This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Riparian Area Inventory and Monitoring Using Large Scale Color Infrared Photography 1 Paul Cuplin 2 Abstract.--Variables that can be photointerpreted from large scale color infrared airphotos with ground data and used to monitor change in stream/riparian areas are stream width; floodplain width; stream channel stability; stream bank stability; stream shade; ground cover of trees, shrubs, and herbaceous vegetation; bare soil; riparian area and width; and density and structure of large trees and shrubs. Photo interpretation of large-scale airphotos combined with ground truthing produces a smaller list of riparian vegetation information that can be determined. These variables are as follows: vegetation type and subtype; width of riparian vegetation zone; riparian area acreage; structure of trees and shrubs; percent ground cover of trees, shrubs, and herbaceous vegetation; percent bare soil; and density of large shrubs and trees. INTRODUCTION Remote sensing is the collection and analysis of information about lands and resources, using a device not in physical contact with the lands or resources. Remote sensing includes techniques such as analysis of satellite, Side Looking Airborne Radar, thermal infrared scanning data; and the interpretation of aerial photography. Stream variables that can be measured from the airphotos are stream width, stream channel stability, streambank stability, floodplain width, and stream shade. The size and shape of riparian areas can often be determined from satellite digital analysis or interpretation of small-scale airphotos. However, large-scale airphotos at scales ranging from 1:1,000 to 1:4,800 are needed to interpret detailed information on streams and riparian vegetation. The 1:1,000 scale is preferred for ease of photo interpretation and good resolution. It is difficult to obtain stereo coverage at 1:1,000 scale due to 9- x 9-inch film recycling speed and safe lowlevel aircraft altitude. The compromise scale of 1:2,000 is acceptable and obtainable. Subtle changes in riparian vegetation are difficult to detect on airphotos. Conversely, catastrophic changes due to flooding can be easily monitored, and the amount of riparian area lost can be readily calculated. The method used to detect change in the stream/riparian area is to visually compare the baseline and monitoring airphotos. If changes are apparent, a sample site that appears in both airphotos is selected and key variables measured to determine the amount of change that has occurred. Color infrared photographs are especially valuable for vegetation analysis. Color tones, along with shape, size, pattern, shadow, and texture, are used to identify individual tree and shrub species in riparian areas. Types of riparian vegetation information that can be collected on the ground are vegetation type and subtype; width of riparian vegetation zone; species composition of shrubs, trees, grasses, and forbs; bare soil; plant density by species; condition class; plant reproduction; upward, downward, or stable trend; tree and shrub structure; and potential natural vegetation community. APPLICATION OF LARGE-SCALE AIRPHOTOS FOR INVENTORY AND MONITORING Ground sampling or familiarity with the riparian vegetation photographed is essential for accurate photo interpretation. Vegetation transects and tree, shrub circular characterization plots are transferable in general terms to large-scale airphotos. Trees, and some shrubs, can be readily identified by species; grasses and forbs cannot be identified by species unless a photo scale of 1:100 to 1:300 is used .. See table 1 for variables that can be identified on a scale of 1:2,000. lpaper presented at the Riparian Ecosystems and Their Management Symposium, [Tucson, Arizona, April 16-18, 1985]. 2Paul Cuplin is a Fishery Biologist, Bureau of Land Management, Denver, Colorado. 69 The most easily detected changes in a riparian area would be a reduction in foliar cover and an increase in bare soil. These changes may be obvious upon inspection of the baseline (original) photo compared with the monitoring photo taken five to ten years later. The cause of the change may be answered only by on-the-ground inspection; thus the photos offer the opportunity to monitor change but not the cause. Table l.--Variables that may be photo interpreted from 1:2,000 scale color infrared airphotos combined with on-the-ground data collection. Variable Photo Interpretation Vegetation Type and Subtype Riparian Area Width and Acreage Yes Yes GROUND DATA COLLECTION Plant Species Composition Trees Shrubs Select ground data sites that are accessible and representative of the riparian vegetation and stream conditions. One site per 1- to 3-mile stream segment may be sufficient for airphoto interpretation. If there are significant differences in a stream segment, additional data collection sites should be esta blished. Yes Yes, some shrubs such as willow and baccharis No No Grasses Forbs Ground Cover % Trees % Shrubs % Herbaceous Vegetation % Bare Soil Yes Yes Density Yes Yes Take color print 35-mm photographs of the stream/riparian area (upstream, across stream, and downstream) at the site where the airphoto target is placed. Yes, large trees and some shru bs such as cottonwood and willow Collect