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Watershed Conditions: Roads and Erosion in KRIS Gualala

KRIS Web Background Pages: Road and Erosion

Road densities in KRIS Gualala were calculated from spatial data provided by the University of California ICE project which digitized roads from recent aerial photographs. Road density calculations include main haul roads, but not skid trails and spur roads, which also contribute to erosion. The road mapping project was funded by the North Coast Regional Water Quality Control Board (NCRWQCB), which has been engaged in a sediment source analysis of the Gualala River watershed pursuant to the Clean Water Act TMDL process (CRWQCB, 2001). That document found that roads are a the most significant erosion source in the Gualala River basin (see the KRIS Web Sediment Background page for more information). The data from the NCRWQCB study is used in KRIS Gualala as the best available estimate for understanding current sediment sources. 

Road densities in the Gualala Basin average 4.8 miles per square mile. KRIS Gualala charts show roads per square mile by sub-basin compared to a threshold of 3 miles of road per square mile. The latter is taken from the National Marine Fisheries Service (1996) working guidelines for salmon conservation (see Table below). The guidelines characterize watersheds over this threshold as "not properly functioning". Valley bottom roads are a significant concern in the Gualala River because many logging haul roads are parallel and proximate to stream courses. 

Properly Functioning Condition At Risk Not Properly Functioning
  • < 2 miles/square mile                            
  • No valley bottom roads
  • 2.5 miles/square miles                                
  • Few valley bottom roads
  • >3 miles/square mile                                    
  • Many valley bottom roads

Recognition of road and erosion problems in the Gualala River basin has lead to a number of road improvement and erosion control projects in recent years. Two notable projects are the upgrading of Kelly Road and road erosion-proofing of the Fuller Creek basin. See Gualala Restoration Background pages to learn more about these efforts.

IFR staff used intersections of stream and road electronic map layers to generate stream crossing data. Road crossing failures are one of the major sources of erosion during storm events. Variability of the USGS 1:24000 hydrography maps make crossings look more numerous in areas with a higher mapped stream density. Pictures displayed below are courtesy of Brian McFadden, North Coast Regional Water Quality Control Board and Don Morse, California Department of Forestry (FRAP), North Coast Watershed Assessment Program.

roads_gualala_basinwide.gif (67532 bytes)
A map of the Gualala basin with roads and large subbasin NCWAP study areas is displayed at left. Road densities are low in the highly erodible earthflow terrain of the eastern and southeastern portions of the watershed. Road densities are highest in industrial timberland holdings in the western and northwestern portions of the Gualala basin. 
roads_chart_gual_all.gif (26928 bytes)
The chart at left shows the density of roads in miles per square mile for all Gualala River Calwater planning watersheds. The highest road densities tend to be in the northern and western basins where industrial timber harvest is the primary land use. Road densities are lower in the eastern Gualala watershed where there is unstable terrain associated with the Central Belt Franciscan formation.
roaddensity.jpg (806872 bytes) Some areas of the Gualala watershed show a dense network of roads, skid roads and skid trails from which sediment can be contributed to streams as surface erosion. Road densities in the Gualala basin only consider main haul roads; therefore, calculations of road density are very conservative. Depending on temporary haul road and skid trail layouts, the actual densities may be two to ten times higher.

 

 

thp_40_60_buckeye.jpg (247420 bytes)
This map shows logging that occurred in the Buckeye Creek basin between 1940 and 1960. The orange lines indicate where roads and/or log skidding followed streams. These may have been temporary roads in some cases, but many logging haul roads still follow stream courses today. See the picture below for an example of logging practices at this time. Map digitized by Don Morse. 

1961_buckeye.jpg (627697 bytes)
The photo at left was taken on May 12, 1961 and shows active logging along Buckeye Creek near its convergence with Franchini Creek. Almost the entire Franchini Creek watershed is visible at upper right and it was 100% logged with extremely dense road and skid trail networks. This intensive post WW II logging caused catastrophic change to both Franchini and Buckeye Creeks after the 1964 flood. Photo provided courtesy of Don Morse. 

nearly plugged culvert.jpg (117324 bytes) This plugged culvert exemplifies a huge problem in the Gualala watershed resulting from past logging and road building. After about 25 years, culverts are likely to collapse from rot. Plugged culverts often take the road prism with them when they wash out. Picture provided by Brian McFadin. 

 

st xing failure -sf Fuller 1.jpg (107540 bytes)
The picture at left shows where a culvert plugged and road fill on both sides of the culvert was washed away. Roads are a major part of sediment problems in the Gualala basin (see Sediment Information in KRIS Gualala Background page). Picture provided by Brian McFadin.

