Pacific States Marine Fisheries Commission, CalFish 20150529 vector digital data https://wildlife.ca.gov/Data/BIOS https://filelib.wildlife.ca.gov/Public/BDB/GIS/BIOS/Public_Datasets/001_099/ds063.zip The in-stream habitat GIS data included in CalFish consist primarily of those collected by the CDFW extending through most of Humboldt and parts of Mendocino counties. More recent data that was collected between 2010 and 2012 is available for Santa Barbara County. Other departments and organizations actively collect these data and as they become available, will be included in CalFishWHAT EACH RECORD REPRESENTS Each record in this dataset represents in-stream habitat unit level data summarized at the stream reach level. A habitat unit is the base level for the stream habitat surveys and is generally determined by the occurrence of riffle, run and pool sections along the stream. Stream reaches are determined by changes in stream channel type as described by Rosgen (1994). In-stream habitat data include measurements of a variety of physical and aquatic stream attributes that collectively reveal a great deal about stream condition for salmonids and trout. Characterizing and inventorying the physical conditions that define stream habitat for salmonids is an important part of the habitat restoration process. The California Department of Fish and Wildlife (CDFW) collects data on a number of physical attributes of streams and classifies these streams by one of several habitat types. The in-stream habitat data collection process involves two distinct steps; identifying channel type and assigning a habitat type. These in-stream habitat data are used for a variety of purposes including analysis of stream suitability for supporting salmonid populations, as part of larger and more complex watershed assessments, and to establish baseline conditions against which future assessments can measure change. They are a critical part of determining restoration priorities and identifying salmonid refugia. The California Salmonid Stream Habitat Restoration Manual, published by the CDFW, describes the process of using in-stream habitat data and other data and information for identifying streams with restoration potential and working through the stream restoration process. Complete As needed -124.483447 -122.564872 41.772468 38.348108 None aquatic, fish, instream, habitat, hydrologic region, restoration, river, basin, planning, steelhead, stream, surveys, salmonids, coho, Chinook, watershed, Oncorhynchus, kisutch, mykiss, tshawytscha, biota, environment, inlandWaters ISO 19115 Topic Categories biota inlandWaters None California, North Coast, Albion River, Big River, Caspar Creek, Eel River, Gualala River, Eureka Plain, Mad River, Mattole River, Navarro River, Oil Creek, Noyo River, Redwood Creek, Rockport, Russian River, Smith River, Ten Mile River, Trinity River, Van Duzen River, Del Norte County, Humboldt County, Mendocino County, Sonoma County, Trinity County None DATA LIMITATIONS AND ASSUMPTIONS: For analytical purposes, users should assume that data collection methods were similar enough between streams, years, and observers to allow comparison of relative values. Observer bias is presumed low to non-existent. Unit-level in-stream habitat data are designed for suitability assessment of salmonid habitat at fine scales (stream segment). They should not be used for large watershed-level assessment tasks since no sampling designs were established for that purpose. In addition, the shapefiles comprising this data set are a visual representation of the data and have not been calibrated to existing stream data. Therefore spatial errors should be expected. KNOWN CAVEATS OF THE DATA: A significant scaling error often occurs in these data. Some of this error could be from mapping fine-scale ground measurements to a coarser map scale. The average in-stream habitat unit is approximately 55 feet (17 m) long while 1:24,000 scale maps may be accurate to the nearest 90 feet (30m). In most cases, distances measured at a fine scale will exceed measurements at a course scale (Mandelbrot, 1982). With this and other errors, habitat units for some streams may not be accurately placed on the map. Uncertainty of habitat unit placement on the map increases with distance upstream from the starting point. In many cases, the scaling error caused the length of the stream as measured in the surveys to exceed the apparent stream length mapped on the hydrography. For these instances, a scaling factor was applied automatically by the NCNCR 'Stream Habitat' application (contact Karen Wilson, Karen.Wilson@wildlife.ca.gov, for information on this program). Even after application of the scaling factor, instances of the length discrepancy exceeding 1000 feet were found in the data where the