the future of stormwater management in south australia
TRANSCRIPT
The Future of Stormwater
Management in South
Australia, Policy or Local
Leaders?
Simon Beecham
Professor Sustainable Water Resources Engineering
Head of School of Natural and Built Environments
University of South Australia
Presentation Outline1. Water Sensitive Urban Design (WSUD)
2. WSU4D
3. Permeable pavements with underlying storage
• Quantifying security of supply
• Quantifying flood control benefits
4. A sustainable future
• UHI and embodied carbon
• Examples from around the world
Where are we now?
Water Sensitive Urban Design in Adelaide
• Recent WSUD initiatives
in South Australia:
– WSUD Framework
– WSUD Technical
Documents
– WSUD Better
Development Plan
policies
What is WSUD?
WSUD SystemsNon-vegetated Systems
Roofwater Harvesting Systems
• Conventional
• Siphonic
Rainwater tanks
Permeable pavements
Managed aquifer recharge
Vegetated Systems
Large-scale systems
• Wetlands
• Ponds
Small-scale systems
• Bioretention basins
• Biofiltration swales
Integrated Systems
• Permeable pavement draining to biofiltration swale
draining to wetland
WSU4Dbiodiversity enhancement
floodinghydraulic control
aesthetics (landscaping provides community involvement and social activities)
pollutantcontrol
Pavement Reuse Concept
0
20
40
60
80
100
120
1 2 24 72 144
Time (hrs)
(mg
/L)
Control
Calcite
Dolomite
Change in alkalinity of stored water
0
0.2
0.4
0.6
0.8
1
1 2 24 72 144
Time (hrs)
(mg
//L
)
Change in dissolved zinc in stored water
Rainwater Tanks
Permeable Pavements
Pavers
Bedding Course
Base Course
Geofabric
80mm pavers
50mm of 5mm
gravel
400mm of 20mm
gravel
Plastic liner
geofabric
Pavement Excavation
Excavation ~
$500
Perforated Pipe for Retrieving
Harvested Stormwater
Liner ~ $400
Gravel ~
$260 to $700
Completed UniSA Prototype Facility
Pavers ~ $500
Bedding gravel ~
$200
Geofab ~$30
Completed UniSA Prototype
Facility
Total materials cost:
$2,200
per car space
PERMAPAVE Design Software
Coupled with a Rainwater Garden
Monitoring
box
Solar panels
Battery
Permeablepavement withunderlyingstorage
Irrigation
pipe
Submersible pump
Moisture
sensors
Rainwater
garden
Planting
Solar Pump
CMAA Permeable Paving Workshop Adelaide
July/August 2014
• Application of permeable paving
– Overview of permeable pavement systems in Australia and overseas
– Examples from USA, Austria, South Africa and Australia
• Design of permeable pavements
– Design objectives, including WSUD
– Design life
– Cross-section selection
– Water infiltration and treatment
– Stormwater management and flood mitigation
– Water quality, harvesting and reuse
– Structural Design
• Maintenance of permeable paving
– Types of maintenance
– Frequency of maintenance
– Design for no maintenance
• Performance of permeable pavements
– Structural testing results
– Hydraulic testing results (field studies and laboratory experiments)
– Water quality testing results
Designing for Climate Change
Heat Island Effects
• Heat island is a phenomenon whereby air temperature in a city
is higher than in the suburbs or peri-urban areas
o Sensible heat flux warms the atmosphere
o CBD areas increase sensible heat flux from buildings
o Decrease of latent heat flux from natural catchments
• Need to quantify
o Surface and internal temperatures
o Conductive heat flux
o Net radiation
o Solar reflection (albedo)
Pavement
type
Max surface
temperature
(˚C)
PICP 40
Asphalt 58
Shackel (2008)
Embodied Carbon in Permeable Pavers
• UK inventory of carbon and energy (v1.6e, 2009) applied on a 1600m2 PICP (Knapton, 2008)
• 25% saving in CO2 emissions when installing a permeable pavement in lieu of a conventional impermeable pavement
