SLIDE 1 Stormwater Design for Redevelopment in Urban Watersheds
June 10, 2010 Brought to you by the Chesapeake Bay Trust and the U of MD Mid-Atlantic Water Program
SLIDE 2 Speaker Info
Tom Schueler Chesapeake Stormwater Network 117 Ingleside Avenue Baltimore, MD 21228 watershedguy@hotmail.com www.chesapeakestormwater.net Bill Stack Center for Watershed Protection 8390 Main Street Ellicott City, MD 21043 bps@cwp.org www.cwp.org
SLIDE 3 Webcast Agenda
- The Skinny on the MDE Redevelopment Rules
- Why Managing Stormwater at Redevelopment Sites is
So Hard (and So Important)
- Design Strategy for Redevelopment Sites
- Review of Effective Practices for Redevelopment
Sites
- Municipal Role in Green Streets
- Setting a Mitigation Fee when full compliance is not
possible
SLIDE 4 The skinny on redevelopment in Maryland
A copy of May 2010 emergency regs can be found in Resource 1
SLIDE 5 Redevelopment & Stormwater in Maryland
PREVIOUSLY (2000-2009)
- Redevelopment “loosely” defined.
- Must treat or reduce existing impervious area by at
least 20%.
- “Green technology” encouraged but not required
- Offset fees if criteria cannot be met on site
- Recharge waived.
SLIDE 6 Redevelopment and Stormwater Now
- Redevelopment is defined as a site with at least 40%
impervious area.
- Applies to disturbed area of project site, not the
entire site area
- Must treat or reduce existing imperviousness by
50%
- New development criteria if IC is increased
- “Green technology” referred to as Environmental
Site Design required
- Offset fees only as last resort
SLIDE 7 Redevelopment Math
Case 1: Proposed IC <= Existing IC/2
- Met your requirement
- Get out of jail
- Get keys to the City
Example: Existing IC = 10 acres Proposed IC= 5 acres 5 acres<= 10 acres/2 5 acres IC goal is met
SLIDE 8 Redevelopment Math
Case 2: Existing IC/2< Proposed IC <= Existing IC
- WQV = 1.0 inch * (Proposed IC-Existing IC/2)
- No Rev And CPV
- Minor but nagging headache
Example: Existing IC = 10 acres Proposed IC= 6 acres
WQv = 1.0 inch*6ac-(10ac/2)
SLIDE 9 Redevelopment Math
Case 3 Proposed IC > Existing IC
- WQV = 1.0 inch * Existing IC/2
- WQV and REv required for (Proposed IC – Existing IC)
- CPv (1.0 yr) required for (Proposed IC – Existing IC)
- Time for a miracle
Note: (WQv and Rev are inclusive of CPv)
SLIDE 10
Redevelopment Math
Case 3: Example
Existing IC = 10 acres Proposed IC = 11 acres
WQV = (1.0 inch * 10 acres/2) + (1.0 inch * 1 acre) REv required for (11 acres IC – 10 acres IC ) CPv (1.0 yr) required for (11 acres IC – 10 acres IC)
(WQv and Rev are inclusive of CPv)
SLIDE 11 Design Implications
Redevelopment sites with less than 40% IC are sized using the full new development criteria Strong incentive to sharply reduce IC at redevelopment sites, although this may be at odds with urban density objectives Strong stormwater “penalty” for large increases in IC at redevelopment sites
SLIDE 12 What Else Changed in May of 2010?
- Grandfathering
- Quantity control waivers
- More local flexibility to provide options in the
event of non-compliance at a redevelopment site (although many of these existed before)
SLIDE 13 Local Options in the Event Full Site Compliance is Not Possible
- Combo of ESD and on-site or off-site structural
BMP
- Retrofitting (BMP upgrades, filtering practices
and off-site ESD)
- Participation in stream restoration project
- Pollution trading
- Payment of a fee-in-lieu
- Partial waiver
SLIDE 14 Step 2: Calculate Site Imperviousness and Water Quality Volume, WQv Site Area, A (acres) 4 Existing Impervious Surface Area (acres) 2.5 Proposed Impervious Surface Area (acres) 3 Existing Imperviousness, Ipre 62.5% Proposed Imperviousness, Ipost 75.0% Development Category Redevelopment Rainfall Depth, P (in) 1.0 Runoff Coefficient, Rv 0.73 Water Quality Volume, WQv (ac-in) 2.90 Water Quality Volume, WQv (cf) 10,527 Step 4: Calculate Environmental Site Design (ESD) Rainfall Target, PE % Soil Type A 0% % Soil Type B 60% % Soil Type C 40% % Soil Type D 0% Pre-Developed Condition, RCNwoods 61 New Development Soil Type A ESD Rainfall Target, PE (in) 0.00 Soil Type B ESD Rainfall Target, PE (in) 1.32 Soil Type C ESD Rainfall Target, PE (in) 0.80 Soil Type D ESD Rainfall Target, PE (in) 0.00 Site ESD Rainfall Target, PE (in) 1.80 ESD Runoff Depth, QE (in) 1.31 ESD Runoff Volume, ESDv (cf) 18,949
A revised version of the ESD to the MEP spreadsheet is provided in Resource 2 Several bugs were fixed including an error in ESD sizing for redevelopment Throw out your old version! Updated users guide to be released next week
SLIDE 15
Many Bay States and Cities are Enhancing Stormwater Requirements at Redevelopment Sites For a comparative review, check out Resource No. 3
SLIDE 16
Why is Stormwater Management So Hard for Redevelopment Projects in Highly Urban Watersheds?
