proprietary Separator Sediment Forebay Vegetated Filter Strip Open Graded Friction Course Treatment BMPs Bioretention Area/Rain Garden Stormwater Treatment Basins Extended Dry Detention Basin Wet Basin Constructed Wetlands Constructed Stormwater Wetland Gravel Wetland Filtration BMPs Sand or Organic Filter Proprietary Media Filter Media Filter Drain Compost Amended Vegetated Filter Strip Conveyance BMPs Drainage Channel Grassed Channel (Biofilter Swale) Water Quality Swale Dry Swale Wet Swale Infiltration BMPs Dry Well Infiltration Basin Infiltration Trench Leaching Catch Basin/Leaching Basin Subsurface Structure Other BMPs Dry Detention Basin Green Roof Porous Pavement4 Rain Barrel/Cistern Outlet Sediment Trap Accessories Level Spreader Check Dam Outlet Structure Catch Basin Insert Flow Splitter Impoundment Structures: Suggested Design Considerations for Small Dams Notes: 6/8/2010 Source of Criteria1 TSS 0.5 in. WQV Pollutant Removal (%)2,3,5 TP Zn 1.0 in 0.5 in. 1.0 in 0.5 in. 1.0 in WQV WQV WQV WQV WQV TSS removal varies w/frequency MassDEP 0‐10 MassDEP MassDEP MassDEP MassDEP MassDEP MassDOT 25 25 25 10‐45 44 USEPA 95 99 58.5 76 95.5 97 USEPA USEPA 39 64 46 77 8.5 9.5 12 18 68.5 82.5 73 89 MassDEP USEPA 80 86.5 80 97 40‐60 46 40‐60 61 20‐85 85.5 20‐85 90 MassDEP MassDEP MassDOT MassDOT 80 80 80 MassDEP MassDEP 0 50 0 50 USEPA 65.5 65.5 80 80 MassDEP USEPA 80 95.5 96 97 97.5 99 100 89.5 92.5 94.5 96 98.5 100 80 Insufficient Data 100 76.5 92 97 100 79 93 98 100 82 95 98.5 100 85.5 97 99.5 100 90.5 98 100 100 97.5 100 100 99 65 89 96 100 70 91 98 100 74.5 94 98.5 100 78.5 96 99.5 100 86 98 100 100 96 100 100 assumed similar to infiltration trench assumed similar to infiltration trench USEPA MassDEP MassDEP USEPA MassDEP MassDOT 0 0‐10 Remarks Insufficient Data 25 Insufficient Data 25 Insufficient Data Requires product‐specific evaluation 25 Insufficient Data 10‐45 Insufficient Data 44 Insufficient Data 80 10‐50 10‐50 50‐90 50‐90 Requires product and media‐specific evaluation 80 65‐85 65‐85 85‐90 85‐90 80 75‐85 75‐85 80‐90 80‐90 0 Insufficient Data Insufficient Data 11 11 21 21 10‐30 88.5 88.5 95 95 100 100 100 100 100 100 99 100 100 100 100 100 10‐30 30‐50 30‐50 62 69 74 78 85 97 97 98 85 97 97 98 0.17 in/hr. infiltration rate 0.27 in/hr. infiltration rate 0.52 in/hr. infiltration rate 1.02 in/hr. infiltration rate 2.41 in/hr. infiltration rate 8.27 in/hr. infiltration rate 0.17 in/hr. infiltration rate 0.27 in/hr. infiltration rate 0.52 in/hr. infiltration rate 1.02 in/hr. infiltration rate 2.41 in/hr. infiltration rate 8.27 in/hr. infiltration rate n/a 92 94 96 97 92 94 96 97 25 25 62 69 74 78 12" filter course 18" filter course 24" filter course 32" filter course n/a Insufficient Data n/a MassDEP Requires product and media‐specific evaluation n/a 1 Performance data in this Table is derived from EPA (March 2010). Where this source does not provide performance data, information is taken from MassDEP (Massachusetts Stormwater Handbook, 2008) or from MassDOT (Stormwater Handbook for Highways and Bridges, 2010). 2 For EPA performance data, the values listed assume highway surfaces are equivalent to "commercial land use" as used in the EPA Stormwater Best Management Practices (BMP) Performance Study (Revised March 2010). 3 BMPs may be sized for treating other Water Quality Volumes than those listed. Refer to the EPA study for pollutant removal data for other Water Quality Treatment Volumes. 4 Porous pavement performance analysis is based on depth of filter course, as this BMP treats all water that falls on it, not just the Water Quality Volume. Performance ratings are therefore provided for a range of filter course depths. 