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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

                                                                       Department of
      Fairfax                                                          Public Works
      County,                                                               and
                                                                       Environmental
      Virginia                       Wetland                             Services
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   2
Why are we here ?

 To discuss restoration of
  the “Harford” stream
  with the community

 This area listed for
  restoration in the Pohick      PC9257
  Creek Watershed
  Management Plan
                                    PC9258
    - Project Number: PC9257
    - Project Number: PC9258




                               Wetland       3
Why are we here ?
The stream is eroding.




3.5’ headcut                Eroded channel, vertical banks

The storm-water pond and emergency spillway need repair.




Significant deposition in stormwater pond    Emergency spillway failure

                                   Wetland                                4
Why are we here ?
• Erosion results in poor water         • The Environmental Protection
  quality; high levels of:                Agency Chesapeake Bay TMDL
    – Total Suspended Solids (TSS)        Plan Requires Fairfax County
    – Total Nitrogen (TN)                 pollutant reductions
    – Total Phosphorous (TP)


    Poor water quality                                   Good water quality




                                     Wetland                                  5
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                                     6
The urban watershed problem




         Source: The Federal Interagency Stream Restoration Working Group

              Wetland                                                       7
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                 8
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                                     9
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.
                                                    Flow Rate vs Drainage Area
     • Rock structures – using native diabase rock
     • Reinforced bed
     • Heavy planting densities – native vegetation only
                                         Reston

Snakeden Branch – Reach 3                         McLean Place (after 4.5 yrs)
                            Flow Rate (cfs)
(after 16 months)

                                                                   Rural




                                                        Drainage Area (sq mi)

                                              Wetland                            10
Stream Reinforcement
Step Pools                    Cross Vanes




Reinforced Bed                Native Vegetation




                         Wetland                  11
Restoration approaches
  Priority 1 Restoration - Raise stream to reconnect with the floodplain.


                                                      Fewer trees removed


                                                      Balanced cut and fill volumes
                                                      result in less waste

                            Width of disturbance



Before                                      After




               Snakeden Branch Reach 2 – Priority 1 Restoration

                                  Wetland                                             12
Restoration approaches
Priority 2 Restoration – Excavate floodplain at lower elevation.


                                                 Many trees removed



                                                 Large cut volumes result in waste material


             Width of disturbance




                                      Priority 3 Restoration – Confined stream valleys.




                                    Wetland                                         13
Restoration approaches
                          Priority 4 Restoration – Stabilize in-place




Snakeden Branch Reach 2
(2003, by others) –
Long-term stability not
achieved using this
approach.




                                            Wetland                     14
Harford stream: Historic Conditions




                               1937

               Wetland                15
Harford stream: Historic Conditions




             1971                     1972




               Wetland                16
Harford stream: Historic Conditions




             1979                     1998




               Wetland                17
Harford stream: Historic Conditions




                              2012

               Wetland                18
Harford stream: Existing Conditions

                              • Drainage Area
                                  121.1 acres

                              • Imperviousness
                                  37%




               Wetland                    19
Harford stream: Existing Conditions

                           Culvert and rip rap channel




               Wetland                         20
Harford stream: Existing Conditions

                              Sediment deposition




               Wetland                    21
Harford stream: Existing Conditions

                         Riprap and deposition along paved path




               Wetland                                  22
Harford stream: Existing Conditions


                                      3.5’ head cut




               Wetland                      23
Harford stream: Existing Conditions

                             Debris, incised channel




               Wetland                       24
Harford stream: Existing Conditions


                                  Existing bridge




               Wetland                    25
Harford stream: Existing Conditions

                               Exposed utility lines




               Wetland                       26
Harford stream: Existing Conditions
           • Eroded channel approximately 5-ft deep
           • Listed for restoration in watershed plan (PC9258)
                                       Outfall from Dahlgreen Place




                   Wetland                                       27
Harford stream: Existing Conditions


                                 Incised channel




               Wetland                   28
Harford stream: Existing Conditions

                              Culvert at Guinea Rd.




               Wetland                      29
Harford stream: Existing Conditions


                         Heavy deposition in sediment forebay




               Wetland                                30
Harford stream: Existing Conditions


                  Emergency spillway showing signs of failure




               Wetland                                31
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                          32
Plan Development Process

• Pre-design Meeting (Tonight)
• Data Collection
• Stream Restoration Design
  Process
• Concept Plan Development
• Preliminary Design
• Final Design
• Pre-construction Review
• Construction


                              Wetland       33
Data collection

• 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




                        Wetland                    34
community Involvement In the Plan
              Development Process

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




                                 Wetland                        35
Stream restoration design process
                     Determine Bankfull Width
                     and Bankfull Area to convey
                           current flows.
THE DESIGN PROCESS




                       Apply Bankfull Width to
                     reference ranges of sinuosity
                          and meander radii.

                         Layout initial design
                     alignment (minimize impact
                      to infrastructure and trees)

                           Citizen Meeting
                                                               Citizen Meeting
                      Revise restoration design
                             and access                         Final Design
                       (based on citizen input)

                                                     Wetland                     36
Stream restoration design process
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.

