harford community stream restoration 2013
DESCRIPTION
Harford Community Stream Restoration 2013TRANSCRIPT
Wetland
Stream Restoration and The Upper Pohick creek
Watershed
Presented by Michael S. Rolband
P.E., P.W.S., P.W.D.
Wetland Studies and Solutions, Inc.
5300 Wellington Branch Drive . Suite 100 . Gainesville . Virginia 20155
www.wetlandstudies.com
Fairfax
County,
Virginia
Department of
Public Works
and
Environmental
Services
Wetland 2
Wetland Studies
and Solutions, Inc.
• Natural & Cultural Resource consulting firm
• 75 Staff
– Archeology, Engineering, Environmental Science & Ecology, Environmental Technology, Compliance, GIS, Regulatory, Surveying, & Wildlife Biology
Wetland 3
Why are we here ?
To discuss restoration of the “Harford” stream with the community
This area listed for restoration in the Pohick Creek Watershed Management Plan
- Project Number: PC9257
- Project Number: PC9258
PC9257
PC9258
Wetland
Why are we here ?
4
The stream is eroding.
The storm-water pond and emergency spillway need repair.
3.5’ headcut Eroded channel, vertical banks
Significant deposition in stormwater pond Emergency spillway failure
Wetland
• The Environmental Protection Agency Chesapeake Bay TMDL Plan Requires Fairfax County pollutant reductions
5
Why are we here ?
• Erosion results in poor water quality; high levels of:
– Total Suspended Solids (TSS)
– Total Nitrogen (TN)
– Total Phosphorous (TP)
Poor water quality Good water quality
Wetland 6
Why are we here ?
• What has caused the erosion?
• What can be done to fix the erosion and prevent future issues?
Dahlgreen Pl tributary (PC9258)
Wetland 7
The urban watershed problem
Source: The Federal Interagency Stream Restoration Working Group
Wetland 8
Why restore ?
Reconnect to the existing floodplain to:
• Slow velocities
• Increase evapotranspiration
• Remove pollutants (TP, TN, and TSS)
• Improve riparian habitat
• Restore groundwater levels
After planting - 1999
Before restoration After restoration
Wetland 9
Design Methodology for Urban Streams
- Natural Channel Evolution -
Evolutionary process considers the channel’s incision, bank stability, & sedimentation load (aggrading or degrading)
Severe Poor Marginal Suboptimal Optimal
Severe Channel Condition Optimal Channel Condition
South Lakes High School Ellanore Lawrence Park
Wetland 10
Rural
Reston
Flo
w R
ate
(cfs
)
Drainage Area (sq mi)
Flow Rate vs Drainage Area
Urban Stream - Design Realities
1. Significantly more flow than rural streams.
2. Significantly more “bankfull” events than in rural watersheds.
3. Given site constraints, reinforcement is necessary.
• Rock structures – using native diabase rock
• Reinforced bed
• Heavy planting densities – native vegetation only
McLean Place (after 4.5 yrs) Snakeden Branch – Reach 3
(after 16 months)
Wetland 11
Stream Reinforcement
Reinforced Bed
Step Pools
Native Vegetation
Cross Vanes
Wetland 12
Restoration approaches
Priority 1 Restoration - Raise stream to reconnect with the floodplain.
Fewer trees removed
Width of disturbance
Balanced cut and fill volumes
result in less waste
Snakeden Branch Reach 2 – Priority 1 Restoration
Before After
Wetland 13
Restoration approaches
Priority 2 Restoration – Excavate floodplain at lower elevation.
Width of disturbance
Large cut volumes result in waste material
Many trees removed
Priority 3 Restoration – Confined stream valleys.
Wetland 14
Snakeden Branch Reach 2
(2003, by others) –
Long-term stability not
achieved using this
approach.