surveys covered several miles. Habitat conditions can change drastically both from year to year and within a season. Some of the factors to consider are variable stream flows (especially flood events), temperatures and silt loads. Use of the data with other time-dependent data such as stream biological inventories and salmon carcass surveys must be done with caution.Disclaimer: The State makes no claims, promises, or guarantees about the accuracy, completeness, reliability, or adequacy of these data and expressly disclaims liability for errors and omissions in these data. No warranty of any kind, implied, expressed, or statutory, including but not limited to the warranties of non-infringement of third party rights, title, merchantability, fitness for a particular purpose, and freedom from computer virus, is given with respect to these data. Pacific States Marine Fisheries Commission, CalFish Karen Wilson CalFish Coordinator physical

1487 Sandy Prairie Court, Suite A

Fortuna CA 95540 US 707-725-7191 karen.wilson@wildlife.ca.gov California Department of Fish and Wildlife, Pacific States Marine Fisheries Commission, CalFish Version 6.2 (Build 9200) ; Esri ArcGIS 10.6.1.9270 Vector String 2013 Custom 34.0 40.5 -120.0 0.0 0.0 -4000000.0 coordinate pair 0.000000003754707655900803 0.000000003754707655900803 meter D North American 1983 GRS 1980 6378137.0 298.257222101 ds63 Feature Class ESRI Shape Feature geometry. ESRI Coordinates defining the features. OBJECTID Internal feature number. Esri Sequential unique whole numbers that are automatically generated. SurveyYear Year of survey derived from the SurveyDate field. Used as a sort field to maintain integrity of the symbology used in the viewer. California Salmonid Stream Habitat Restoration Manual, 2010. Stream Stream name according to cdfg 2003 24K stream hydrography layer, unnamed streams are listed as Unnamed Tributary to "stream name". California Salmonid Stream Habitat Restoration Manual, 2010. Basin The basin to which the stream pertains, according to calw221 (Calwater 221). California Salmonid Stream Habitat Restoration Manual, 2010. LLID A unique Identification code for each stream mapped in the routed hydrography layer. It is derived by concatenating the latitude and longitude in degrees, minutes and seconds at the confluence of the stream. California Salmonid Stream Habitat Restoration Manual, 2010. Reach A length of channel uniform with respect to selected habitat characteristics or elements such as discharge, depth, area, slope, population of hydrologic units, fish species composition, water quality, and type and condition of bank cover. Each stream channel type change proceeding upstream is designated by a new stream reach number. California Salmonid Stream Habitat Restoration Manual, 2010. ChannelType channel type as described by Rosgen (1994) and determined using five measured parameters: 1) water slope gradient, 2) entrenchment, 3) width/depth ratio, 4) substrate composition, and 5) sinuosity California Salmonid Stream Habitat Restoration Manual, 2010 A1 Steep, narrow, cascading, step-pool streams; high-energy debris transport associated with depositional soils; very stable bedrock channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly bedrock. XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: Generally not suitable. High energy streams with stable stream banks, and poor gravel retention capabilities. California Salmonid Stream Habitat Restoration Manual, 2010 A2 Steep, narrow, cascading, step-pool streams; high energy/debris transport associated with depositional soils; boulder channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly boulders. XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: Generally not suitable. High energy streams with stable stream banks, and poor gravel retention capabilities. California Salmonid Stream Habitat Restoration Manual, 2010 A3 "Steep, narrow, cascading, step-pool streams; high energy/debris transport with depositional soils; cobble channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly cobble. XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: * Good for bank-placed boulders California Salmonid Stream Habitat Restoration Manual, 2010 A4 "Steep, narrow, cascading, step-pool streams; high energy/debris transport with depositional soils; gravel channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly gravel. XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: * Good for bank-placed boulders California Salmonid Stream Habitat Restoration Manual, 2010 A5 "Steep, narrow, cascading, step-pool streams; high energy/debris transport with depositional soils; gravel channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly sand. XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: * Good for bank-placed boulders California Salmonid Stream Habitat Restoration Manual, 2010 A6 "Steep, narrow, cascading, step-pool streams; high energy/debris transport with depositional soils; silt/clay channel. ENTRENCHMENT: Entrenched < 1.4 GRADIENT: 4-10% SUBSTRATE: Predominantly silt/clay XRATIO: < 12 SINUOSITY: < 1.2 SUITABILITY: * Good for bank-placed boulders California Salmonid Stream Habitat Restoration Manual, 2010 B1 "Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; bedrock channel. ENTRENCHMENT: Moderately Entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly bedrock. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: * Excellent for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 B2 Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; boulder channel. ENTRENCHMENT: Moderately Entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly boulders. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: Excellent for plunge weirs; single and opposing wing-deflectors; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 B3 Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; cobble channel. ENTRENCHMENT: Moderately entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly cobble. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: Excellent for plunge weirs; boulder clusters and bank placed boulder; single and opposing wing-deflectors; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 B4 Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; gravel channel. ENTRENCHMENT: Moderately entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly gravel. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: Excellent for low-stage plunge weirs; boulder clusters; bank placed boulders; single and opposing wing-deflectors; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 B5 "Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; sand channel. ENTRENCHMENT: Moderately entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly sand. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: * Excellent for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 B6 "Moderately entrenched, moderate gradient, riffle dominated channel with infrequently spaced pools; very stable plan and profile; stable banks; silt/clay channel. ENTRENCHMENT: Moderately entrenched 1.4 - 2.2 GRADIENT: 2-4% SUBSTRATE: Predominantly silt/clay. XRATIO: > 12 SINUOSITY: > 1.2 SUITABILITY: * Excellent for bank-placed boulders; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 C1 "Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; bedrock channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly bedrock. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Excellent for bank-placed boulders; and log cover. California Salmonid Stream Habitat Restoration Manual, 2010 C2 Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; boulder channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly boulder. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for plunge weirs; single and opposing wing-deflectors; channel constrictors; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 C3 "Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; cobble channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly cobble. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Excellent for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 C4 "Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; gravel channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly gravel. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 C5 "Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; sand channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly sand. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 C6 "Low gradient, meandering, point-bar, riffle/pool, alluvial channels with broad, well defined floodplain; silt/clay channel. ENTRENCHMENT: Slightly entrenched > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly silt/clay. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 D3 "Multiple channels with longitudinal and transverse bars; very wide channel with eroding banks; cobble channel. ENTRENCHMENT: No entrenchment GRADIENT: < 2% SUBSTRATE: Predominantly cobble. XRATIO: > 40 SINUOSITY: < 1.1 SUITABILITY: * Fair for bank-placed boulders; single and opposing wing deflectors; channel constrictors. California Salmonid Stream Habitat Restoration Manual, 2010 D4 "Multiple channels with longitudinal and transverse bars; very wide channel with eroding banks; gravel channel. ENTRENCHMENT: No entrenchment GRADIENT: < 2% SUBSTRATE: Predominantly gravel. XRATIO: > 40 SINUOSITY: < 1.1 SUITABILITY: * Fair for bank-placed boulders; single and opposing wing deflectors; channel constrictors. California Salmonid Stream Habitat Restoration Manual, 2010 D5 "Multiple channels with