5 For data on removal rates for nitrogen and pathogens, see Table 5‐2. Table L‐4: Conditions Affecting Selection of BMPs Physical Feasibiliy Factors Notes: 6/8/2010 ● ● ● ● ● ● ● ● ● ○ ○ ○ ○ ● ● ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ○ ● ● ● ● ○ ○ ● ● ● ● ● ● ○ ○ ○ ○ ○ ○ ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ○ ○ ○ ● ○ ● ● ● ● ○ ○ ● ● ● ● ● ● ● ● ● ○ ● ● ○ ○ ○ ● ● ○ ○ ● ● ○ ○ ○ ● ● ● ● ● ● ● ○ ● ○ ● ● ● ● ● ● ● ○ ● ○ ● ○ ● ● ○ ○ ○ ● ● ● ○ ○ ● ● ○ ○ ○ ○ ○ ○ ● ● ○ ○ ● ● ● ● ● ● ● ● ○ ○ ○ ○ ● ● ● ● ○ ○ ● ● ○ ○ ○ ○ ○ ○ ● ● ○ ○ ● ● ● ○ ○ ○ ● ● ● ● ● ● ○ ○ ○ ○ ○ ● ● ● ● ○ ○ ● ● ● ● ● ● ● ● ● ○ ● ● ● ● ○ ○ ○ ○ ○ ○ ○ ○ ● ● ○ ○ ● ● ○ ○ ● ● ○ ○ ● ○ ○ ● ● ○ ○ ● ● ○ ○ ● ● ○ ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ○ ● ○ ● ● ● ● ● ○ ○ ○ ○ ○ ● ○ ● ● ○ n/a ○ ● ● ● ● ● ● ● ● ● ○ ○ ○ ○ ● ○ ● ● ● ○ ● ● ● ○ ○ ○ ○ ○ ○ ○ ● ● ○ ● ● ● ● ● ● ● ● ○ ○ ○ ● ● ● ● ○ ○ ○ ● ● ● ● ● ● ● ● ○ ● ● ● ● ● ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ○ ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ○ ○ ○ ○ ● ● ● ● ● ● ● ● ● ● ● n/a ● ● ● ● ● ● ● ○ ● ○ ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ● ● ● ● n/a n/a n/a n/a n/a ● ● ● ● ● ● n/a ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ● ● ● ● ○ ● n/a ● ○ ● ● ● ● ● ● ● ○ ● ○ ○ ○ ○ ○ n/a n/a ○ ● ● ● ● ● ● ○ ● ● ● ○ ○ ○ ○ ○ ● ● ● ● ● ● ● ● ● ● ○ ○ ● ● ● ● ● ● ● ● n/a ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ○ ● ● ● n/a 1 Clearance to high water table or bedrock is measured from the bottom surface of the BMP. (e.g., bottom surface of wet pond, infiltration basin, of other basin; bottom of lowest storage layer for porous pavement, subsurface infiltration system). < 0 ft means water table may be higher than bottom surface of BMP 2 Consult Title 5 Regulations (310 CMR 15.00) for specific setback requirements. Not all provisions are reflected in this table. For example, dry wells may be no closer than 25 ft. to a soil absorption system; surface and subsurface drains that discharge to a surface water supply may be no closer than 100 feet. 3 Vegetated filters, media filter drains, and compost‐amended vegetative filter strips are not limited to a maximum drainage area, but are limited to maximum contributing lengths of flow. See discussion under the description for each of these BMPs. ● ○ ● ○ ● n/a ● ● ● ● ○ ● ○ ● ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ○ ● ○ ● ○ ○ ● ○ ● ● ● ● ● ● ● ● ● ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● n/a Legend ● ○ n/a ○ ○ n/a Applicable May be applicable with careful design Criteria not applicable ○ ○ ● ● ● n/a Low Moderate ● ● n/a n/a ● ● ● ● Significant > 15% 6% to 15% 0 to 6% Requires Large Land Area Requires Small Land Area > 10 ft ≤10 ft > 50 ft ○ ○ ○ ○ ○ ○ Maintenance Sensitivity Slope n/a n/a ● ● ● ● ● ● ● ● ● Property Line ● ● ● ○ ○ ○ ○ ● ● ● Other Surface Waters n/a n/a n/a n/a ● ● ● ● ● ● Land Area ≤ 50 ft ● ● ● ● ● ● ● ● Public Reservoir Within Zone A ● ● ● ● ● ● ● ● Public Wells Within Zone 1 ● ● n/a n/a > 100 ft ● ● n/a n/a Private Wells ≤ 100 ft ○ ○ ● ● ● Setback Requirements > 50 ft ● ○ ○ ● ● ● 1 ≤ 50 ft ● ● > 2 ft ● ● Clearance to Bedrock 0‐2 ft ● ● > 2 ft ● ● < 0 ft 0‐2 ft 50+ ● ● Clearance1 to High Water Table Title 5 Soil Absorption System2 >2.41 20‐50 ● ● <0.17 10‐20 3 Vegetated Filter Strip Open Graded Friction Course Treatment BMPs Bioretention Area/Rain Garden Stormwater Treatment Basins Extended Dry Detention Basin Wet Basin Constructed Wetlands Constructed Stormwater Wetland Gravel Wetland Filtration BMPs Sand or Organic Filter Proprietary Media Filter Media Filter Drain3 Compost Amended Vegetated Filter Strip3 Conveyance BMPs Drainage Channel Grassed Channel (Biofilter Swale) Water Quality Swale Dry Swale Wet Swale Infiltration BMPs Dry Well Infiltration Basin Infiltration Trench Leaching Catch Basin/Leaching Basin Subsurface Structure Other BMPs Dry Detention Basin Green Roof Porous Pavement Rain Barrel/Cistern Outlet Sediment Trap Accessories Level Spreader Check Dam Outlet Structure Catch Basin Insert Flow Splitter Impoundment Structures: Suggested Design Considerations for Small Dams 5‐10 Street Sweeping Semi‐annual Catch Basin Cleaning Structural Pretreatment BMPs Deep Sump Catch Basin Oil Grit Separator Proprietary Separator Sediment Forebay 1‐5 Best Management Practice 0‐1 BMP Type >0.17 and <2.41 Soil Infiltration Capacity (inches per hour) Drainage Area (acres) ● ● ● ● ● ● ● ● ● ● ● ● ● ● ○ ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●