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Coastal Watershed Assessment Procedure Guidebook Table of Contents]

The CWAP procedure

The multi-agency round table

The first step of the procedure requires that a round table meeting be organized, attended by the Ministry of Forests district planner, the timber officer or district geoscientist, and the regional hydrologist; and representatives of BC Environment; Department of Fisheries and Oceans (if anadromous fisheries are involved); Ministry of Health (if necessary for a community watershed); and timber, water, and range licensees.

At the first meeting, the watershed management issues of concern should be discussed and clearly defined (such as why this particular watershed assessment is required). Other issues that should be resolved at this meeting include:

The WAP applies to that portion of the watershed above the point of interest (POI). The POI in a community watershed is usually the lowest water intake in that watershed (see Appendix 2). In a fish-bearing stream it is usually the entire reach that contains fish. Once the POI is determined, the watershed above that point is divided into smaller watersheds (sub-basins) according to the guidelines provided in Appendix 2.

The process of having the round table at the outset, identifying all the watershed concerns and defining the sub-drainages of interest, is critical to the success of the entire assessment procedure. Although Appendix 2 provides a suggested method for dividing the watershed into sub-basins and determining the POI, these are only guidelines. The round table can override these guidelines at any time to make them more applicable to specific circumstances.

The watershed should be coded according to its gazetteered name and its unique numeric identifier, using the British Columbia hierarchical watershed coding system.

Level 1 analysis

Level 1 of CWAP involves the collection and collation of data that describe the basic geophysical characteristics of the watershed and the extent and location of harvesting activities in the watershed. Most of the information required can be obtained from a variety of maps—information on topography, soils, bedrock geology and logging history. Level 1 also requires that landslides be counted from the most recent aerial photographs (or from a helicopter survey). Except for the latter requirements, all of the information can be extracted from a geographic information system (GIS).

In the analysis, perform the following tasks:

The sections on “The level 1 analysis procedure” and “Interpretations and recommendations” describe the above process in detail and include forms for recording results.

The 15 impact indicators

  1. Peak flow index (based on elevation-weighted equivalent clearcut area determination)
  2. Road density (used for assessing peak flow changes)
  3. Road density (used for assessing surface erosion)
  4. Density of roads on erodible soils
  5. Density of roads less than 100 m from a stream
  6. Density of stream crossings
  7. Portion of stream logged
  8. Portion of fish stream logged
  9. Portion of mainstem logged
  10. Density of landslides in the watershed
  11. Number of large landslides hitting the mainstem stream
  12. Density of roads on potentially unstable terrain
  13. Percentage of logged, potentially unstable terrain
  14. Density of streams logged on slopes >60%
  15. Density of stream crossings on slopes >60%

Level 2 and 3 analyses

Depending on the results of the level 1 analysis, more detailed analyses (levels 2 or 3) may be required in high hazard watersheds or sub-basins. A level 2 analysis is an overview stream channel assessment performed by an individual with some basic experience in hydrology and/or geomorphology (see the section, “Level 2 watershed assessment,” as well as the Channel Assessment Procedure Guidebook). A level 3 analysis is a very detailed analysis, involving mostly field work. It must be performed by a watershed specialist.

Developing watershed constraints for the forest development plan

The information and interpretations provided by the assessment will be used to identify in which sub-basins certain activities are constrained over the next 5 to 10 years. From this, planning constraints will be developed and applied to the forest development plan.

Examples of the type of recommendations that might be developed are:

It is rare that all resource activity would be restricted everywhere in the watershed, but it is possible that in extremely sensitive, extremely damaged watersheds such restrictions would apply until restoration had occurred.


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