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Transcript
Restoration scale and stream
benefits in California rangelands
Bronwen Stanford
Erika Zavaleta
University of California, Santa Cruz
Riparian tree restoration
• Widely used in agricultural systems
• Potential to restore ecological function
• BUT width matters.
• Potential importance of buffer length
•
•
•
•
Lower temperatures
More organic debris and opportunities to trap wood
Improved channel complexity
Less fine sediment
1. In rangelands, which ecological metrics
improved with restoration at narrow buffer
scales?
2. Are larger ecological gains possible with
longer buffers?
- 2nd-4th order streams
- Consistent land use: rangelands
- Restoration completed >7 years ago
NLCD 2011
Treatment
(distance along
buffer)
• Abiotic
Rangeland
0m
>200 m
>500 m
1
• Channel form
• Substrate size (D50)
• Dissolved solids (specific
conductivity)
• Water temperature
• Biotic
2
3
• Aquatic vegetation (% cover)
• Organic debris and wood
• Benthic macroinvertebrates
• Density
• Richness
• Percent sensitive -California Aquatic
Bioassessment Laboratory Network
• 25 sites nested in 8 streams
• Primary predictor variable is buffer length –
upstream linear length with riparian trees
Upstream of buffer
Within buffer
Upstream of buffer
Within buffer
Upstream of buffer
Within buffer
Response of in-stream conditions to
Watershed condition (hydrology, land cover)
Riparian buffer length
Riparian buffer presence
Watershed scale controls water quality
Buffer length increased % sensitive taxa
Sensitive = tolerance level 0 - 2 out of 10, CAMLnet 2003
Buffer length increased % sensitive taxa
Sensitive = tolerance level 0 - 2 out of 10, CAMLnet 2003
Buffer length increased % sensitive taxa
y=inverse logit (-3.38 + 0.001 * x + ɛ)
p < 0.001
Sensitive = tolerance level 0 - 2 out of 10, CAMLnet 2003
Similar responses
- Abundance (inverse)
- Temperature (inverse)
Buffer presence increased in-stream wood
Buffer presence increased in-stream wood
Paired t-test
p < 0.04
No Trees
Trees
Similar responses
- % cover macrophyte (inverse)
1. Response controlled by watershedscale
(controls including land use, geology)
2. Buffer length
Proportion sensitive insect families
Insect abundance
Temperature
Conductivity
Channel form
3. Buffer presence
4. Patterns vary by site
Wood
Aquatic vegetation
Substrate size
Insect family richness
Year Two - 2016
• Addition of 7 more streams (total 15)
• Comparison of contrasting rainfall conditions
Conclusions
• BUFFERS MATTER – even short buffers (~200 m)
• Longer buffers (>500m) can be better than shorter
• Recovery is constrained by watershed condition
Thanks to
Liam Zarri
David Herbst
Karen Holl
[email protected]
Stream width
Aquatic vegetation
Macrophyte cover
Increasing
buffer length
18% of
variance
explained
Conductivity
Woody debris
Bare ground
Complexity
Organic debris
Substrate size
39% of
variance
explained
Sun
Macrophyte cover
Aquatic vegetation
% Predators
Year Two - 2016
Tolerance value
PCA for environmental variables
14.99-0.0068*Buffer Length + ɛ
p=0.07