longitudinal and transverse bars; very wide channel with eroding banks; sand channel. ENTRENCHMENT: No entrenchment GRADIENT: < 2% SUBSTRATE: Predominantly sand. XRATIO: > 40 SINUOSITY: < 1.1 SUITABILITY: * Fair for bank-placed boulders; single and opposing wing deflectors; channel constrictors. California Salmonid Stream Habitat Restoration Manual, 2010 D6 "Multiple channels with longitudinal and transverse bars; very wide channel with eroding banks; silt/clay channel. ENTRENCHMENT: No entrenchment GRADIENT: < 2% SUBSTRATE: Predominantly sand. XRATIO: > 40 SINUOSITY: < 1.1 SUITABILITY: * Fair for bank-placed boulders; single and opposing wing deflectors; channel constrictors. California Salmonid Stream Habitat Restoration Manual, 2010 DA4 Multiple channels, narrow and deep with expansive well vegetated floodplain and associated wetlands; very gentle relief with highly variable sinuosities; stable stream banks; gravel channel. ENTRENCHMENT: Low to zero entrenchment > 2.2 GRADIENT: < 0.5% SUBSTRATE: Predominantly gravel. XRATIO: < 40 SINUOSITY: 1.1 - 1.6 SUITABILITY: Generally not suitable. California Salmonid Stream Habitat Restoration Manual, 2010 DA5 Multiple channels, narrow and deep with expansive well vegetated floodplain and associated wetlands; very gentle relief with highly variable sinuosities; stable stream banks; sand channel. ENTRENCHMENT: Low to zero entrenchment > 2.2 GRADIENT: < 0.5% SUBSTRATE: Predominantly sand. XRATIO: < 40 SINUOSITY: 1.1 - 1.6 SUITABILITY: Generally not suitable. California Salmonid Stream Habitat Restoration Manual, 2010 DA6 Multiple channels, narrow and deep with expansive well vegetated floodplain and associated wetlands; very gentle relief with highly variable sinuosities; stable stream banks; silt/clay channel. ENTRENCHMENT: Low to zero entrenchment > 2.2 GRADIENT: < 0.5% SUBSTRATE: Predominantly silt/clay. XRATIO: < 40 SINUOSITY: 1.1 - 1.6 SUITABILITY: Generally not suitable. California Salmonid Stream Habitat Restoration Manual, 2010 E3 "Low gradient, meandering riffle/pool stream with low width/depth ratio and little deposition; very efficient and stable; high meander width ratio; cobble channel. ENTRENCHMENT: Slight entrenchment > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly cobble. XRATIO: < 12 SINUOSITY: > 1.5 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 E4 "Low gradient, meandering riffle/pool stream with low width/depth ratio and little deposition; very efficient and stable; high meander width ratio; gravel channel. ENTRENCHMENT: Slight entrenchment > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly gravel. XRATIO: < 12 SINUOSITY: > 1.5 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual 2010 E5 "Low gradient, meandering riffle/pool stream with low width/depth ratio and little deposition; very efficient and stable; high meander width ratio; sand channel. ENTRENCHMENT: Slight entrenchment > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly sand. XRATIO: < 12 SINUOSITY: > 1.5 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 E6 "Low gradient, meandering riffle/pool stream with low width/depth ratio and little deposition; very efficient and stable; high meander width ratio; silt/clay channel. ENTRENCHMENT: Slight entrenchment > 2.2 GRADIENT: < 2% SUBSTRATE: Predominantly silt/clay. XRATIO: < 12 SINUOSITY: > 1.5 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 F1 "Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; very stable if bedrock controlled channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly bedrock. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 F2 Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; boulder channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly boulders. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: Fair for plunge weirs; single and opposing wing deflectors; log cover. California Salmonid Stream Habitat Restoration Manual, 2010 F3 "Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; cobble channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly cobble. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders; single and opposing wing deflectors. California Salmonid Stream Habitat Restoration Manual, 2010 F4 "Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; gravel channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly gravel. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 F5 "Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; sand channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly sand. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 F6 "Entrenched meandering riffle/pool channel on low gradients with high width/depth ratio; silt/clay channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: < 2% SUBSTRATE: Predominantly silt/clay. XRATIO: > 12 SINUOSITY: > 1.4 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual 2010 G1 "Entrenched ""gully"" step-pool and low width/depth ratio on moderate gradient; stable if in a bedrock controlled channel. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly bedrock. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: * Fair for log cover. California Salmonid Stream Habitat Restoration Manual, 2010 G2 Entrenched "gully" step-pool and low width/depth ratio on moderate gradient. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly boulders. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: Fair for log cover. California Salmonid Stream Habitat Restoration Manual, 2010 G3 "Entrenched ""gully"" step-pool and low width/depth ratio on moderate gradient. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly cobble. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 G4 "Entrenched ""gully"" step-pool and low width/depth ratio on moderate gradient. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly gravel. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 G5 "Entrenched ""gully"" step-pool and low width/depth ratio on moderate gradient. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly sand. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 G6 "Entrenched ""gully"" step-pool and low width/depth ratio on moderate gradient. ENTRENCHMENT: Well entrenched < 1.4 GRADIENT: 2-4% SUBSTRATE: Predominantly silt/clay. XRATIO: < 12 SINUOSITY: > 1.2 SUITABILITY: * Good for bank-placed boulders. California Salmonid Stream Habitat Restoration Manual, 2010 Units Number of habitat units in reach. California Salmonid Stream Habitat Restoration Manual, 2010. Length The thalweg length of the habitat unit, in feet. California Salmonid Stream Habitat Restoration Manual, 2010. From_ The downstream (beginning) distance of a habitat unit in terms of distance in feet from the stream confluence. Calculated from cumulative lengths of habitat units. California Salmonid Stream Habitat Restoration Manual, 2010. To_ The upstream (ending) distance of a habitat unit from the confluence of the stream. Calculated from cumulative lengths of habitat units. California Salmonid Stream Habitat Restoration Manual, 2010. StartDate Starting date for reach summary typing California Salmonid Stream Habitat Restoration Manual, 2010. EndDate Ending date for reach habitat typing California Salmonid Stream Habitat Restoration Manual, 2010. Flow Stream flow, in cubic feet of water per second (cfs), measured at the beginning and end of a survey. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_BKVEG Percent of the bank vegetated California Salmonid Stream Habitat Restoration Manual, 2010. DOMBKSUB Dominant bank substrate. California Salmonid Stream Habitat Restoration Manual, 2010. A Silt/Clay California Salmonid Stream Habitat Restoration Manual, 2010. B Sand (<0.08") Bare undercut banks or bedrock ledge. Single piece of large wood (>12 in. diameter and 6 ft. long) defined as large woody debris (LWD). California Salmonid Stream Habitat Restoration Manual, 2010. C Gravel (0.08"-2.5") California Salmonid Stream Habitat Restoration Manual, 2010. D Sm Cobble (2.5-5"). LWD/boulders/root wads. Three or more pieces of LWD combined with SMD. Bubble curtain combined with LWD or boulders. Stable undercut bank with greater than 12 in. undercut, associated with root mass or LWD.Sm Cob California Salmonid Stream Habitat Restoration Manual, 2010. E Lg Cobble (5-10") California Salmonid Stream Habitat Restoration Manual, 2010. F Boulder (>10") California Salmonid Stream Habitat Restoration Manual, 2010. G Bedrock California Salmonid Stream Habitat Restoration Manual, 2010. MEANMAXDEP Mean maximum depth (feet). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_RFL_L Percent riffle by length for reach. Riffles are units having HAB_TYP numbers 1.1-2.2 California Salmonid Stream Habitat Restoration Manual, 2010. PCT_FW_L Percent flat (flat water) by length for reach. Flat are units having HAB_TYP numbers 3.1-3.5 California Salmonid Stream Habitat Restoration Manual, 2010. MW_MEASL Total length (feet) of units that have MEAN_WIDTH measured. California Salmonid Stream Habitat Restoration Manual, 2010. MEAN_WIDTH Average of MEAN_WIDTH weighted by unit length. California Salmonid Stream Habitat Restoration Manual, 2010. TOT_PLS Number of units in reach that are pools. Pools are HAB_TYP numbers 4.1-6.5. California Salmonid Stream Habitat Restoration Manual, 2010. TOT_PLSL Total length (feet) of units in reach that are pools. California Salmonid Stream Habitat Restoration Manual, 2010. PLS_MEAS Number of pool units in reach measured. Measured if MEAN_WIDTH was taken. California Salmonid Stream Habitat Restoration Manual, 2010. PLS_MEASL Number of pool units in reach measured. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_POOL Percent pools by stream length. TotalPoolLength / TotalReachLength * 100. California Salmonid Stream Habitat Restoration Manual, 2010. POOL_FREQ Pool frequency (percent). TotalPools / TotalUnits * 100. California Salmonid Stream Habitat Restoration Manual, 2010. EMBED_L1 Number of pool tails in reach with embeddedness rating 1 (0 to 25%). California Salmonid Stream Habitat Restoration Manual, 2010. EMBED_L2 Number of pool tails in reach with embeddedness rating 2 (26 to 50%). California Salmonid Stream Habitat Restoration Manual, 2010. EMBED_L3 Number of pool tails in reach with embeddedness rating 3 (51 to 75%). California Salmonid Stream Habitat Restoration Manual, 2010. EMBED_L4 Number of pool tails in reach with embeddedness rating 4 (76 to 100%). California Salmonid Stream Habitat Restoration Manual, 2010. EMBED_L5 Number of pool tails in reach with embeddedness rating 5 (unsuitable for spawning). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_EMB1 Percent units in reach with embedded=1 (0 to 25%). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_EMB2 Percent units in reach with embedded=2 (26 to 50%). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_EMB3 Percent units in reach with embedded=3 (51 to 75%). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_EMB4 Percent units in reach with embedded=4 (76 to 100%). California Salmonid Stream Habitat Restoration Manual, 2010. PCT_EMB5 Percent units in reach with embedded=5 (unsuitable for spawning). California Salmonid Stream Habitat Restoration Manual, 2010. NUM_EMBED # units in reach where embedded measured California Salmonid Stream Habitat Restoration Manual, 2010. LSL_PCTL Percent log-formed scour pool habitat by pool length; HAB_TYP number 5.2. California Salmonid Stream Habitat Restoration Manual, 2010. LSR_PCTL Percent rootwad-formed pool habitat by pool length; HAB_TYP number 5.3. California Salmonid Stream Habitat Restoration Manual, 2010. MCP_PCTL Percent main channel pool habitat by pool length; HAB_TYP number 4.1-4.4. California Salmonid Stream Habitat Restoration Manual, 2010. SCL_PCTL Percent scour pool habitat by pool length; HAB_TYP number 5.1-5.6. California Salmonid Stream Habitat Restoration Manual, 2010. BWP_PCTL Percent backwater pool habitat by pool length; HAB_TYP number 6.1-6.5. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_DLT2 Percent residual pool depth < 2 feet. (Count of Pools with resid depth <2ft) / (Count of all pools in which resid depth was measured) * 100. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_DGE2L3 Percent residual pool depth 2 to 2.9 feet. (Count of Pools with resid depth 2 to 2.9ft) / (Count of all pools in which resid depth was measured) * 100. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_DGE3L4 Percent residual pool depth 3 to 3.9 feet. (Count of Pools with resid depth 3 to 3.9ft) / (Count of all pools in which resid depth was measured) * 100. California Salmonid Stream Habitat Restoration Manual, 2010. PCT_DGE4 Percent residual pool depth >= 4 feet. Where resid pool depth = pool depth - depth of pool-tail crest. California Salmonid Stream Habitat Restoration Manual, 2010. NP_DLT2 Number of pools w/ residual pool depth < 2 feet. Where resid pool depth = pool depth - depth of pool-tail crest. California Salmonid Stream Habitat Restoration Manual, 2010. NP_DGE2L3 Number of pools w/ residual pool depth 2 to 2.9 feet. Where resid pool depth = pool depth - depth of pool-tail crest. California Salmonid Stream Habitat Restoration Manual, 2010. NP_DGE3L4 Number of pools w/ residual pool depth 3 to 3.9 feet. Where resid pool depth = pool depth - depth of pool-tail crest. California Salmonid Stream Habitat Restoration Manual, 2010. NP_DGE4 Number of pools w/ residual pool depth >= 4 feet. Where resid pool depth = pool depth - depth of pool-tail crest. California Salmonid Stream Habitat Restoration Manual, 2010. CAN_DENS Canopy density (percent). TotalCanopy / CountTotalCanopy California Salmonid Stream Habitat Restoration Manual, 2010. PCT_CONIF Coniferous component (percent), where percent deciduous + percent coniferous = 100 percent California Salmonid Stream Habitat Restoration Manual, 2010. PCT_DECID Percent of total canopy cover contributed by deciduous trees. California Salmonid Stream Habitat Restoration Manual, 2010. SHLRTN_AVG Mean shelter rating where shelter rating = shelter value * % cover California Salmonid Stream Habitat Restoration Manual, 2010. 0 No shelter California Salmonid Stream Habitat Restoration Manual, 2010. 1 One to five boulders. Bare undercut banks or bedrock ledge. Single piece of large wood (>12 in. diameter and 6 ft. long) defined as large woody debris (LWD). California Salmonid Stream Habitat Restoration Manual, 2010. 