Priority 4 Restoration – Stabilize in-place
Restoration approaches
Wetland 15
Harford stream: Historic Conditions
1937
Wetland 16
1971 1972
Harford stream: Historic Conditions
Wetland 17
1979 1998
Harford stream: Historic Conditions
Wetland 18
2012
Harford stream: Historic Conditions
Wetland 19
Harford stream: Existing Conditions
• Drainage Area
121.1 acres
• Imperviousness
37%
Wetland
Culvert and rip rap channel
20
Harford stream: Existing Conditions
Wetland 21
Sediment deposition
Harford stream: Existing Conditions
Wetland 22
Riprap and deposition along paved path
Harford stream: Existing Conditions
Wetland 23
3.5’ head cut
Harford stream: Existing Conditions
Wetland 24
Debris, incised channel
Harford stream: Existing Conditions
Wetland 25
Existing bridge
Harford stream: Existing Conditions
Wetland 26
Exposed utility lines
Harford stream: Existing Conditions
Wetland 27
• Eroded channel approximately 5-ft deep
• Listed for restoration in watershed plan (PC9258)
Outfall from Dahlgreen Place
Harford stream: Existing Conditions
Wetland 28
Incised channel
Harford stream: Existing Conditions
Wetland
Culvert at Guinea Rd.
29
Harford stream: Existing Conditions
Wetland 30
Heavy deposition in sediment forebay
Harford stream: Existing Conditions
Wetland 31
Emergency spillway showing signs of failure
Harford stream: Existing Conditions
Wetland 32
What does fairfax county need from your
association ?
• Guidance from the community regarding:
• The desire for additional project meetings or stream walks
• Details of the Community Association approval process
• An easement to allow the County and its contractors to:
• Survey and develop restoration plans
• Restore the stream
• Maintain the stream
Wetland 33
• Pre-design Meeting (Tonight)
• Data Collection
• Stream Restoration Design Process
• Concept Plan Development
• Preliminary Design
• Final Design
• Pre-construction Review
• Construction
Plan Development Process
Wetland 34
• Obtain topography
• Survey locate & tag trees (> 8” dbh)
• Survey channel profile and cross-sections
• Sediment sampling
• Perform wetland delineations and obtain Jurisdictional Determinations (JD’s) from U.S. Army Corps of Engineers
Data collection
Wetland 35
Objective – Partnership between Fairfax County staff and the Lake Braddock Community
• Establish community representative(s) to coordinate with County staff as the project progresses
• Community involvement at all levels of the plan development process (Concept, Preliminary, Final Design, and Construction)
– Plan review, discussion, and feedback
community Involvement In the Plan
Development Process
Wetland 36
Stream restoration design process T
HE
DE
SIG
N P
RO
CE
SS
Determine Bankfull Width
and Bankfull Area to convey
current flows.
Apply Bankfull Width to
reference ranges of sinuosity
and meander radii.
Layout initial design
alignment (minimize impact
to infrastructure and trees)
Revise restoration design
and access
(based on citizen input)
Final Design
Citizen Meeting Citizen Meeting
Wetland 37
Tree impact considerations
Ecological / Habitat Value
• Size / Diameter
• Higher - Climax species: Oaks, Hickory, Holly (mast
producers, long-lived).
• Lower – Early successional species: Maples, Poplar
(fast-growing, short-lived).
Existing Condition
• Undercut by stream, high proportion of exposed
roots, short life expectancy
• Dead, dying, diseased, or damaged trees that pose a human safety hazard
• Impacting or pending impact to infrastructure (utilities, roads, trails, etc.)
Proposed Condition
• Drip line heavily impacted during restoration, minimal chance of survival, AND
• Human safety hazard to trails, houses, bridges, etc.
Stream restoration design process
Wetland 38
Short term impact for long term benefit
• Cleared trees “recycled” as in-stream habitat, grade control, wood-chip
trails, habitat “brush” piles, firewood
• Restoration raises the water table, (raises stream bed) which increases
stream access to floodplain and nutrient delivery to roots.