SLIDE 17 Why Redevelopment is So Hard
- Many projects are quite small
- Many cities traditionally waive redevelopment
projects
- Lack of space and/or high cost of land
- Constrained by inverts of existing storm drains
- Conflicts with existing underground utilities
- Compacted and polluted soils
- Traditional and even some new stormwater ESD
practices developed in suburban areas don’t work in
- ur cities
- Designers have little or no experience in designing
the practices that do
SLIDE 18 Why Redevelopment is So Hard – 2
- Most sites discharge to impaired waters subject to
TMDLs
- Natural stream network altered or eliminated
- Underground treatment is very expensive
- Full compliance can not be achieved at many sites
- Higher cost of compliance than in greenfield
settings*
- Conflicts with Smart Growth objectives of land use
efficiency
- Surface practices could result in loss of development
intensity
SLIDE 19
The Degree of Difficulty
Redevelopment Intensity (Post Development IC) Less than 40% 40 to 65% 66 to 85% 85 to 100%
Alternate Surfaces Alternate Surfaces Alternate Surfaces Alternate Surfaces Landscaping ESD Landscaping ESD Landscaping ESD Landscaping ESD IC Reduction IC Reduction Micro ESD Micro ESD Disconnections
SLIDE 20 Why Redevelopment is So Important
- Incrementally Reduces Untreated Pollution from
Existing Development
- Green Building and Green Infrastructure Movement
- Sustainable Cities
- Combined Sewer Overflow Abatement
SLIDE 21 Redevelopment expected to increase as a share of total development in the future
- About 2 million acres of existing IC in Bay
watershed
- 42% of urban land expected to be
redeveloped by 2030
- Sharp increase in growth in core cities and
inner suburbs in bay cities in last 5 years
- Sprawl seems to be slowing a bit in this
economy
SLIDE 22
Street Dirt Contains Many Harmful Pollutants
SLIDE 23
Stormwater Pollutant BALTIMORE National Average Fecal Coliform Bacteria 36,025 5,091 Total Copper 28 ug/l 16 ug/l Total Lead 64 ug/l 16 ug/l Total Nitrogen 2.8 mg/l 2.0 mg/l Total Phosphorus 0.32 mg/l 0.27 mg/l Oxygen Demand 19.3 mg/l 8.6 mg/l Baltimore Data from Diblasi (2008)
City Runoff Can Be More Polluted than Suburban Runoff
SLIDE 24
City Runoff Has a Very High load of Trash and Floatables
SLIDE 25 Stormwater Runoff is a Leading Cause of Water Quality Impairment
SLIDE 26 Stormwater Compounding ( 5 to 59% IC treated in 25 years) Source: Philadelphia OW
SLIDE 27
Ten Strategies to Integrate Redevelopment with Stormwater
SLIDE 28
- 1. Understand the Urban Watershed Context
- Pollutant of Concern
- Combined or Separate Sewers
- Age of watershed development
- Habitat condition of streams
- Hydraulic capacity of existing
stormwater conveyance and floodplain
- Historical flooding capacity
- Existence of watershed plans
- Other stormwater retrofit and
restoration opportunities
SLIDE 29
- 2. Investigate Site History
- Most redevelopment projects require an
environmental site assessment to determine if they are subject to “brownfield” remediation
- Site history investigation, soil testing and
groundwater analysis
- These data are critical in stormwater design
to determine whether:
- Soils need to be capped
- Infiltration should be encouraged or
discouraged
- Historical drainage paths can be used to
route stormwater
- Existing utilities will constrain design
SLIDE 30
- 3. Better Site Design in the Urban Context
- Land Use Efficiency (density is encouraged)
- Unique and Attractive Street-Scapes
- Integration of Stormwater & Landscaping
- Reduce Parking Demand
- Shared or Structured Parking
Several useful guides can be found in the weblinks found in Resource 4
SLIDE 31
- 4. Identify Potential Hotspot Generating Areas (HGAs)
- Review future site operations and activities
- Common areas include loading/unloading, fueling, outdoor
storage, dumpsters, compactors and maintenance
- Identify areas of high pedestrian and vehicular traffic
- HGAs usually only a fraction of site area
- Isolate HGA in design and cover or filter runoff
- Integrate pollution prevention into design
SLIDE 32
- 5. Really Reduce Impervious Cover at the Site
- Strong incentive to make token change in site
footprint to reduce IC to comply