2 One or two pieces of (LWD) associated with any amount of small wood (< 12 in. diameter) defined as small woody debris (SWD).Six or more boulders per 50 feet. Stable undercut bank lacking root mass. A single root wad lacking complexity. California Salmonid Stream Habitat Restoration Manual, 2010. 3 Combinations of: (must have at least two cover types): LWD/boulders/root wads. Three or more pieces of LWD combined with SMD. Bubble curtain combined with LWD or boulders. Stable undercut bank with greater than 12 in. undercut, associat California Salmonid Stream Habitat Restoration Manual, 2010. LWD_PCT_P Percent shelter from LWD. Where PCT_COVER has value, multiply PCT_COVER * (PER_LWD/100), then average weighted by length. California Salmonid Stream Habitat Restoration Manual, 2010. DRY_LENGTH Dry length (feet) for reach. California Salmonid Stream Habitat Restoration Manual, 2010. WaterMax Maximum water temperature (degrees F) in reach California Salmonid Stream Habitat Restoration Manual, 2010. WaterMin Minimum water temperature (degrees F) in reach California Salmonid Stream Habitat Restoration Manual, 2010. AirMax Maximum air temperature (degrees F) in reach California Salmonid Stream Habitat Restoration Manual, 2010. AirMin Minimum air temperature (degrees F) in reach California Salmonid Stream Habitat Restoration Manual, 2010. DomBkVeg Dominant bank vegetation California Salmonid Stream Habitat Restoration Manual, 2010. 5 Grass California Salmonid Stream Habitat Restoration Manual, 2010. 6 Brush California Salmonid Stream Habitat Restoration Manual, 2010. 7 Decidous trees California Salmonid Stream Habitat Restoration Manual, 2010. 8 Coniferous trees California Salmonid Stream Habitat Restoration Manual, 2010. 9 No vegetation California Salmonid Stream Habitat Restoration Manual, 2010. DOM_SHELT Dominant shelter from a list of nine types: undercut bank, swd (d<12 inches), lwd (d>12 inches), root mass, terrestrial vegetation, aquatic vegetation, bubble curtain, boulders (d>10 inches) and bedrock ledges. California Salmonid Stream Habitat Restoration Manual, 2010. 0 No shelter. California Salmonid Stream Habitat Restoration Manual, 2010 1 One to five boulders. Bare undercut banks or bedrock ledge. Single piece of large wood (>12 in. diameter and 6 ft. long) defined as large woody debris (LWD). California Salmonid Stream Habitat Restoration Manual, 2010 2 One or two pieces of (LWD) associated with any amount of small wood (< 12 in. diameter) defined as small woody debris (SWD). Six or more boulders per 50 feet. Stable undercut bank lacking root mass. A single root wad lacking complexity. California Salmonid Stream Habitat Restoration Manual, 2010 3 Combinations of: (must have at least two cover types): WD/boulders/root wads. Bubble curtain combined with LWD or boulders. Stable undercut bank with greater than 12 in. undercut, associat California Salmonid Stream Habitat Restoration Manual, 2010 Shape_Length Length of feature in internal units. Esri Positive real numbers that are automatically generated. BFW_MAX Bank Full Width (feet) max in reach California Salmonid Stream Habitat Restoration Manual, 2010. BFW_MIN Bank Full Width (feet) min in reach California Salmonid Stream Habitat Restoration Manual, 2010. BFW_MEAN Bank Full Width (feet) mean in reach California Salmonid Stream Habitat Restoration Manual, 2010. LWD_RIFFLE count of LWD per 100 ft for riffles units in reach California Salmonid Stream Habitat Restoration Manual, 2010. LWD_FLAT count of LWD per 100 ft for pools units in reach California Salmonid Stream Habitat Restoration Manual, 2010. LWD_POOL count of LWD per 100 ft for flat units in reach California Salmonid Stream Habitat Restoration Manual, 2010. PCT_SILTCL % pool tail substrate = silt/clay (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_GRAVEL % pool tail substrate = gravel (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_SMCOBB % pool tail substrate = sm cobble (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_LGCOBB % pool tail substrate = lg cobble (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_BOULDR % pool tail substrate = boulder (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_BEDROC % pool tail substrate = bedrock (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 PCT_SAND % pool tail substrate = sand (in reach) California Salmonid Stream Habitat Restoration Manual, 2010 BFW_STD Bank Full Width standard deviation in reach California Salmonid Stream Habitat Restoration Manual, 2010 20231027 Pacific States Marine Fisheries Commission, CalFish Karen Wilson CalFish Coordinator physical

1487 Sandy Prairie Court, Suite A

Fortuna CA 95540 US 707-725-7191 karen.wilson@wildlife.ca.gov FGDC Content Standard for Digital Geospatial Metadata FGDC-STD-001-1998 local time None