• Healthier ecosystem will develop with the density and species variety
of replacement plantings
– Mosquito population control via predator habitat
– Dense streambank planting will provide shade, reduce water
temperatures, increase oxygenation, increase fish survivability
– Dragonfly larva molting access via heavily planted streambank with
shallower slope
• Canopy loss will close as remaining trees adjust and react to increased
sunlight, growing to fill in openings
Fewer trees cut = lower restoration cost • Tree-climbing removal method vs. traditional forestry timbering
(minimize impacts to neighboring trees) is expensive.
Lower water table
Higher water table
Incised stream
Restored (raised) stream
Stream restoration design process
Wetland 39
Pre-Construction Construction
Post-Construction 5 Months After Construction
Examples - Snakeden Reach 2
Wetland
Examples - Snakeden Reach 3
40
Pre-Construction
15 Months After Construction Post-Construction
Wetland 41
Examples – Snakeden reach 13
Post-Construction
Pre-Construction
Wetland 42
Pre-Construction Construction
Post Construction After plant establishment
Examples – Big Rocky Run Tributary
Post-Construction
Wetland
Examples - Sheffield
43
Pre-Construction Post-Construction
Construction
Wetland 44
PLANTING – TREES & SHRUBS
Split into 2 planting zones:
- Riparian
- 1 gallon containers (planted at 640 plants/acre)
- both trees & shrubs
- Streamside
- live stakes/tubelings (planted 1ft o.c.)
- shrubs (planted 3 ft o.c.)
Tree Species: Pin Oak, Willow Oak, White Oak, Swamp White
Oak, Northern Red Oak, Sweet Gum, Black Gum, River
Birch, Sycamore, Red Maple, Box Elder, and Black Willow.
Shrub Species: Silky Dogwood, Southern Arrowwood,
American Holly, Service-Berry, Black-Haw, Eastern Redbud,
Elderberry, Flowering Dogwood, and Brookside Alder,
Hazelnut, Northern Spicebush, Black-Haw, Winterberry.
Eastern Redbud
Wetland 45
PLANTING - Riparian Seed Mix
• Tree Species
• Musclewood
• Black Gum
• American Sycamore
• Red Maple
• Eastern Redbud
• Flowering Dogwood
• Forbs
• Oxeye Sunflower
• Joe-Pye Weed
• Grass Leaved Goldenrod
• PLUS 24 additional species!
• Shrub Species
• Witch Hazel
• Winterberry
• Southern Arrow Wood
• Northern Spicebush
• Canadian Serviceberry
• Black Chokeberry
• Black-Haw
• Grass Species
• Squarrose Sedge
• Riverbank Wild Rye
• Foxtail Millet
• PLUS 8 additional species!
• Applied at a rate of 125 lbs/acre
• Custom mix
• Consists of native species found in a healthy, diverse NOVA ecosystem:
Wetland 46
Greater Biodiversity
• Mature forest continues to provide habitat for raptors, woodpeckers, bats and deer
• Recently planted areas provide habitat for small mammals, song birds, fox and deer
• All species benefit from the “edge effect”
• Restored stream allows detrital input to be processed, thus increasing stream health and function
Orchard Oriole
Red-shouldered Hawk
Cottontail Rabbit
Wetland 47
technical review
• Fairfax County Department of Public Works and Environmental Services
• US Army Corps of Engineers
• Virginia Department of Environmental Quality
Wetland 48
Conclusion
1. The “Harford” tributary of the Pohick Creek Watershed is severely degraded due to urbanization – a situation made worse by inadequate stormwater management.
2. Fully restored streams will provide long-term stability, improved aesthetics, & greater open space usability.
3. Short-term construction disturbance will provide long-term societal and ecological benefits to a heavily used, urban stream valley network.
Wetland 49
Questions?
Wetland
For more information
• 703-324-5500, TTY 711
• www.fairfaxcounty.gov/dpwes/stormwater
• A Fairfax County, Virginia
publication, April 2013
50