Benefits of Green Infrastructure
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Transcript of Benefits of Green Infrastructure
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Benefits of GI
EPA Wet Weather Workshop
Charleston, WV, July 21 , 2009
Paula Estornell, EPA Brownfields Program Manager
Outline
Wet Weather and Water Quality
Benefits of GI
Financial, Public Health, Environmental
GI BMP Performance BMP, Site Level, Watershed Level
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Water Quality Problems in the 1960s
Cuyahoga River, 1960sCuyahoga River, 1960s
Water Quality Problems Today
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US Water Quality SnapshotAssessed water not meeting WQS (1)
RiversOver 40%
LakesOver 45%
EstuariesOver 51%
Coastal
Over 75%
(1) National Water Quality Inventory Report,(1) National Water Quality Inventory Report,2000; Statistically Valid Surveys of the Nations2000; Statistically Valid Surveys of the NationsWaters, 2005, 2006Waters, 2005, 2006
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Urbanized Areas in West Virginia
Charleston Urbanized AreaEncompasses Montgomery to Hurricane
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Thinking Outside the Pipe
Back to Nature
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Benefits of GI Financial Lower costs
Higher tax base
Active commercial districts
Jobs
Public Health Wellness
Cooler cities
Recreation
Stronger communities
Crime reduction
Environmental Habitat
Cleaner air Cleaner water
EPA Reducing Stormwater Costs through LID Strategies and Practices
EPA GI Cost-effectiveness Study, 2007
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vegetated strips, nocurbs = 11% reduction in
impermeable surface
25% cost savings
compared to
conventional design
90+% runoff reduction
Cost-Effectiveness: Seattle SEA Streets
EPA GI Cost Analysis, 2009
Modeled Capital Costs for 4 Sites
4 to 27 acres
40% to 95% imperviousness
3 Climate Conditions
3 Design Storms
GI vs. LID costs competitive
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Site A: Single Family Residential Development(40% imperviousness)
Grey Design
Green DesignCapital costs for entire site
Note: All sites use traditional
development patterns and do not
represent innovative green designs
InletsYellow Pipes
Off-site Storage
Bioretention
$0
$20,000
$40,000
$60,000
$80,000
$100,000
$120,000
$140,000
$160,000
$180,000
$200,000
Humid
(48.9"/ yr)
Humid
(41.9"/ yr)
Semi Arid
(15.2"/ yr)
90% Design 95% Design Traditional
Site B: Commercial Development(55% imperviousness)
Grey Design
Capital costs for entire site
Green Design
Bio
rete
ntion Surface Drainage
$0
$100,000
$200,000
$300,000
$400,000
$500,000
$600,000
$700,000
$800,000
Humid(48.9"/ yr)
Humid(41.9 / yr)
Semi Arid(15.2"/ yr)
90% Design 95% Design Traditional
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Site C: High Density Residential Development(70% imperviousness)
Grey Design
Capital costs for entire site
22 acre site
Green Design
Bioretention Surface Drainage
Porous Pavement
$0
$100,000
$200,000
$300,000
$400,000
$500,000
$600,000
$700,000
$800,000
Humid
(48.9"/ yr)
Humid
(41.9"/ yr)
Semi Arid
(15.2"/ yr)
90% Design 95% Design Traditional
Site D: Industrial Development(95% imperviousness)
Capital costs for entire site
27 acre site
Green Design
Cisterns
SurfaceDrainage
Porous Pavement
Green
Roof
Grey Design
$0
$500,000$1,000,000
$1,500,000
$2,000,000
$2,500,000
$3,000,000
$3,500,000
$4,000,000
Humid (48 .9"/
yr)
Humid (41.9 /
yr)
Semi Arid
(15.2"/ yr)
90% Design 95% Design Traditional
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Energy SavingsGreen Roof at WVU, Monongalia River
Real Estate Value:A Philadelphia Story
Vacant land improvements
increased surrounding
housing values by as much
as 30%
New tree plantings
increased surrounding
housing values by
approximately 10%
Before
After(University of PA data)
(Philadelphia Watersheds Office photos))
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Increases Commercial District
Revenue
More frequent/longer shopping
Shoppers spend more
for parking
Shoppers spend 12% more
for goods
http://www.ccurbangreen.org/Benefits.html
Green Jobs
Entry level landscaping
Certified permeable
pavement installers
High skilled engineering,landscape architecture,
monitoring
Chicago GreenCorps at Our Lady Gate of Heaven project site
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Benefits of GI Financial Lower costs
Higher tax base
Active commercial districts
Jobs
Public Health Wellness
Cooler cities
Recreation
Stronger communities
Crime reduction
Environmental Habitat
Cleaner air Cleaner water
Public HealthBenefits
Views of nature reduce the stress response (Parsons et.al., 1998).
Trees (along with other plants) absorb high-frequencynoise which is the most distressing frequency range forhumans (Miller, 1997).