- The “reduced IC” should perform hydrologically as if
it were un-compacted grass, and ideally should be used to filter some runoff from remaining hard surfaces
- Deed or covenant that the area cannot be rebuilt in
the future
SLIDE 33
- 6. Decompose Site Into Smaller Drainage Units
SLIDE 34 Source: COE,(2005)
SLIDE 35 Source: COE,(2005)
SLIDE 36
- 7. “Roof to Street” Design Approach
SLIDE 37
- 8. Maximize Forest Canopy and Restore
Natural Area Remnants
SLIDE 38
- 9. Careful Urban Infiltration and Recharge
- Past development has
destroyed soil structure and porosity
- Urban soil infiltration rates are
very low
- Increased risk to foundations,
infrastructure and landscaping
- Avoid infiltrating at hotspot &
brown-field sites
- Infiltrate a fraction of WQv
and rely on extended filtration (storage and underdrains)
SLIDE 39 Urban Fill Soils and Recharge
will be on fill soils
- Fill soils cannot be classified
into any hydrological soil group
- Infiltration into fill soils is
not desirable
are not subject to the recharge volume requirement
- For new IC, assume D soils
for Pe comps
SLIDE 40
- 10. Establish Offset Fee
- Set Offset Fee when
compliance cannot be achieved
untreated runoff volume, impervious cover or phosphorus load generated by site
some ESD has been utilized
- n the site
- Fees are used for retrofit
- r restoration projects in
the same watershed
SLIDE 41 Photos: Chesapeake Bay Program
Questions and Answers
SLIDE 42 Green Roofs * Cisterns and Rain Tanks * Permeable Pavers * Bioretention * Expanded Tree Pits Urban Tree Planting Foundation Planters Green Streets Sand Filters
Sustainable Stormwater Practices for the City
After: Courtyard bioretention
SLIDE 43 Green Roof
- Extensive green roof can be
major element of compliance at many redevelopment sites
- High installation cost is
compensated by long term energy savings and roof longevity
- 70% of Bay engineers have never
designed one
- New design specification available
from CSN
SLIDE 44 Rain Tanks and Cisterns
- Redevelopment intensity means
more internal demand for non- potable water
landscape irrigation
- Moderate cost of $15 cubic
foot
- 60% of Bay Engineers have
never designed one
spreadsheet available from CSN
SLIDE 45 Permeable Pavers
most redevelopment sites
for extended filtration
space and plazas
- Design as enhanced filter
rather than as an alternative surface
SLIDE 46
Foundation Planters
SLIDE 47 Proposed Design Guidelines for Foundation Planters
- Not specifically described in MDE
Chapter 5, but is certainly an acceptable micro-ESD practice
- Pe = 15” x Surface Area/CIDA
- Rapid flow through design
- Use hi sand media recipe (80%)
- More details can be found in
Urban Bioretention Spec and Portland Guide (see Resources 5 and 6)
SLIDE 48
Impervious Cover Removal
SLIDE 49 Proposed Design Guidelines for IC Removal
- No specific MDE guidelines yet
impervious cover reduction
- Plans should show the specific
areas where concrete or asphalt will be removed
- Underlying soils should be deep
tilled and amended with compost to restore porosity
- Areas should be graded to accept
runoff from adjacent hard surfaces
- Planting plan should reflect
landscaping objectives
Courtesy S. Schwartz
SLIDE 50
Reforestation and Street Tree Credit
SLIDE 51 Proposed Design Guidelines for Reforestation
Not specifically addressed in MDE manual It can be treated as a disconnection
- 1 Street Tree = 100 sf Imp Area
- Soil Restoration and Reforestation = 200 sf
Or as a Micro-ESD Practice
- Expanded Tree Pit
- Pe = 12” x Surface Area/CIDA
- Must combine adequate root volume and
water drainage in either case
SLIDE 52
Expanded Tree Pits
SLIDE 53 Source: City of Baltimore, MD
SLIDE 54
Design and Construction Issues
SLIDE 55
Underground Sand Filter and Proprietary Practices
SLIDE 56
Green Street Bioretention:
SLIDE 57
Lessons Learned in Green Streets in Baltimore
SLIDE 58 Figure 9: Sidewalk enhancements on Collington between Lombard and Baltimore Streets Figure 10: Bump out at Collington and Lombard Street
Green Streets are Popular in Neighborhoods
SLIDE 59
Tree Box Inlet with Curb Extension and Bioretention
SLIDE 60 B-15: Tree Box Inlet with Curb Extension and Bioretention
