Area/Topic | Bibliography | Background | Hypotheses | Home |
KRIS E. Marin Sonoma: Chart Table Page
Area | Corte Madera Creek |
Topic | Aquatic Insects: Percent Dominant Taxon in Corte Madera Cr 1999-2002 |
Caption: The Chart Table inverthab_cm_mcdpw_1999_2002.db is the same as the Source Table, although filtered for the Corte Madera 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 63 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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Corte Madera Creek | Corte Madera Creek | CM1 | 17 | 1 | 36 | 3 | 3 | 1 | 1 | 1 | 2 | 1 | 5.5 | 1 | 8 | poor | 12 | 1 | 74 | 1 | 2 | 1 | 0 | 1 | 1 | 1 | 5.4 | 1 | 6 | poor | 13 | 2 | - | 16 | 51 | 3 | 8 | 1.4 | 6.7 | 8 | 8 | 12 | 11 | 9 | 9 | 5 | 8 | 5 | 8 | 11 | 14 | 8 | 14 | 16 | 17 | 17 | 16 | 13 | 13 | 104 | 116 | suboptimal | suboptimal | 32 | 43 | 16 | 15 | - | 330 | - | - |
Corte Madera Creek | Corte Madera Creek | CM2 | 17 | 1 | 34 | 3 | 4 | 1 | 7 | 1 | 2 | 1 | 5.6 | 1 | 8 | poor | 15 | 1 | 48 | 1 | 7 | 1 | 5 | 1 | 1.6 | 1 | 5.2 | 1 | 6 | poor | 10 | 18 | - | 12 | 43 | 1 | 43 | 1.5 | 5.8 | 7 | 10 | 12 | 12 | 7 | 14 | 9 | 9 | 7 | 10 | 6 | 6 | 3 | 5 | 16 | 18 | 9 | 10 | 6 | 6 | 82 | 100 | marginal | marginal | 78 | 63 | 15 | 15 | - | 370 | - | r-2 under bridge abutment |
Corte Madera Creek | Ross Creek | CM3 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 21 | 1 | 37 | 3 | 7 | 1 | 11 | 1 | 2.1 | 1 | 5.3 | 1 | 8 | poor | - | 23 | - | - | - | - | - | - | - | - | 17 | - | 12 | - | 15 | - | 18 | - | 9 | - | 20 | - | 17 | - | 18 | - | 16 | - | 19 | - | 161 | - | optimal | - | 72 | - | 16 | - | 162 | - | reach may be missing sand substrate |
Corte Madera Creek | Billy Williams Creek | CM3b | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 30 | 3 | 23 | 3 | 18 | 3 | 44 | 3 | 2.6 | 3 | 3.7 | 3 | 18 | good | - | 64 | - | - | - | - | - | - | - | - | 14 | - | 18 | - | 15 | - | 17 | - | 6 | - | 20 | - | 17 | - | 18 | - | 18 | - | 20 | - | 163 | - | optimal | - | 77 | - | 11 | - | 155 | - | Pacific giant salamander |
Corte Madera Creek | San Anselmo Creek | CM4 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 20 | 1 | 53 | 1 | 9 | 1 | 4 | 1 | 1.7 | 1 | 5.3 | 1 | 6 | poor | - | 12 | - | 9 | 49 | 1 | 4 | 1.3 | 5.8 | - | 15 | - | 14 | - | 15 | - | 14 | - | 14 | - | 15 | - | 6 | - | 11 | - | 13 | - | 7 | - | 124 | - | suboptimal | - | 42 | - | 13 | - | 188 | - | sculpin. stormdrain under u/s r-3 |
Corte Madera Creek | Sleepy Hollow Creek | CM5 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 11 | 1 | 43 | 1 | 2 | 1 | 1 | 1 | 1.5 | 1 | 5.3 | 1 | 6 | poor | - | 7 | - | - | - | - | - | - | - | - | 15 | - | 13 | - | 15 | - | 15 | - | 11 | - | 15 | - | 14 | - | 14 | - | 16 | - | 10 | - | 138 | - | suboptimal | - | 48 | - | 13 | - | 358 | - | - |
