Interacting effects of water input, nitrogen deposition, and fire on Coastal Sage Scrub Mike Goulden mgoulden@uci.edu How vulnerable (resilient, resistant,

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Presentation transcript:

Interacting effects of water input, nitrogen deposition, and fire on Coastal Sage Scrub Mike Goulden mgoulden@uci.edu How vulnerable (resilient, resistant, etc) are Southern California’s ecosystems to stress (fire, climate change, N deposition, etc)? What stress or combination of stresses poses greatest risk (where’s the Achilles heel)?

Experimental approach Loma Ridge San Jacinto Mtns Pacific Palm Springs Santa Ana Mtns Transect Surveys Eddy Flux Manipulations

Loma Ridge section of historic Irvine Ranch (~75 km southeast of here) Currently managed by Irvine Ranch Conservancy Mosaic of exotic annual grassland coastal sage evergreen oaks Experiment site What did this area look like 80 years ago?

VTM (Vegetation Type Map) survey in ~1930 Hand drawn – working off ~1895 topographic maps – lots of uncertainty Mosaic of exotic annual grassland coastal sage evergreen oaks Similar to what we see today Experiment site - dominated by California sagebrush, black sage and buckwheat

GL CSS California sagebrush, black sage and buckwheat California sagebrush, black sage still dominate; Rhus/Malosma have increased

Why so stable? Differences in soil? Nope – same texture across border – same texture to 2-m depth Constant environment? Nope – at least 4 wildfires (1948, 67, 98, 07), an order of magnitude interannual precip variation Lots of ecological resiliency (at least to normal fire and precip patterns of management since 1930)

Air T Resiliency to wildfire – an unfortunate dataset * 65 mph gusts

Two sites ~300 m apart on similar soil Santiago Fire Coastal sage Eddy covariance – measures whole ecosystem exchanges, such as photosynthesis Two sites ~300 m apart on similar soil Both burned in Oct 2007 Santiago wildfire Fire had no (or positive) effect on grass production CSS production recovered rapidly –rates of exchange 3-4 years after fire appear higher than before fire Respiration July Jan July Jan July Jan July Jan July Jan July Greater photosynthesis 72 mm 223 mm 212 mm 370 mm 540 mm Respiration Annual grassland July Jan July Jan July Jan July Jan July Jan July Greater photosynthesis

Loma Ridge Manipulate water (+-50%) and Nitrogen (+) input for last 5 years CSS GL CSS

Simulate effects of climate change on experimental plots using roofs that close/open to remove/add water - Roofs open ~97% of the time

Roofs closed 3% of the time (for big storms)

Water input for the various treatments 1/3 of the plots get extra water 1/3 of the plots get normal water 1/3 of the plots get reduced water

Grassland - Very rapid shifts in species composition

Rapid changes in relative abundance – Species reordering Species coexist at climatological precipitation (median 236 mm /yr) Species reordering tied to traits Favored with drought - Forbs and shorter time to flowering Favored in wet treatments - Grasses and N fixers 1929-2010 median 236 mm

CSS’ Achilles heel? The combination of: Fire (knocks shrubs back 2-3 years; no or positive effect on grasses) Several dry years (soil below 0.5-1 m remains dry; hurts shrubs, not grasses) Added N (accelerates grasses; only small effect on shrubs) Normal Nitrogen Added Nitrogen Reduced precipitation Moderate risk of change to red brome grassland Large risk of change to red brome grassland Normal precipitation Stable Moderate risk of change to brome grassland Added precipitation