Post- Construction Pre- Construction During Construction
SLIDE 61 Project Selection and Design Issues
- Initially High Design Costs
- Initial High Interagency Coordination
Right-of-Way Highway Design Street Lighting Traffic Engineering ESC Wastewater Engineering Stormwater Engineering Traffic Control MOT
SLIDE 62 Construction Issues
– 10 to 30 day construction period
– Every project requires closing at least two travel lanes
- Coordination with utilities and other City agencies
– street lights, parking meters, changes in traffic patterns and parking restrictions)
- Equipment and materials staging locations
– Not a lot of extra space in an urban area – Contractor has to haul excess material off-site
SLIDE 63 Making Green Streets Happen
- Strong Grass Roots support
- Visual aides showing outcomes
- Cost benefit numbers (expanded community
benefit)
- Requires municipal leadership
- Interagency coordination to get consensus
- Initial demonstration and testing to convince the
skeptics
- Local Green street design manuals
SLIDE 64 The Price of Stormwater
– IC and CDA – New vs Redevelopment – Design Era – Your Agenda
SLIDE 65 The Stormwater Version of the Price is Right Show
For the technical assumptions for the following cost projections, please consult resources 7 and 8
SLIDE 66
$120.00 $10.00 $225.00 $25.00
What is the Price of Treating a Cubic Foot of Stormwater?
SLIDE 67 What is the Cost to Treat:
One Acre of IC of Urban Redevelopment One acre of IC at Pre-ESD Greenfield Development One acre of IC at Greenfield Development to ESD One Acre of IC with Storage Retrofits
$31,700 $46,500
$191,000
$32,500
SLIDE 68 What is the Cost to Treat:
One acre IC with Green Streets
Stream Restoration in length equivalent to one acre IC, expressed in terms
$167,120 $35,600 $167,100
SLIDE 69 Setting up a stormwater
- ffset fee
- Fully recover all public costs for
stormwater mitigation (D-E-P, Contracting, Maintenance)
- Municipally-driven
- Watershed-based
- Equitable (the price)
- Easy to administer
- Indexed for construction inflation
- Must do some on-site ESD
- Reflect the development intensity
in your community
SLIDE 70 Why a Locality Should Avoid Waivers
- You will get some nutrient liability in the Bay
TMDL and the MS4 permit in the future
- Mitigation fee creates a revenue stream to
support retrofitting and watershed restoration
- Environmental community is watching this issue
very more closely
SLIDE 71 Recommended Accountability Elements in Local Stormwater Offset Fee
- Define qualifying public sector
projects (e.g., retrofits, stream restoration, green streets)
- Conduct watershed restoration
inventory to ID candidate projects
- Identify priority projects in
watershed plan
- Track funds collected and
disbursed
- Keep a retrofit registry that
tracks project implementation and IC areas treated
SLIDE 72
Suggested Stormwater Offset Fees for Maryland
Fee Should be expressed in unit terms such as: Per pound of phosphorus to be removed Per acre of untreated impervious cover Per cubic feet of untreated water quality volume To be equitable, the fee should be set at the cost of effectively retrofitting development by the public sector. Funds collected should be used to provide equivalent runoff reduction and/or pollutant removal in the same watershed
SLIDE 73
Example of Offset Fee
Assume a unit fee of $35,000/IC acre 20,000 sf Commercial Redevelopment 90% Impervious Pre-development 5000 sf of IC treated by on-site ESD practices 0.3 untreated acres of IC 0.3 * 35,000 = $10,500 Please make check payable to “chesapeake stormwater network”
SLIDE 74
Stormwater Smackdown
So at what level should the offset fee be set? Tom: Set fee to recover the public sector cost to implement storage retrofits in a suburban setting ($32,500 per IC acre) Bill: Set fee to recover the public sector cost to implement Green Streets or ESD practices in urban setting ($167,100 per IC acre)
SLIDE 75
Questions and Answers
SLIDE 76
Session Resources
Redevelopment Reqmts in Other Bay States Links to good Redevelopment Specs and Design Manuals Urban Bioretention Guide Portland Specs for Foundation Planters Retrofit Appendix with Cost Data (Appendix E) Technical Documentation for Cost Estimates