Process based Design Criteria for Ecological...

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Processbased Design Criteria for Ecological Restoration 15th Annual UC Berkeley River Restoration Symposium Damion Ciotti U.S. Fish and Wildlife Service Jared McKee, Karen L. Pope, G. Mathias Kondolf, and Michael M. Pollock

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Page 1: Process based Design Criteria for Ecological Restorationriverlab.berkeley.edu/wp/wp-content/uploads/BerkeleySymposium_D… · Integrity of functional ecosystem Space + Energy + Materials

Process‐based Design Criteria for Ecological Restoration15th Annual UC Berkeley River Restoration Symposium

Damion CiottiU.S. Fish and Wildlife Service

Jared McKee, Karen L. Pope, G. Mathias Kondolf, and Michael M. Pollock

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Result in a net gain in fluvial process SPACE Capitalize on natural ENERGYUse geomorphically appropriate MATERIALSMeet habitat objectives over TIME

Space + Energy + Materials = Change/Time 

Design Criteria

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Integrity of constructed feature

Integrity of functional ecosystem

Space + Energy + Materials = Change/Time 

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Form‐based ConstructionWhat will the project accomplish? Stabilize a bank and channel

How will project be undertaken? Heavy equipment and rock

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Infrastructure Protection/Modification

Restoration Design

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Principles for Process‐based Restoration(Beechie et al, 2010): Address root causes of degradation Scale commensurate with problem

Standards for Ecological Restoration(Palmer et al, 2005):  Dynamic ecological endpoint  Restoration does not inflict lasting harm 

Process‐based StandardsTraditional Ecological Knowledge  Spiritual land ethic Working with disturbance regimes Bigger time and spatial scales

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1. Address source problems

2. Work with system recovery

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Result in a net gain in fluvial process SPACE Capitalize on natural ENERGYUse geomorphically appropriate MATERIALSMeet habitat objectives over TIME

Space + Energy + Materials = Change/Time 

Application of the Design Criteria

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Doty Ravine Stream Corridor

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Setting the Project Goal ‐ Dynamic End PointRiverine Ecosystem Theory

Riparian Zone, Flood pulse, Stage ZeroShifting Habitat Mosaic

(Ward et al., 2002;  Cluer and Thorne 2014)

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Space: Project actions increase the spatial extent of fluvial processes and connectivity lost due to human alterations

Applied Geomorphic Analysis: Connectivity, process space, source problems(Kondolf and Piegay 2003; Fryirs and Brierley 2016)

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Space Available process space 67 acres

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Space

Incision

Grazing

Oak Planting

Disconnections

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Space Starting Process Space 7 acresAvailable Process Space 67 acres

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Space Final project process space 57 acres

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Energy:  Project actions capitalize on natural energy within the system to do the work of restoration and minimize the use of external mechanical energy

Fluvial Energy (Flood pulse)Solar Energy (Primary production)Biological Energy (Beaver, willow, wolves)

Ecological EngineeringSelf design, energy efficiency, accelerate process, mimicry(HT Odum; Pollock et al., 2014; Wheaton et al. 2018)

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2 yr flood event = 21 backhoe days of energy 7.2 tons of carbon. (McKee et al. 2019 in review)

Energy

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Self‐system design

Year 2

Year 3

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Year 2 Year 3

Geomorphic Work Biological Work

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Materials: Do not over‐stabilize project elements or unnaturally constrain channel migration. (Native and geomorphically appropriate)

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Biological work

Time: Achieve habitat objectives over time via restored geomorphic and biologic processes

Recovery Trajectory

Geomorphic Work

Biological Work

Geomorphic work

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Time

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0

500

1000

1500

2000

Oct‐12 Oct‐13 Oct‐14 Oct‐15 Oct‐16 Nov‐17 Nov‐18 Nov‐19

10 yr flow

2 yr flow

Time Doty Ravine 2012‐2019

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0

500

1000

1500

2000

Oct‐12 Oct‐13 Oct‐14 Oct‐15 Oct‐16 Nov‐17 Nov‐18 Nov‐19

10 yr flow

2 yr flow

Time Doty Ravine 2012‐2019

Geomorphic Work

Biological Work

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0

500

1000

1500

2000

Oct‐12 Oct‐13 Oct‐14 Oct‐15 Oct‐16 Nov‐17 Nov‐18 Nov‐19

10 yr flow

2 yr flow

Time Doty Ravine 2012‐2019 Geomorphic Work

Biological Work

0.3 acre constructed wetland

Oak planting

Tree planting and constructed wetland $160,000

Beaver depredation ceased

Shallower water table

LeveeRemoval, BDAs and livestock management

Levee removal and beaver analogue dam building $58,000

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0

500

1000

1500

2000

Oct‐12 Oct‐13 Oct‐14 Oct‐15 Oct‐16 Nov‐17 Nov‐18 Nov‐19

10 yr flow

2 yr flow

Time Doty Ravine 2012‐2019 Geomorphic Work

Biological Work

0.3 acre constructed wetland

Oak planting

Tree planting and constructed wetland $160,000

Terrestrial79%

Stage 3‐420%

Constructed wetland

1%

2012‐2016

Beaver depredation ceased

Shallower water table

LeveeRemoval, BDAs and livestock management

Terrestrial57%Stage 3‐4

16%

Stage 027%

2017

Terrestrial25%

Stage 3‐46%

Stage 069%

2019

Terrestrial46%

Stage 3‐411%

Stage 043%

2018

Levee removal and beaver analogue dam building $58,000

Terrestrial

Stage 0

Stage 3

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Space

Energy

Materials

Time

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1. Kondolf, G.M., Piegay, H., 2003. Tools in fluvial geomorphology: problem statement and recent practice. In: Kondolf, G.M., Piegay, H. (Eds.), Tools in Fluvial Geomorphology. John Wiley & Sons, Chichester, England

2. Beechie TJ, Sear DA, Olden JD, Pess GR, Buffington JM, Moir H, Roni P, Pollock MM. 2010. Process‐based principles for restoring river ecosystems. BioScience 60: 209–222.

3. Palmer MA, et al. 2005. Standards for Ecologically Successful River Restoration. Journal of Applied Ecology 42‐2: 209–217.

4. Pollock, M. M., T. J. Beechie, J. M. Wheaton, C. E. Jordan, N. Bouwes, N. Weber, and C. Volk. 2014. Using Beaver Dams to Restore Incised Stream Ecosystems. Bioscience 64:279‐290.

5. Odum, H.T., Odum, B., 2003. Concepts and methods of ecological engineering. Ecological 5 Engineering, 20 (5): 339‐361.

6. Cluer B, Thorne C. A stream evolution model integrating habitat and ecosystem benefits. River Research and Applications. 2014 Feb 1;30(2):135‐54.

References