                                            Wetland                                 37
Stream restoration design process
                             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
Incised stream                 of replacement plantings
                                 – Mosquito population control via predator habitat
                                 – Dense streambank planting will provide shade, reduce water
  Lower water table                temperatures, increase oxygenation, increase fish survivability
                                 – Dragonfly larva molting access via heavily planted streambank with
Restored (raised) stream
                                   shallower slope
                             • Canopy loss will close as remaining trees adjust and react to increased
                               sunlight, growing to fill in openings
  Higher water table


                           Fewer trees cut = lower restoration cost
                           • Tree-climbing removal method vs. traditional forestry timbering
                             (minimize impacts to neighboring trees) is expensive.


                                              Wetland                                           38
Examples - Snakeden Reach 2




   Pre-Construction                      Construction




  Post-Construction        5 Months After Construction

                 Wetland                        39
Examples - Snakeden Reach 3




  Pre-Construction




 Post-Construction             15 Months After Construction

                     Wetland                         40
Examples – Snakeden reach 13




   Pre-Construction




                               Post-Construction

                 Wetland                  41
Examples – Big Rocky Run Tributary




                    Pre-Construction                     Construction




Post Construction   Post-Construction        After plant establishment

                                   Wetland                      42
Examples - Sheffield




                               Construction




Pre-Construction           Post-Construction

               Wetland                43
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              44
PLANTING - Riparian Seed Mix
• Applied at a rate of 125 lbs/acre
• Custom mix
• Consists of native species found in a healthy, diverse NOVA ecosystem:

    • Tree Species                            • Shrub Species
        •   Musclewood                              •   Witch Hazel
        •   Black Gum                               •   Winterberry
        •   American Sycamore                       •   Southern Arrow Wood
        •   Red Maple                               •   Northern Spicebush
        •   Eastern Redbud                          •   Canadian Serviceberry
        •   Flowering Dogwood                       •   Black Chokeberry
                                                    •   Black-Haw
    • Forbs                                   • Grass Species
        •   Oxeye Sunflower                         •   Squarrose Sedge
        •   Joe-Pye Weed                            •   Riverbank Wild Rye
        •   Grass Leaved Goldenrod                  •   Foxtail Millet
        •   PLUS 24 additional species!             •   PLUS 8 additional species!


                                          Wetland                                    45
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
                                                                  Red-shouldered Hawk
• All species benefit from the “edge
  effect”

• Restored stream allows detrital
  input to be processed, thus                 Cottontail Rabbit
  increasing stream health and
  function
                                                                       Orchard Oriole



                                    Wetland                                             46
technical review

• Fairfax County Department of Public Works and Environmental Services

• US Army Corps of Engineers

• Virginia Department of Environmental Quality




                                Wetland                              47
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   48
Questions?
Wetland                49
For more information

• 703-324-5500, TTY 711
• SWPDMail@fairfaxcounty.gov
• www.fairfaxcounty.gov/dpwes/stormwater
• A Fairfax County, Virginia
publication, April 2013




                   Wetland                 50

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Harford Community Stream Restoration 2013

