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KRIS E. Marin Sonoma: Chart Table Page
Area | Novato and Miller Creeks |
Topic | Habitat: Physical Habitat Quality Scores in Miller Creek 2000 |
Caption: The Chart Table inverthab_miller_mcdpw_1999_2002.db is the same as the Source Table, although filtered for the Miller Creek watershed. The metrics included in the table are the mean values for Taxonomic Richness (TAXARICH), Percent Dominant Taxon (PCTDOM), EPT Taxa (EPTTAXA), Modified EPT (MODEPT), Shannon Diversity (SHANNON), and Tolerance Value (TOLVALUE), along with the associated Index of Biological Integrity (IBI) score for each metric as well as the total IBI (IBI_TOTSCORE) and rank (IBIRANK). In addition, EPT Index (EPTINDEX) is also included. The habitat parameters include instream cover (INSTCOV), embeddedness (EMBEDD), velocity/depth (VELDEPTH), sediment deposition (SEDDEP), channel flow (CHANFLOW), channel alteration (CHANALT), riffle frequency (RIFFREQ), bank stability (BANKSTAB), vegetative protection (VEGPROT), riparian vegetative zone width (RIPVEG), total reach score (REACHTOT), condition (CONDITION), percent vegetative canopy cover estimate (VEGCANOP), water temperature in C (WATTEMP), specific conductance in uS/cm at 25 C (SPECCOND), and comments pertinent to the habitat assessment (HABCOMMENTS). Click on Map to view the sampling locations. Data were collected and analyzed by the Sustainable Land Stewardship Institute and provided by the Marin County Department of Public Works.
50 rows of a possible 660 have been displayed.
WATERSHED | LOCATION | SITE | TAXARICH_99 | IBI_TAXARICH_99 | PCTDOM_99 | IBI_PCTDOM_99 | EPTTAXA_99 | IBI_EPTTAXA_99 | MODEPT_99 | IBI_MODEPT_99 | SHANNON_99 | IBI_SHANNON_99 | TOLVALUE_99 | IBI_TOLVALUE_99 | IBI_TOTSCORE_99 | IBIRANK_99 | TAXARICH_00 | IBI_TAXARICH_00 | PCTDOM_00 | IBI_PCTDOM_00 | EPTTAXA_00 | IBI_EPTTAXA_00 | MODEPT_00 | IBIMODEPT_00 | SHANNON_00 | IBI_SHANNON_00 | TOLVALUE_00 | IBI_TOLVALUE_00 | IBI_TOTSCORE_00 | IBIRANK_00 | EPTINDEX_99 | EPTINDEX_00 | COMMENTS | TAXARICH_02 | PCTDOM_02 | EPTTAXA_02 | EPTINDEX_02 | SHANNON_02 | TOLVALUE_02 | INSTRCOV_99 | INSTRCOV_00 | EMBEDD_99 | EMBEDD_00 | VELDEPTH_99 | VELDEPTH_00 | SEDDEP_99 | SEDDEP_00 | CHANFLOW_99 | CHANFLOW_00 | CHANALT_99 | CHANALT_00 | RIFFREQ_99 | RIFFREQ_00 | BANKSTAB_99 | BANKSTAB_00 | VEGPROT_99 | VEGPROT_00 | RIPVEG_99 | RIPVEG_00 | REACHTOT_99 | REACHTOT_00 | CONDITION_99 | CONDITION_00 | VEGCANOP_99 | VEGCANOP_00 | WATTEMP_99 | WATTEMP_00 | SPECCOND_99 | SPECCOND_00 | HABCOMMENTS_99 | HABCOMMENTS_00 |