Corte Madera Creek | Sleepy Hollow Creek | CM6 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 9 | 1 | 61 | 1 | 2 | 1 | 1 | 1 | 1.2 | 1 | 5.4 | 1 | 6 | poor | - | 8 | - | - | - | - | - | - | - | - | 13 | - | 12 | - | 13 | - | 12 | - | 7 | - | 9 | - | 11 | - | 15 | - | 13 | - | 6 | - | 111 | - | suboptimal | - | 60 | - | 14 | - | 520 | - | low water. filamentous algae. 4 stormdrains in reach. R-3 under house |
Corte Madera Creek | Sleepy Hollow Creek | CM7 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 17 | 1 | 64 | 1 | 9 | 1 | 11 | 1 | 1.5 | 1 | 4.8 | 1 | 6 | poor | - | 18 | - | 17 | 51 | 5 | 34 | 1.5 | 4.9 | - | 15 | - | 12 | - | 14 | - | 14 | - | 7 | - | 10 | - | 11 | - | 14 | - | 15 | - | 9 | - | 121 | - | suboptimal | - | 47 | - | 12 | - | 347 | - | - |
Corte Madera Creek | Sleepy Hollow Creek | CM7b | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 18 | 1 | 40 | 1 | 10 | 1 | 50 | 5 | 1.9 | 1 | 3.6 | 3 | 12 | fair | - | 86 | - | 18 | 52 | 3 | 26 | 1.6 | 5.1 | - | 8 | - | 12 | - | 11 | - | 17 | - | 12 | - | 19 | - | 17 | - | 16 | - | 19 | - | 14 | - | 145 | - | suboptimal | - | 37 | - | 13 | - | 307 | - | algae. minimal flow. wild bamboo. scotch/franch broom. |
Corte Madera Creek | San Anselmo Creek | CM8 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 24 | 1 | 27 | 3 | 12 | 3 | 34 | 3 | 2.4 | 3 | 4.2 | 1 | 14 | fair | - | 42 | - | 14 | 44 | 5 | 39 | 1.4 | 5.2 | 12 | 9 | 14 | 17 | 12 | 13 | 7 | 5 | 7 | 8 | 14 | 12 | 14 | 15 | 16 | 16 | 14 | 16 | 14 | 10 | 124 | 121 | suboptimal | suboptimal | 53 | 47 | 15 | 13 | - | 276 | sculpin in r-4, many yoy fingerling | heavy sediment behind dam. yoy trout. sculpin. riffle sculpin. |
Corte Madera Creek | San Anselmo Creek | CM8b | 18 | 1 | 42 | 1 | 4 | 1 | 12 | 1 | 1.9 | 1 | 4.9 | 1 | 6 | poor | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 15 | - | CM-8 excluded transects 4 and 5 from CRT, mean, and CV calculations. | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Corte Madera Creek | Cascade Creek | CM9 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 13 | 1 | 40 | 1 | 12 | 3 | 77 | 5 | 2 | 1 | 2.1 | 5 | 16 | fair | - | 80 | - | - | - | - | - | - | - | - | 16 | - | 16 | - | 16 | - | 14 | - | 11 | - | 17 | - | 14 | - | 13 | - | 16 | - | 11 | - | 144 | - | suboptimal | - | 63 | - | 15 | - | 265 | - | - |
Corte Madera Creek | Cascade Creek | CM10 | - | - | - | - | - | - | - | - | - | - | - | - | - | - | 27 | 3 | 18 | 3 | 17 | 3 | 44 | 3 | 2.7 | 3 | 3 | 5 | 20 | good | - | 64 | - | - | - | - | - | - | - | 12 | 17 | 18 | 17 | 11 | 15 | 17 | 18 | 4 | 8 | 20 | 19 | 18 | 16 | 15 | 17 | 15 | 18 | 18 | 19 | 148 | 164 | suboptimal | optimal | 90 | 77 | 14 | 12.5 | - | 305 | spotsampled due to possible steelhead habitat | - |
www.krisweb.com |