  • 1. 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 Department of Fairfax Public Works County, and Environmental Virginia Wetland Services
  • 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 2
  • 3. Why are we here ?  To discuss restoration of the “Harford” stream with the community  This area listed for restoration in the Pohick PC9257 Creek Watershed Management Plan PC9258 - Project Number: PC9257 - Project Number: PC9258 Wetland 3
  • 4. Why are we here ? The stream is eroding. 3.5’ headcut Eroded channel, vertical banks The storm-water pond and emergency spillway need repair. Significant deposition in stormwater pond Emergency spillway failure Wetland 4
  • 5. Why are we here ? • Erosion results in poor water • The Environmental Protection quality; high levels of: Agency Chesapeake Bay TMDL – Total Suspended Solids (TSS) Plan Requires Fairfax County – Total Nitrogen (TN) pollutant reductions – Total Phosphorous (TP) Poor water quality Good water quality Wetland 5
  • 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 6
  • 7. The urban watershed problem Source: The Federal Interagency Stream Restoration Working Group Wetland 7
  • 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 8
  • 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 9
  • 10. 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. Flow Rate vs Drainage Area • Rock structures – using native diabase rock • Reinforced bed • Heavy planting densities – native vegetation only Reston Snakeden Branch – Reach 3 McLean Place (after 4.5 yrs) Flow Rate (cfs) (after 16 months) Rural Drainage Area (sq mi) Wetland 10
  • 11. Stream Reinforcement Step Pools Cross Vanes Reinforced Bed Native Vegetation Wetland 11
  • 12. Restoration approaches Priority 1 Restoration - Raise stream to reconnect with the floodplain. Fewer trees removed Balanced cut and fill volumes result in less waste Width of disturbance Before After Snakeden Branch Reach 2 – Priority 1 Restoration Wetland 12
  • 13. Restoration approaches Priority 2 Restoration – Excavate floodplain at lower elevation. Many trees removed Large cut volumes result in waste material Width of disturbance Priority 3 Restoration – Confined stream valleys. Wetland 13
  • 14. Restoration approaches Priority 4 Restoration – Stabilize in-place Snakeden Branch Reach 2 (2003, by others) – Long-term stability not achieved using this approach. Wetland 14
  • 15. Harford stream: Historic Conditions 1937 Wetland 15
  • 16. Harford stream: Historic Conditions 1971 1972 Wetland 16
  • 17. Harford stream: Historic Conditions 1979 1998 Wetland 17
  • 18. Harford stream: Historic Conditions 2012 Wetland 18
  • 19. Harford stream: Existing Conditions • Drainage Area 121.1 acres • Imperviousness 37% Wetland 19
  • 20. Harford stream: Existing Conditions Culvert and rip rap channel Wetland 20
  • 21. Harford stream: Existing Conditions Sediment deposition Wetland 21
  • 22. Harford stream: Existing Conditions Riprap and deposition along paved path Wetland 22
  • 23. Harford stream: Existing Conditions 3.5’ head cut Wetland 23
  • 24. Harford stream: Existing Conditions Debris, incised channel Wetland 24
  • 25. Harford stream: Existing Conditions Existing bridge Wetland 25
  • 26. Harford stream: Existing Conditions Exposed utility lines Wetland 26
  • 27. Harford stream: Existing Conditions • Eroded channel approximately 5-ft deep • Listed for restoration in watershed plan (PC9258) Outfall from Dahlgreen Place Wetland 27
  • 28. Harford stream: Existing Conditions Incised channel Wetland 28
  • 29. Harford stream: Existing Conditions Culvert at Guinea Rd. Wetland 29
  • 30. Harford stream: Existing Conditions Heavy deposition in sediment forebay Wetland 30
  • 31. Harford stream: Existing Conditions Emergency spillway showing signs of failure Wetland 31
  • 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 32
  • 33. Plan Development Process • Pre-design Meeting (Tonight) • Data Collection • Stream Restoration Design Process • Concept Plan Development • Preliminary Design • Final Design • Pre-construction Review • Construction Wetland 33
  • 34. Data collection • 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 Wetland 34
  • 35. community Involvement In the Plan Development Process 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 Wetland 35
  • 36. Stream restoration design process Determine Bankfull Width and Bankfull Area to convey current flows. THE DESIGN PROCESS Apply Bankfull Width to reference ranges of sinuosity and meander radii. Layout initial design alignment (minimize impact to infrastructure and trees) Citizen Meeting Citizen Meeting Revise restoration design and access Final Design (based on citizen input) Wetland 36
  • 37. Stream restoration design process 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. Wetland 37
  • 38. Stream restoration design process 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 Incised stream of replacement plantings – Mosquito population control via predator habitat – Dense streambank planting will provide shade, reduce water Lower water table temperatures, increase oxygenation, increase fish survivability – Dragonfly larva molting access via heavily planted streambank with Restored (raised) stream shallower slope • Canopy loss will close as remaining trees adjust and react to increased sunlight, growing to fill in openings Higher water table Fewer trees cut = lower restoration cost • Tree-climbing removal method vs. traditional forestry timbering (minimize impacts to neighboring trees) is expensive. Wetland 38
  • 39. Examples - Snakeden Reach 2 Pre-Construction Construction Post-Construction 5 Months After Construction Wetland 39
  • 40. Examples - Snakeden Reach 3 Pre-Construction Post-Construction 15 Months After Construction Wetland 40
  • 41. Examples – Snakeden reach 13 Pre-Construction Post-Construction Wetland 41
  • 42. Examples – Big Rocky Run Tributary Pre-Construction Construction Post Construction Post-Construction After plant establishment Wetland 42
  • 43. Examples - Sheffield Construction Pre-Construction Post-Construction Wetland 43
  • 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 44
  • 45. PLANTING - Riparian Seed Mix • Applied at a rate of 125 lbs/acre • Custom mix • Consists of native species found in a healthy, diverse NOVA ecosystem: • Tree Species • Shrub Species • Musclewood • Witch Hazel • Black Gum • Winterberry • American Sycamore • Southern Arrow Wood • Red Maple • Northern Spicebush • Eastern Redbud • Canadian Serviceberry • Flowering Dogwood • Black Chokeberry • Black-Haw • Forbs • Grass Species • Oxeye Sunflower • Squarrose Sedge • Joe-Pye Weed • Riverbank Wild Rye • Grass Leaved Goldenrod • Foxtail Millet • PLUS 24 additional species! • PLUS 8 additional species! Wetland 45
  • 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 Red-shouldered Hawk • All species benefit from the “edge effect” • Restored stream allows detrital input to be processed, thus Cottontail Rabbit increasing stream health and function Orchard Oriole Wetland 46
  • 47. technical review • Fairfax County Department of Public Works and Environmental Services • US Army Corps of Engineers • Virginia Department of Environmental Quality Wetland 47
  • 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 48
  • 50. For more information • 703-324-5500, TTY 711 • SWPDMail@fairfaxcounty.gov • www.fairfaxcounty.gov/dpwes/stormwater • A Fairfax County, Virginia publication, April 2013 Wetland 50