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The interagency Forest Health Monitoring Program involves a network of about 4200 forest plots on a triangular grid across the United States. We present data on recent mortality of trees 27.9 cm diameter from the first three years of measurements in California (1992–1994). Three plot designs were used to collect data representative of a 1-ha stand at each site; the designs differed primarily in total area sampled (0.067, 0.4 and 1.0 ha). Approximately 50 sites were visited each year yielding a total of about 150. Field tallies showed few cases of recent mortality in the smallest plot size. Cumulative distribution functions of recent dead tree densities in the 0.067-ha plots differed significantly from those generated by tallies from entire 1-ha stands. We conclude that an area of 0.067 ha is unsuitable to assess and monitor overstory mortality in Pacific Coast forests.The U.S. government right to retain a non-exclusive, royalty free licence in and to any copyright is acknowledged. 相似文献
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Leon Liegel David Cassell Donald Stevens Paul Shaffer Robbins Church 《Environmental management》1991,15(2):269-279
The Direct/Delayed Response Project (DDRP) is one of several studies being conducted by the United States Environmental Protection
Agency to assess risk to surface waters from acidic deposition in the eastern United States. In one phase of DDRP, land use,
wetland, and forest cover data were collected for statistical samples of 145 Northeast lake and 35 Southern Blue Ridge Province
stream watersheds in the United States. Land-use and other data then were extrapolated from individual to target watershed
populations. Project statistical design allows summarization of results for various subsets of the target population. This
article discusses results and implications of the land-use and land-cover characterization for both regions.
Forest cover was the primary land use in both regions. In the Northeast, developed (agriculture and urban) land was positively
associated with surface-water chemistry values for acid neutralizing capacity, Ca plus Mg, pH, and sulfate in the Pocono/Catskill
subregion. Extensive wetlands and beaver activity occur in parts of the Northeast region, whereas topography limits wetland
and riparian development in the Southern Blue Ridge Province. Northeast soils have low sulfate adsorption capacity, most watersheds
are near sulfur steady state, and lake sulfate concentrations are controlled principally by levels of sulfur deposition. Net
annual sulfur retention in Northeast watersheds is positively correlated with occurrence of wetlands and beaver impoundments.
In contrast, most Southern Blue Ridge Province soils have high sulfate adsorption capacities, resulting in high net watershed
sulfur retention. At the present time, stream sulfate concentrations and percent sulfur retention are controlled principally
by soil chemical properties related to adsorption rather than atmospheric deposition and land use.
The information in this document has been funded wholly by the United States Environmental Protection Agency. It has been
subjected to the agency's peer and administrative review, and it has been approved for publication as an EPA document. Mention
of trade names or commercial products does not constitute endorsement or recommendation for use. 相似文献
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Jeffrey Lee Robbins Church Duane Lammers Leon Liegel Mark Johnson Deborah Coffey Richard Holdren Donald Stevens Robert Turner Louis Blume 《Environmental management》1989,13(1):95-108
Through the Direct/Delayed Response Project (DDRP), the United States Environmental Protection Agency is attempting to assess the risk to surface waters from acidic deposition in three regions of the eastern United States: the Northeast Region, the Southern Blue Ridge Province, and the Mid-Appalachian Region. The central policy question being addressed by the DDRP is: Within the regions of concern, how many surface water systems (lakes, streams) will become acidic due to current or altered levels of acidic sulfur deposition, and on what time scales? The approach taken by the DDRP is to select a statistically representative set of watersheds in each region of concern and to project the future response of each watershed to various assumed levels of acidic deposition. The probability structure will then be used to extrapolate the watershed-specific results to each region. The data will be used also for statistical investigation of hypothesized relationships between current surface water chemistry and watershed characteristics. Because the needed terrestrial data base was not available, regional watershed surveys were conducted to meet the specific data needs of the DDRP. Maps (1∶24,000) of soils, vegetation, land use, depth to bedrock, and bedrock geology were made for each watershed. The soils were grouped into sampling classes based on their hypothesized response to acidic deposition. Randomized sampling of these classes provided regional means and variances of soil properties that can be applied to individual watersheds. Because of DDRP's need for consistency within and among regions, unique quality control/quality assurance activities were developed and implemented. After verification and validation, the DDRP data base will be made publicly available. This will be a unique and useful resource for others investigating watershed relationships on a regional scale. The results of these surveys and the conclusions of the DDRP will be presented in several future papers. The current paper gives an overview of the context, rationale, logistical considerations, and implementation of these surveys, with special emphasis on the field activities of watershed mapping and soil sampling. This discussion should be useful to those planning, implementing, and managing survey activities in support of regional assessments of other environmental concerns, who are likely to face similar choices and constraints. 相似文献
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