 

road_kelly.gif (83099 bytes) Gully erosion off of Kelly Road in the upper Wheatfield drainage is depicted at left. While Kelly Roads has had drainage improvements pursuant to its transfer from the Army Corp of Engineers to private parties, it has not been out-sloped and instead an in-board ditch has been maintained. The erodible terrain of the Central Belt Franciscan melts under culverts discharging water from the ditch to the hillslope. Photo by Pat Higgins
road_nfgual_haul.gif (324410 bytes)
Haul roads in the North Fork Gualala often run parallel to streams and winter hauling pumps fine sediment from the road surface into those adjacent streams. The picture at left shows a haul road where the water table in winter is so high that there is standing water. Photo provided courtesy of the National Marine Fisheries Service.
roads_doqs_stewart_cwe.gif (287686 bytes)
This map image shows roads in the Stewart Creek Calwater in the North Fork Gualala basin which total seven miles per square mile. This basin is very steep with many inner gorge areas. Note that roads follow streams in many locations, such as Lost Creek. 

 

roadslide1.jpg (39327 bytes)

cutandfillfailure.jpg (501661 bytes)

Fill failure.jpg (125294 bytes)

The image above shows a large slide associated with a road immediately adjacent to a major tributary of the Gualala River. This road location is high risk in that it is on steep slopes right above the watercourse in an "inner gorge" location. Photo by Brian McFadin. This picture typifies a cut and fill road failure, which triggered a very large debris slide on a steep slope above a Gualala River tributary. The road does not appear to have been in active use at the time of this failure. Picture provided by Brian McFadin. Close up of fill failure near a road at some location in the Gualala watershed. Side cast material from road grading can over-steepen slopes, become saturated with water during storms, and trigger a fill failure. In some cases such slides take the rest of the road prism. Photo by Brian McFadin.

References

California Regional Water Quality Control Board (CRWQCB). 2001.  Technical Support Document for the Gualala River Watershed Water Quality Attainment Action Plan for Sediment. CRWQCB, Region 1. Santa Rosa, CA. 147 pp. 

Cedarholm, C.J., L.M. Reid and E.O. Salo. 1981. Cumulative effects of logging road sediment on salmonid populations of the Clearwater River, Jefferson County, Washington. Pages 38-74 in Proceedings of Conference on Salmon Spawning Gravel: A Renewable Resource in the Pacific Northwest? Report 19. Wash. State University, Water Research Center, Pullman, WA.

Flanagan, S.A., M.J. Furniss, T.S. Ledwith, M.A. Love, K. Moore, and J. Ory. 1998. Methods for inventory and environmental risk assessment of road drainage crossings. Water/Road Interaction Technology Series. 9877 1809-SDTDC. USDA Forest Service, Technology and Development Program. San Dimas, CA. 52 pp.

Hagans, D.K., W.E. Weaver and M.A. Madej. 1986. Long term on-site and off-site effects of logging and erosion in the Redwood Creek basin, Northern California. In: Papers presented at the American Geophysical Union meeting on cumulative effects (1985 December); National Council on Air and Streams, Tech. Bull. No. 490, pp.38-66.

Harr, R.D. and R.A. Nichols. 1993. Stabilizing Forest Roads to Help Restore Fish Habitats: A Northwest Washington Example. Fisheries 18(4): 18-22.

Keithley, Chris. California Department of Forestry, Fire and Resources Assessment Project, Sacramento, CA.

Klamath National Forest. In Press. Salmon River Restoration Plan. Klamath National Forest, Yreka, CA in cooperation with Salmon River Restoration Council, Sawyers, Bar, CA. 

Matthews & Associates. 1999 . Sediment source analysis and preliminary sediment budget for the Noyo River. Weaverville, CA. (Contract 68-C7-0018. Work Assignment #0-18.) Prepared for Tetra Tech, Inc. Fairfax, VA.

Morrison, P.H. 1975. Ecological and Geomorphological Consequences of Mass Movements in the Alder Creek Watershed and Implications for Forest Land Management. B.A. Thesis. University of Oregon, Eugene, OR. 102 p.

Weaver, W.E., and D.K. Hagans. 1994. Handbook for Forest and Ranch Roads - A Guide for Planning, Designing, Constructing, Reconstructing, Maintaining and Closing Wildland Roads. Prepared for the Mendocino County Resource Conservation District, Ukiah, California. 161 pp.

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