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Miller Creek | Miller Creek | MC1 | 19 | 1 | 28 | 3 | 5 | 1 | 15 | 1 | 2.2 | 1 | 5.2 | 1 | 8 | poor | 9 | 1 | 42 | 1 | 2 | 1 | 1 | 1 | 1.5 | 1 | 5.6 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 12 | 13 | 14 | 14 | 14 | 11 | 12 | 16 | 5 | 9 | 19 | 17 | 15 | 16 | 18 | 15 | 16 | 13 | 14 | 15 | 139 | 139 | suboptimal | suboptimal | 70 | 65 | 62 | - | 354 | 360 | Stormdrain between riffle 1 and 2; residence on left bank; minimal flow for sampling | stormdrain r-2 |
Miller Creek | Miller Creek | MC2 | 19 | 1 | 29 | 3 | 4 | 1 | 19 | 3 | 2.1 | 1 | 5 | 1 | 10 | poor | 9 | 1 | 53 | 1 | 2 | 1 | 0 | 1 | 1.3 | 1 | 5 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 14 | 18 | 13 | 15 | 15 | 16 | 11 | 10 | 7 | 9 | 18 | 18 | 15 | 17 | 15 | 14 | 16 | 14 | 14 | 14 | 138 | 145 | suboptimal | suboptimal | 70 | 80 | 62 | - | 332 | 340 | Bridge abutments, residences and school within or near riparian zone; minimal flow for sampling | school nearby. stormdrain d/s r-1 |
Miller Creek | Miller Creek | MC3 | 19 | 1 | 30 | 3 | 5 | 1 | 16 | 1 | 2.3 | 3 | 5 | 1 | 10 | poor | 15 | 1 | 53 | 1 | 5 | 1 | 3 | 1 | 1.5 | 1 | 5.1 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | 13 | 15 | 14 | 11 | 14 | 15 | 14 | 13 | 8 | 11 | 18 | 18 | 15 | 12 | 14 | 14 | 14 | 14 | 15 | 16 | 139 | 139 | suboptimal | suboptimal | 85 | 70 | 61 | - | 294 | 310 | Stormdrain on right bank upstream of riffle 1; trails within riparian zone | stormdrain u/s r-5 |
Miller Creek | Miller Creek | MC4 | 23 | 1 | 27 | 3 | 8 | 1 | 11 | 1 | 2.5 | 3 | 5.4 | 1 | 10 | poor | 20 | 1 | 36 | 3 | 12 | 3 | 19 | 3 | 2 | 1 | 4.7 | 1 | 12 | fair | - | - | - | 15 | 37 | 4 | 16 | 1.7 | 5.9 | 17 | 19 | 16 | 14 | 16 | 17 | 13 | 13 | 7 | 10 | 20 | 19 | 17 | 18 | 18 | 18 | 19 | 20 | 18 | 18 | 161 | 166 | optimal | optimal | 50 | 47 | 60 | - | 273 | 280 | Overall good quality site but minimal flow for sampling; samples collected under blackberry vines; recommend frog surveys for this site | - |
Miller Creek | Miller Creek | MC5 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 19 | 1 | 56 | 1 | 10 | 1 | 25 | 3 | 1.6 | 1 | 4.4 | 3 | 10 | poor | - | - | - | 14 | 48 | 2 | 25 | 1.5 | 5.3 | - | 13 | - | 12 | - | 14 | - | 12 | - | 7 | - | 19 | - | 16 | - | 18 | - | 14 | - | 16 | - | 141 | - | suboptimal | - | 17 | - | - | - | 220 | - | stormdrain @ upper end reach |
Miller Creek | Miller Creek | MC6 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 23 | 1 | 37 | 3 | 15 | 3 | 44 | 3 | 2.1 | 1 | 3.6 | 3 | 14 | fair | - | - | - | - | - | - | - | - | - | - | 13 | - | 17 | - | 14 | - | 12 | - | 7 | - | 18 | - | 18 | - | 5 | - | 8 | - | 14 | - | 126 | - | suboptimal | - | 20 | - | - | - | 210 | - | yoy trout. stream dry u/s of bridge @ top of riffle |
Miller Creek | Miller Creek | MC9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 17 | 52 | 7 | 43 | 1.3 | 4.9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
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