• Typical tree may capture 20kg of CO2 pa or 1 tonne over a fifty year lifespan
• 1 tree per 11m2 of PICP for carbon neutral paving
Pavement type Tonnes CO2
Impermeable pavements 144
Underground drainage provision 47
Total 191
PICP 146
Market Development
• Europe
– Mid 80s Germany, Austria
– Mid 90s Belgium, The Netherlands etc
– 2000s UK
• SUDS – Sustainable Drainage Systems
• National Government Approach
• In line with the European Water Framework Directive
– Top Down – driven by legislation
• USA
– 1990s: EPA mandated to control stormwater runoff
– Low Impact Development Centre
– US Green Building Council
– Centre for Watershed Protection
– LEED – Leadership in Energy and Environmental Design to manage runoff
– EPA established design permits and best management practices – infiltration
practices emerged as a major focus
Australian Market
• Bottom up approach – no regulation or national
guidance
• Research into PICP began in early 90s
• Routine installation of PICPs introduced in late 90s
– Market approach project x project basis
– including prestigious projects such as the Sydney Olympic
Precinct – largest landscaping project ever undertaken in
Southern hemisphere
• Only site tested to receive routine maintenance although only a
small street sweeper
• Low infiltration results were due to locations being over buried
services
Vienna Football Stadium
• Bus and car park at PraterStadium, Vienna
• Installed by machine in 1990
• area of 39,000 m2
Shackel, B., Beecham, S., Pezzaniti, D. and Myers, B. (2008), Design of
Permeable Pavements for Australian Conditions, 23rd ARRB Conference,
Adelaide, Australia
Chigago White Sox
Baseball Stadium Car Park• EDI designed Lot L at U.S. Cellular
Field, home of the Chigago White
Sox baseball team
• Converted a 2.43 ha industrial site
into a fully permeable parking facility
• At the time of construction (April
2008) it was believed to be the
largest permeable paving parking lot
in the U.S.
• Permeable system allows for the
retention of a 100-year storm event
on site, which helps alleviate
overloading the existing combined
sewer system
• Parking system was constructed at
an elevation that allowed an
engineered barrier to be placed
above the existing Brownfield
contaminated site
Chigago White Sox
Baseball Stadium Car Park• 100-mm-thick L-shaped Eco-Optiloc
• 10mm voids between each stone
• 3.5 cm deep bedding layer of 3 to 6
mm gravel
• 350mm deep basecourse, comprising
a mixture of 75mm diameter recycled
concrete and 20-25mm limestone
gravel
• 527,616 permeable pavers were
installed at a rate of 1,900 m2 a day
www.envdesigni.com/us-cellular-field-lot-l/
Chigago White Sox
Baseball Stadium Car Park• Designed to meet the 2008 City
of Chicago Stormwater
Management Ordinance
• 2,271 kL of water storage
(equivalent to a 100-year ARI
rainfall event).
• Equates to a void ratio of es =
0.27 (note: graded basecourse)
• Total project cost AUD $3.8m
which was approximately
$432,000 less expensive that a
conventional asphalt car park
with a pit and pipe drainage
system
• Equates to AUD $155/m2 total
costwww.envdesigni.com/us-cellular-field-lot-l/
Morton Arboretum in Lisle, Illinois
• 500 lot car park constructed
in 2003 for arboretum that
features 4,117 kinds of trees,
shrubs and other plants from
around the world
• 1.6 ha permeable paving with
additional 3,230 m2 of regular
interlocking concrete
pavement
Morton Arboretum in Lisle, Illinois
• 80mm pavers with 3 to 6 mm blue
mahogany granite jointing gravel and
40 mm depth of bedding material
(Illinois DOT CA-16, 1 to 10 mm
crushed stone )
• Basecourse depth of 150 mm of
Illinois DOT CA-7 (5 to 25 mm,
ASTM No. 57) crushed stone base
overlying a further 300 mm of Illinois
DOT CA-1 (25 to 63 mm, ASTM No.
