Shapefile
Tags
history, soils, Blue
River Watershed, Oregon, Willamette Basin, Andrews watershed 1, HJ Andrews Experimental
Forest
To document the history of soil classification for watersheds 1, 2, and 3, using the field map of small watershed survey completed by CT Dyrness in 1964.
Two soil surveys exist for the Andrews small watersheds. Soils datasets were developed from both surveys to test model sensitivity to variations in soil variables. The 1964 soil survey is the soils dataset used by most researchers at the Andrews. It was completed in 1964 by a USGS soil survey team andwas available through the Andrews GIS data archive (FSDB). The 1964 survey includes map units of soil series, percent slope, and Iandform (USDA, 1964). This survey was largely based on aerial photo interpretation.
Additionally, an intensive soil survey was completed for the Andrews WS 1, 2 & 3 in the 1960's in conjunction with the beginning of the small watershed experiments (Dyrness, 1969). In order to create a dataset from the small watershed survey, the soil survey field map (Dymess et al., unpublished) was digitized using Arclnfo 7.0.4 (ESRI,1996). The small watershed survey includes map units of soil series, soil series phase (based on rock fragment), percent slope, and landform. This survey was based on soil profile and Iandform analysis. Soil series and soil phase profile summaries (Rothacher et al., 1967 & Dyrness, 1969) were used to develop the soil depth, percent rock fragment and texture percentages needed for the modeling datasets. The soil attributes were added to the soil survey maps in Arclnfo 7.0.4 (ESRI, 1996) and each attribute layer was converted to a 30m grid using ArcGrid 7.0.4 (ESRI, 1996) for use in the modeling effort/
There are no credits for this item.
While substantial efforts are made to ensure the accuracy of data and documentation, complete accuracy of data sets cannot be guaranteed. All data are made available "as is". The Andrews LTER shall not be liable for damages resulting from any use or misinterpretation of data sets.
Extent
West | -122.258898 | East | -122.224566 |
North | 44.219904 | South | 44.198715 |
Maximum (zoomed in) | 1:5,000 |
Minimum (zoomed out) | 1:150,000,000 |
ground condition
Access constraints: Available on-line
Use constraints: See data access policy at www.fsl.orst.edu/lter (especially the data use policy)
While substantial efforts are made to ensure the accuracy of data and documentation, complete accuracy of data sets cannot be guaranteed. All data are made available "as is". The Andrews LTER shall not be liable for damages resulting from any use or misinterpretation of data sets.
Obtain information off of WWW site, call contact person for special requests.
Call contact person for instructions and costs.
polygon feature class
esri
Internal feature number.
ESRI
Feature geometry.
ESRI
Area of feature in internal units squared.
ESRI
Perimeter of feature in internal units.
ESRI
Internal feature number.
esri
User-defined feature number.
esri
soil codes
internal documentation
Soil series name
internal documentation
SRI phase codes
internal documentation
soils series phase name
internal documentation
slope in percent
internal documentation
Slope Percent
internal documentation
landform
internal documentation
land form names
internal documentation
total soil depth
internal documentation
percent clay in top 500mm of soil
internal documentation
percent clay in 2nd soil layer (500-1500mm)
internal documentation
percent clay in 3rd soil layer (>1500mm)
internal documentation
percent sand in top 500mm of soil
internal documentation
percent sand in 2nd soil layer (500-1500mm)
internal documentation
percent sand in 3rd soil layer (>1500mm)
internal documentation
percent rock fragment in the top 500mm of soil
internal documentation
percent rock fragment in the 2nd soil layer (500-1500mm)
internal documentation
percent rock fragment in the 3rd soil layer (>1500mm)
internal documentation
Vegetation history classification for watersheds 1, 2, and 3 (1959-1990),
Andrews Experimental Forest. Photos were interpreted for hydrologically relevant
vegetation types (conifer, broadleaf, grasses and bare soil) and forest age class
was determined for each year (1959, 1962, 1967, 1972, 1979, and 1990). Vegetation
data for functional groups (conifer, evergreen broadleaf, deciduous broadleaf) was
aggregated from species data available in TP73 for the long term vegetation plots in
Watershed 1.
To document the history of vegetation classification for watersheds 1, 2, and
3, pre and post harvest.
ground condition
Available on-line
See data access policy at www.fsl.orst.edu/lter (especially the data use
policy)
The accuracy of the aerial photo interpretation was assessed through comparison of
the percent cover maps against the plot cover measurements. Some differences were
expected between the mapped cover percentages and the plot measurement, because of the
difference in the resolution of the mapped areas and the 2x2m plot size. The mapped
areas were drawn with an expectation that there was significant heterogeneity in the
vegetation cover within each map unit. These results are presented in Appendix B of
thesis. The 1972 herbaceous cover map agreed with the plot data for 45 plots, and in
general overestimated herbaceous cover. The 1972 conifer and evergreen broadleaf cover
map agreed with the plot data for 31 plots, and in general overestimated conifer and
evergreen broadleaf cover. The 1972 deciduous broadleaf cover map agreed with the plot
data for 58 plots, and in general underestimated deciduous cover. The 1979 conifer and
evergreen broadleaf cover map agreed with the plot data for 35 plots, and in general
overestimated conifer and evergreen broadleaf cover. The 1979 deciduous broadleaf cover
map agreed with the plot data for 44 plots, and in general underestimated deciduous
cover. The 1990 herbaceous cover map agreed with the plot data for 27 plots, and in
general overestimated herbaceous cover. The 1990 evergreen broadleaf cover map agreed
with the plot data for 18 plots, and in general overestimated evergreen broadleaf cover.
The 1990 conifer cover map agreed with the plot data for 28 plots, and in general
overestimated conifer cover. The 1990 deciduous broadleaf cover map agreed with the plot
data for 34 plots. These map assessments were not used to adjust the cover map for two
reasons. The resolution of the map units was quite a bit larger than the plot size, and
there was no discernible spatial pattern in the plot data that could have been used to
adjust the cover maps.
Small watershed survey was completed in 1964.
Metadata imported.
While substantial efforts are made to ensure the accuracy of data and
documentation, complete accuracy of data sets cannot be guaranteed. All data are made
available "as is". The Andrews LTER shall not be liable for damages resulting from any
use or misinterpretation of data sets.
Obtain information off of WWW site, call contact person for special
requests.