Hospital patients that see trees need less medicationand have faster recovery times following surgery (Ulrich,1985).
http://www.ccurbangreen.org/Benefits.html
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Urban Cooling
Trees:
10% canopy increase
5-10% energy savings
from shading, wind blocking
Green Roof:
15% green roof coverage
5-9 degree heat island reduction
Permeable pavements:
reduce heat island
Crime Reduction
Compared with areas that had little or no vegetation,
buildings with high levels of greenery had 52% fewer
crimes
Landscape and Human Health Laboratory
University of Illinois at Urbana-Champaign
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Community Connection
Recreation
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Benefits of GI Financial Lower costs
Higher tax base
Active commercial districts
Jobs
Public Health Wellness
Cooler cities
Recreation
Stronger communities
Crime reduction
Environmental Habitat
Cleaner air Cleaner water
Habitat
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Air Quality
10 ft2 roof removes pound
particulate per year
Chicago2 million square feet built, 4 million planned
~ annual particulate capture from
74,322 cars
Surface Water Protection Aquatic Life
Fish Consumption
Swimming
Drinking Water
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Monitored Demonstrations
Typical Pollutant Removal
International BMP Database Bay Runoff Reduction Report
(October 2007) (April 2008)
BMP Type TSS TP TN TP TN
(influent/effluent (mg/l)) (% Removal)
Detention Pond 72/31 .19/.19 1.3/2.7 15 10
Wet Pond 34/13 .21/.12 1.6/1.4 50-75 30-40
Constructed Wetlands 38/18 .27/.14 2.1/1.2 50-75 25-55
Biofilter (biofiltration) 52/24 .25/.34 .9/.8 25-50 40-60
Media Filter 43/16 .2/.14 1.3/.76 60-65 30-45
Porous Pavement NA/17 NA/.09 NA 25 25
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Bioretentionl
TSS TPH D NO3 Zn
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Raingarden Performance
Infiltration reduces peakdischarge rate
Vegetative uptake of
stormwater pollutants
Pretreatment for
suspended solids
plus
Groundwater recharge
Aesthetic Improvement
0.06mg/
0.38m g/l
774ug/l37 mg/l
0%10%20%30%40%50%60%70%80%90%
100%
-
RemovalEfficiency
Summer
W inter
Annual
Performance Efficiencies Filtration/Infiltration
University ofNew HampshireStormwater Center
Sediment Hydrocarbons Nitrogen Zinc
Raingardens (Bioretention)
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Porous Asphalt
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Porous Pavement Performance
16 year old porouspavement in Philadelphia
reported zero discharge
during Hurricane Floyd in
1999 (10 rain/24 hours)
Functions in cold weather
75% reduction in salt use
(Toronto & NH) from
reduced surface freezing
37 mg/l
774ug/l0.06mg/l
0%10%20%30%40%50%
60%70%80%90%
100%
RemovalEfficiency
SummerWinterAnnual
Performance Efficiencies Filtration/Infiltration
University ofNew HampshireStormwater Center
Sediment Hydrocarbons Nitrogen Zinc
Porous Asphalt
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Stormwater Wetlands
Shallow marsh
Extended detention
wetland
Gravel based
wetland
Gravel Wetland
0.06mg/
0.38mg/l
774ug/l37 mg/l
0%10%20%30%40%50%60%70%80%90%
100%
RemovalEfficiency
Summer
Winter
Annual
Performance Efficiencies Filtration/Infiltration
University ofNew HampshireStormwater Center
Sediment Hydrocarbons Nitrogen Zinc
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Conservation
Open
Drainage
Rain
Gardens
Amended
Soils
Rain
Barrel
Porous
Pavement
Create a Hydrologically Functional Lot
GI at Site Level(Whiteman, EPA)
Cincinnati,
OhioEPALaboratory
0.68Runoff for 95th Percentile Rainfall Event (in)
0.8 to 1.3Bioretention estimated runoff capture (inches)
1.4595th Percentile Rainfall Event (in)
51%Estimated Imperviousness (%)
19Total Area (acres)
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GI at Watershed LevelSmart Growth (Richards, EPA)
10,000 houses on
10,000 acres
Site: 20% impervious
Watershed: 20%impervious
10,000 houses on
2,500 acres
Site: 38% impervious
Watershed: 9.5%impervious
10,000 houses on
1,250 acres
Site: 65% impervious
Watershed: 8.1%impervious
The lower density scenario creates more run-off and consumes 2/3
more land than the higher density scenario.
(1 unit/acre) (4 units/acre) (8 units/acre)
Preserve Critical Land Areas
Preserve large, continuous areas of open space;
Preserve sensitive ecological areas
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Washington DC Greening Analysis
Casey Trees Study
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M
M
M
M
M
Lower Density ZoningLowerDensityZoning
Arlington, VA-- Smart growth preserves green space
Low-End High-EndResult Scenario Scenario
Runoff Reduction 10% 26%
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Ecological Impacts
Total Impervious Area and Trees vs IBI
M.Alberti , et al, (October 2007), The impact of urban patterns on aquatic ecosystems:
An empirical analysis in Puget lowland sub-basins , Landscape and Urban Planning,
Before: Stream RestorationSpring Creek, Spencer, WV
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After: Stream RestorationSpring Creek, Spencer, WV
Rain Garden, Martinsburg, WV
AcknowledgementsSteve Wise, Center for Neighborhood Development
Jenny Molloy and Lynn Richards, EPA