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Eva Dettweiler-Robinson

Publications and source records attributed to Eva Dettweiler-Robinson.

2 recordsLinked to original sources

Are fungal networks key to dryland primary production?

In low-resource ecosystems, competition among primary producers can be reduced through the partitioning of limiting resources in space or time. Partitioning, coupled with species interactions, can be a source of ecosystem stability by retaining resources within a biotic “loop” and slowing losses due to physical processes, such as erosion, gaseous loss, or leaching. Such coupling occurs in marine food webs (the microbial loop), where positive interactions among microbes limit losses of nutrients that would otherwise drop to the ocean floor (Fenchel, 2008). Likewise, mycorrhizal fungi in tropical rainforests may rapidly recycle litter nutrients back to canopy trees, preventing leaching driven by high rainfall (Hattenschwiler et al., 2011). Such dynamics differ from the paradigm for most mesic, terrestrial ecosystems, in which the primary source of nutrients for primary production is the decomposition of soil organic matter (SOM, Schimel and Bennett, 2004). Thus, in ecosystems that lack large reserves of soil organic matter to supply nutrients to producers (e.g., drylands, where sparse litter yields low SOM), biotic retention of nutrients may be particularly critical to primary production and ecosystem dynamics.

American Journal of Botany

Outplanting Wyoming big sagebrush following wldfire: stock performance and economics

Finding ecologically and economically effective ways to establish matrix species is often critical for restoration success. Wyoming big sagebrush (Artemisia tridentata subsp. wyomingensis) historically dominated large areas of western North America, but has been extirpated from many areas by large wildfires; its re-establishment in these areas often requires active management. We evaluated the performance (survival, health) and economic costs of container and bare-root stock based on operational plantings of more than 1.5 million seedlings across 2 200 ha, and compared our plantings with 30 other plantings in which sagebrush survival was tracked for up to 5 yr. Plantings occurred between 2001 and 2007, and included 12 combinations of stock type, planting amendment, and planting year.We monitored 10 500 plants for up to 8 yr after planting. Survival to Year 3 averaged 21% and was higher for container stock (30%) than bare-root stock (17%). Survival did not differ among container stock plantings, whereas survival of bare-root stock was sometimes enhanced by a hydrogel dip before planting, but not by mycorrhizal amendments. Most mortality occurred during the first year after planting; this period is the greatest barrier to establishment of sagebrush stock. The proportion of healthy stock in Year 1 was positively related to subsequent survival to Year 3. Costs were minimized, and survival maximized, by planting container stock or bare-root stock with a hydrogel dip. Our results indicate that outplanting is an ecologically and economically effective way of establishing Wyoming big sagebrush. However, statistical analyses were limited by the fact that data about initial variables (stock quality, site conditions, weather) were often unrecorded and by the lack of a replicated experimental design. Sharing consistent data and using an experimental approach would help land managers and restoration practitioners maximize the success of outplanting efforts.

Washington