Mitigation Options for the Endangered Tahoe yellow cress (Rorippa - - PowerPoint PPT Presentation

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Mitigation Options for the Endangered Tahoe yellow cress (Rorippa - - PowerPoint PPT Presentation

Mitigation Options for the Endangered Tahoe yellow cress (Rorippa subumbellata) Alison E. Stanton and Bruce M. Pavlik BMP Ecosciences South Lake Tahoe alisonestanton@sbcglobal.net Tahoe yellow cress (TYC) Endangered in CA Critically


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Mitigation Options for the Endangered Tahoe yellow cress

(Rorippa subumbellata)

Alison E. Stanton and Bruce M. Pavlik BMP Ecosciences South Lake Tahoe alisonestanton@sbcglobal.net

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Tahoe yellow cress (TYC)

  • Endangered in CA
  • Critically Endangered in NV
  • TRPA threshold species
  • Candidate for federal protection under ESA
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Habitat and Threats

  • Restricted to sandy

beach below high water line

  • Beach use and

trampling

  • Water

management: sustained high lake levels

Reservoir management : 6,222 – 6,229.1 ft LTD

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9 sites in 1999

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Conservation Strategy

  • Adopted in 2002
  • Adaptive Management

Working Group (AMWG) meets quarterly

  • 6 Goals and associated

Objectives for recovery

  • Collaborative research

program started in 2003

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Post CS

24 sites in 2006 6,228 ft 46 sites in 2009 6,223 ft

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Project-related impacts to TYC

  • All regulations

require full mitigation of actual

  • r potential

significant impacts.

TRPA SHOREZONE CODE 75.2.A Sensitive Plants: Projects and activities in the vicinity of sensitive plants or their associated habitat, shall be regulated to preserve sensitive plants and their habitat. All projects or activities that are likely to harm, destroy, or

  • therwise jeopardize sensitive

plants or their habitat, shall fully mitigate their significant adverse effects.

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No projects have required any mitigation other than avoidance

  • Project re-design
  • Plant flagging
  • Fencing
  • Construction personnel education

Mitigation Tool box

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AMWG: Experimental plantings from 2003-09

10,000 container-grown plants at 14 sites

  • utplanting

translocation

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What we know about outplanting with container-grown TYC

  • What types of container-grown plants to

use (good roots, mixed seed sources)

  • How to propagate quality container-grown

plants

  • When to plant (optimal lake elevation and

seasonality factors)

  • The Where is more problematic
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Where (within a site): plant performance improves with decreasing depth to the water table

10 20 30 40 50 60 70 80 90 100 6/9/2004 6/23/2004 7/19/2004 8/17/2004 9/14/2004 10/14/2004 Mean Reproduction (% of survivors) Moist shoreline Low Beach High Beach

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Where (among sites) : Survivorship and reproduction highly variable among sites

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When: early planting in June is better than later planting in August or Sept

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How does translocation compare with outplanting?

Paired design: 50 container-grown 50 translocants

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Pattern of differential survivorship among sites is inconclusive

10 20 30 40 50 60 70 80 90 100 Ebright NV Pope UTE

survivorship (% of cohort

2009 cohort year 2

Translocant Container

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Container-grown plants perform greater than translocated plants

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Container-grown Translocation

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Mitigation Toolbox NOW

  • Avoidance
  • Population enhancement or

creation

  • Outplanting of container-grown

plants

  • Translocation
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Current and future projects will require mitigation

  • Storm water quality improvements
  • Erosion control
  • River and stream restoration
  • Lake shore development
  • Pier and boating facilities
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Mitigation: what are the options?

  • On-site plantings: if habitat is available
  • Off-site plantings: if no suitable habitat
  • Need for a reference site to assess

planting success

  • Attempt translocation or use container-

stock?

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Choosing a planting site

TYC performance is highly microsite- specific: absence of TYC may equal unsuitable habitat

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Moving plants to a public enclosure

Transfers responsibility and sets an undesirable precedent Lacks conservation value because those sites are already “saturated” with TYC

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TYC is not like typical rare plants

  • Little genetic variation or evidence of

population architecture

  • Vigorous clonal growth and prolific seed

production

  • Metapopulation dynamic: presence and

absence linked to lake levels

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Standard regulations are difficult to apply

  • Assessing impact may be difficult
  • “perpetuity” requirements for protection of

plants or habitat are not biologically feasible

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So what do we do?

  • Utilize an Adaptive Management approach

and the knowledge of the AMWG to assess project impacts and specify mitigation

  • Update Conservation Strategy with

research results

  • Re-new the MOU to implement the CS
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Acknowledgements

  • AMWG members
  • Funding
  • CA Dept of Fish and

Game Section 6

  • SNPLMA – contract

administration through the USFS LTBMU