Forest responses to climate change in the northwestern United States: Ecophysiological foundations for adaptive management

Climate change resulting from increased concentrations of atmospheric carbon dioxide ([CO₂]) is expected to result in warmer temperatures and changed precipitation regimes during this century. In the northwestern U.S., these changes will likely decrease snowpack, cause earlier snowmelt, increase summer evapotranspiration, and increase the frequency and severity of droughts. Elevated [CO₂] and warmer temperatures may have positive effects on growth and productivity where there is adequate moisture or growth is currently limited by cold. However, the effects of climate change are generally expected to reduce growth and survival, predispose forests to disturbance by wildfire, insects, and disease; and ultimately change forest structure and composition at the landscape scale. Substantial warming will likely decrease winter chilling resulting in delayed bud burst, and adversely affect flowering and seed germination for some species. The extent of these effects will depend on the magnitude of climate change, the abilities of individual trees to acclimate, and for tree populations to adapt in situ, or to migrate to suitable habitats. These coping mechanisms may be insufficient to maintain optimal fitness of tree populations to rapidly changing climate. Physiological responses to climatic stresses are relatively well-understood at the organ or whole-plant scale but not at the stand or landscape scale. In particular, the interactive effects of multiple stressors is not well known. Genetic and silvicultural approaches to increase adaptive capacities and to decrease climate-related vulnerabilities of forests can be based on ecophysiological knowledge. Effective approaches to climate adaptation will likely include assisted migration of species and populations, and density management. Use of these approaches to increase forest resistance and resilience at the landscape scale requires a better understanding of species adaptations, within-species genetic variation, and the mitigating effects of silvicultural treatments.     

Experiments in rooting bishop pine (Pinus muricata D. Don) cuttings

Presented here are results of rooting studies using hedges established from juvenile seedlings of blue and green foliaged bishop pine (Pinus muricata D. Don) from Mendocino and Sonoma Counties, California. Rootability, averaged over all clones and all setting dates, was 88%. The average time for 50% of the cuttings to root was 6 months. In general, cuttings began to root rapidly in late winter/early spring. The time of year when cuttings were set determined how soon they began a phase of rapid rooting, with cuttings set in winter and early spring beginning faster than other setting dates. The period of rapid rooting lasted 2–3 months until mid/late summer, beyond which time, rooting was slow. Population and family differences in rooting were not significant; differences in rooting among clones, however, were large and significant. Analyses of clones in two experiments indicated that rooting was heritable.     

2008 AFHVS presidential address

The critical studies in the Sociology of Agriculture can be generally divided into four questions: Agrarian, Environmental, Food, and Emancipatory. While the four questions overlap and all address social justice concerns, there is a chronological sequence to the studies. In this presidential address presented at the joint meetings of the Agriculture, Food, and Human Values Society and the Association for the Study of Food in Society held in June 2008 in New Orleans, LA, I provide an overview of the four questions and call for researchers and activists in agrifood studies to engage as public social scientists to bring about a more just and equitable agrifood system.