stream inventory of 1/10 mile of stream segment. Reproduction Yes, young trees and shrubs but not seedlings Condition Class No Trend Yes, as related to change in the amount of ground cover and bare soil Potential Structure Stream bank Shade Stream Width Floodplain Width Streambank Stability Streambed Silt Stream Channel Stability ON-SITE DATA COLLECTION Determine the dominant and subdominant herbaceous vegetation, shrubs, and trees, and the percent bare soil. Take additional field notes that may assist in photo interpretation. ACQUISITION OF LARGE-SCALE LARGE-FORMAT (9- x 9-INCH) AERIAL PHOTOGRAPHS The 9- x 9-inch format is easy to work with, and most photo interpretation can be accomplished with a minimum of equipment. The 9- x 9-inch photos are identified by date, fiducial marks, agency, photo scale, state symbols, roll number, and exposure number. Photos can be easily filed, and extra prints can be ordered as needed for field use. No Yes, height of trees and shrubs Yes Yes Yes Yes Yes Yes A 9- x 9-inch format photo covers approximately 52 acres, or 2,250,000 square feet, at a scale of 1:2,000. At this scale, riparian zones on first, second, and third order streams are easily photographed with a good margin of the adjacent upland. BASELINE Original large-scale airphotos of a riparian area provide an overview of existing conditions in terms of the readily interpreted variables. Subsequent airphotos over time provide the means of detecting change in these variables. Subtle change due to the lack of or above normal precipitation may not be evident as compared to the catastrophic change caused by a lOO-year flood. Assistance on airphoto acquisition should be sought from a remote sensing coordinator. The publication "Aerial Photography Specifications," June 1983, BLM, is available from the Branch of Remote Sensing (D-442), Denver Service Center, BLM. This publication provides detailed specifications for acquiring aerial photographs via contract. 70 Sample Size Provide the photographer with a USGS quad map that shows the beginning and end of each stream/riparian area to be photographed. Delineate flight lines on the maps to indicate to the photographer the direction of airplane travel and the midpoint and width of each flight line according to the photo scale that has been requested. The sample size used to determine change should be large enough to represent the area and the changes that have occurred. Select a representative site that can be identified on both baseline and monitoring airphotos. Accuracy SUGGESTED STREAM/RIPARIAN INVENTORY AND MONITORING PROCEDURES USING LARGE-SCALE COLOR INFRARED AIRPHOTOS AND GROUND DATA Determine the accuracy required to assess a variable to assure that the correct variable is being assessed and that changes are the result of management and not the result of natural variation caused by precipitation or other influences. Baseline Inventory Identify the stream/riparian segment. Results Describe existing condtions for the stream/riparian segment. If results are uncertain, select other comparative areas for analysis. From the changes detected in photo interpretation, determine if management objectives were achieved. Identify resource needs and concerns. Area Management Describe the management for the area. CONCLUSIONS Identify the objectives and management goals for the area. The use of large-scale color infrared airphotos for inventory and monitoring riparian areas is best applied at a scale of 1:2,000 in 9- x 9-inch format. Identify improvement goals and the changes, such as increasing the amount of ground cover, narrowing stream width, or increasing the number of trees and shrubs, that can be measured. Ai rphotos that were taken from a small bubble type helicopter while using a handheld 35-mm camera have application to small projects. However, if several miles of stream/ riparian area are to be photographed, it can best be done by an airphoto contractor with a 9- x 9-inch mapping camera. Variables Variables that can be used to easily detect changes are as follows: Variables that can be photointerpreted from large-scale color infrared airphotos with ground truth and that can be used to detect change in the stream/riparian area are stream width; floodplain width; stream channel stability; stream bank stability; stream shade; ground cover of trees, shrubs, and herbaceous vegetation; bare soil; riparian area and width; and density and structure of large trees and shrubs. Ground cover--An increase or decrease in ground cover of trees, shrubs, and herbaceous vegetation, and in bare soil can be detected by visual observation of large-Reale airphotos. Stream width--Changes in stream width can be easily measured on large-scale airphotos. These changes are an early indicator of improving or degrading stream conditions. Stream width increases under heavy livestock grazing and narrows during the recovery period of no livestock grazing. LITERATURE CITED U.S. Department of Interior, Bureau of Land Management. 1983. Aerial Photography Specifications. BLM Denver Service Center. Denver, CO. l5pp. Channel and bank stability--Stream channel and streambank stability can be readily interpreted from large scale airphotos. Size of riparian area--Riparian area width and acreage can be readily measured on large-scale airphotos. 71