57) crushed stone sub-base
• Subgrade was native clay soil
• Biofiltration swale includes native
grasses and black-eyed Susans to
help filter runoff before it enters
Meadow Lake and eventually the
DuPage River
Morton Arboretum in Lisle, Illinois
• Initial design and construct cost was
AUD $1.05m
• Full life-cycle cost comparison showed
that it was less expensive than an
equivalent asphalt car park over 25 year
lifespan
• Importantly, annual maintenance costs
were estimated at AUD $4,955, including
vacuum cleaning and paver repairs
(although no cleaning was actually done
for first 6 years)
• Equivalent average annual maintenance
costs for asphalt surface plus pit and
pipes was estimated at AUD $29,397
including patching, crack filling and
cleaning www.icpi.org
• In both the USA and
Brazil permeable
paving has been
successfully used in
container handling
areas and ports
subject to high
wheel loads
• e.g. Knapton and
Cook (2000)
Knapton J and Cook I D. (2000). Permeable Paving for a New Container
Handling Area at Santos Container Port, Brazil. Proc.6th Int. Conf. on
Concrete Block Paving, Tokyo
Howland Hook Marine Terminal
Container Yard, Staten Island, NY, USA
Howland Hook Marine Terminal
Container Yard, Staten Island, NY, USA
• Expanded existing container yard by
approximately 5 ha with 0.1 ha of
permeable interlocking concrete block
pavement
• ICBP selected for resistance to container
loads, particularly damage at corner
castings, and because of the potential
subgrade problems (due to presence of
gypsum)
• 20-year service life of top picks and lift
trucks and 4-high container stacks
• dual wheel axle loads of 97,500 kg
excluding dynamic forces
• stacked containers can result in point
loads of up to 23,000 kg at each corner
casting at the bottom container
Howland Hook Marine Terminal
Container Yard, Staten Island, NY, USA
The Reeds, Fairlands, Johannesburg• First system was constructed in 2007 as an
affordable housing project
• Some 89,000 square units and 94,000
rectangular units were supplied to cover an
area of 4,320m²
• 500mm of top soil was removed and the
exposed surface was then covered with an
SABS approved BIDIM A5 geotextile
• Rockfill comprising 160mm stone, 500mm
deep formed the next layer followed by a
second layer of geotextile membrane
• Once compacted, the rockfill was covered
with 80mm of coarse washed river sand and
this in turn was compacted. To this was
added another 20mm of washed river sand
for bedding. The same sand was also used
for jointing. www. cma.org.za
Permeable Concrete Block Paving
Witwatersrand University
Two car park areas
13,000m2
Largest permeable paving project in South Africa
60mm pavers
Durban North Kensington Drive
Durban North Kensington Drive
• Shopping mall
• 480m2 of paving harvests both roof and pavement runoff
• Includes 500mm concrete detention tank under paving system
• Designed by Arups
Smith Street, Manly
• An Australian
retrofit (in 2001) of
permeable paving
to a residential
street originally
constructed
around 1900
• Ecoloc paversShackel, B., Beecham, S., Pezzaniti, D. and Myers, B. (2008), Design of
Permeable Pavements for Australian Conditions, 23rd ARRB Conference,
Adelaide, Australia
PICP in Kiama, NSW, Australia
• Constructed in
1997
Shackel, B., Beecham, S., Pezzaniti, D. and Myers, B. (2008), Design of
Permeable Pavements for Australian Conditions, 23rd ARRB Conference,
Adelaide, Australia
• Constructed in 1998
• Installed over dense-graded
20mm granular basecourse
(DGB20)
Lane 30 Grange, SA
• Rear access service laneway, constructed in 2010
• 2500m2 effective contributing area
• Graded permeable basecoursematerial with a void ratio of 15%
Lane 30 Grange, SA
Shackel, B., Beecham, S., Pezzaniti, D. and Myers, B. (2008), Design of
Permeable Pavements for Australian Conditions, 23rd ARRB Conference,
Adelaide, Australia
GeotextileTransverse barriers
(impermeable liner or
equivalent) to promote full
infiltration /storage and
prevent ponding at low
point.
• Hydraulic conductivity of subgrade = 1.0 x 10-4 m/s (results from falling head test, UniSA report, dated 14 May 2009)
• All storm events for the 5yr ARI shall be managed by the permeable pavement section
Conclusions
• traditional approaches to water resource management will present major constraints to new development
• this is already occurring and will be exacerbated by climate change
• future lies in multi-functional landuse
o flood storage, WSUD, social amenity all in the same land corridors
o this will release flood fringe areas and enhance urban ecology
Simon Beecham
Head of School of Natural and Built Environments
University of South Australia
http://people.unisa.edu.au/simon.beecham