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KRIS Humboldt Bay: Chart Source Table Page
Area | Salmon Creek |
Topic | Aquatic Insects: Pct. Dominant Taxa Salmon Cr, 1994 |
Caption: The Source Table humbugs.dbf was derived from data provided in the draft PALCO HCP and is a subset of Humboldt Bay tributaries only. The column HYDROUNIT refers to PALCO planning units which coincide with real watersheds (i.e. Elk River), CALWATER is the CalWater watershed name and STATION is the name applied in KRIS Coho to the PALCO stations for making graphs. YEAR is the year of the aquatic insect sampling scores. RICHNESS, SIMPSON, HILSENHOFF, DOMINANT and EPTINDEX all refer to metrics using aquatic insects. Click on Info Links for more information on these. HITEMP is the highest temperature recorded at that station. SEDLT85 and SEDLT470 refers to fine sediment less than 0.85 mm and 4.7 mm, respectively. See Sediment Topics for more information or sedtemp.dbf Source Table for more information on station locations (select from drop box at upper left).
50 rows of a possible 271 have been displayed.
HYDROUNIT | CALWATER | STATION | YEAR | RICHNESS | SIMPSON | HILSENHOFF | DOMINANT | EPTINDEX | HITEMP | SEDLT85 | SEDLT470 |
---|---|---|---|---|---|---|---|---|---|---|---|
Elk River | Scout Camp | NF Elk 1 | 1994 | 21 | 0.79 | 2.15 | 30.67 | 14 | 23 | 38 | 63 |
Elk River | Elkhead | LSF Elk 2 | 1994 | 32 | 0.94 | 0.88 | 12.37 | 24 | - | 28 | 40 |
Elk River | Elkhead | LSF Elk 1 | 1994 | 34 | 0.94 | 0.67 | 13 | 23 | - | - | - |
Elk River | Scout Camp | NF Elk 1 | 1995 | 18 | 0.64 | 1.86 | - | - | 20 | - | - |
Elk River | Elkhead | LSF Elk 1 | 1995 | 28 | 0.93 | 1.01 | - | - | - | - | - |
Elk River | Elkhead | LSF Elk 2 | 1995 | 28 | 0.92 | 0.98 | - | - | 14 | - | - |
Elk River | Elkhead | LSF Elk 2 | 1996 | 37 | 0.95 | 0.94 | - | - | - | 22 | 31 |
Elk River | Scout Camp | NF Elk 1 | 1996 | 18 | 0.78 | 1.97 | - | - | 19 | 34 | 60 |
Elk River | Elkhead | LSF Elk 1 | 1996 | 29 | 0.93 | 1.05 | - | - | - | 19 | 28 |
Freshwater Cr | Freshwater Cr | Freshwat 4 | 1994 | 38 | 0.93 | 1.74 | 13 | 21 | - | 18 | 28 |
Freshwater Cr | Camp 12 | Freshwat 2 | 1994 | 31 | 0.93 | 1.57 | 13.71 | 21 | - | 24 | 32 |
Freshwater Cr | Freshwater Cr | Graham 1 | 1994 | 33 | 0.93 | 1.86 | 15.38 | 20 | - | 22 | 37 |
Freshwater Cr | Freshwater Cr | Graham 2 | 1994 | 37 | 0.93 | 1.51 | 13 | 21 | - | 25 | 40 |
Freshwater Cr | Camp 12 | SF Fresh 1 | 1994 | 34 | 0.92 | 1.62 | 20 | 19 | - | 25 | 50 |
Freshwater Cr | Camp 12 | SF Fresh 2 | 1994 | 33 | 0.92 | 1.53 | 21.67 | 21 | - | 22 | 35 |
Freshwater Cr | Freshwater Cr | Freshwat 6 | 1994 | 40 | 0.94 | 1.46 | 13.33 | 26 | - | 25 | 51 |
Freshwater Cr | Camp 12 | Freshwat 3 | 1994 | 34 | 0.92 | 1.79 | 21.36 | 20 | - | 16 | 25 |
Freshwater Cr | Freshwater Cr | Freshwat 5 | 1994 | 35 | 0.94 | 1.63 | 10.33 | 23 | - | 21 | 34 |
Freshwater Cr | Freshwater Cr | Graham 2 | 1995 | 32 | 0.91 | 1.58 | - | - | - | - | - |
Freshwater Cr | Camp 12 | Freshwat 3 | 1995 | 27 | 0.91 | 1.9 | - | - | 17 | - | - |
Freshwater Cr | Freshwater Cr | Freshwat 4 | 1995 | 32 | 0.92 | 1.62 | - | - | 18 | - | - |
Freshwater Cr | Freshwater Cr | Freshwat 6 | 1995 | 40 | 0.92 | 1.58 | - | - | 15 | - | - |
Freshwater Cr | Freshwater Cr | Graham 1 | 1995 | 31 | 0.89 | 1.96 | - | - | 17 | - | - |
Freshwater Cr | Freshwater Cr | Freshwat 5 | 1995 | 29 | 0.91 | 1.25 | - | - | - | - | - |
Freshwater Cr | Camp 12 | Freshwat 2 | 1995 | 31 | 0.89 | 1.94 | - | - | - | - | - |
Freshwater Cr | Camp 12 | SF Fresh 1 | 1995 | 41 | 0.95 | 1.4 | - | - | - | - | - |
Freshwater Cr | Camp 12 | SF Fresh 2 | 1995 | 37 | 0.89 | 1.93 | - | - | 16 | - | - |
Freshwater Cr | Freshwater Cr | Freshwat 6 | 1996 | 30 | 0.91 | 1.63 | - | - | 17 | 23 | 44 |
Freshwater Cr | Eddysville | McCready | 1996 | 29 | 0.89 | 1.44 | - | - | - | 48 | 67 |
Freshwater Cr | Camp 12 | SF Fresh 1 | 1996 | 35 | 0.88 | 1.62 | - | - | - | 26 | 45 |
Freshwater Cr | Freshwater Cr | Graham 2 | 1996 | 25 | 0.88 | 1.45 | - | - | - | 24 | 48 |
Freshwater Cr | Freshwater Cr | Graham 1 | 1996 | 28 | 0.86 | 2.22 | - | - | - | 29 | 49 |
Freshwater Cr | Camp 12 | L Fresh 1 | 1996 | 29 | 0.84 | 2.03 | - | - | - | 39 | 54 |
Freshwater Cr | Freshwater Cr | Freshwat 5 | 1996 | 29 | 0.88 | 2.12 | - | - | - | 25 | 49 |
Freshwater Cr | Freshwater Cr | Freshwat 4 | 1996 | 23 | 0.85 | 1.61 | - | - | - | 20 | 33 |
Freshwater Cr | Camp 12 | Freshwat 3 | 1996 | 28 | 0.91 | 1.8 | - | - | 18 | 15 | 28 |
Freshwater Cr | Camp 12 | Freshwat 2 | 1996 | 32 | 0.87 | 1.83 | - | - | - | 13 | 29 |
Freshwater Cr | Camp 12 | SF Fresh 2 | 1996 | 35 | 0.92 | 1.53 | - | - | - | 25 | 41 |
Salmon Cr | Upper Salmon Cr | Salmon 2 | 1994 | 30 | 0.92 | 0.92 | 17.67 | 21 | - | 18 | 34 |
Salmon Cr | Upper Salmon Cr | Salmon 1 | 1994 | 32 | 0.92 | 1.64 | 16.33 | 20 | - | 41 | 55 |
Salmon Cr | Upper Salmon Cr | Salmon 3 | 1994 | 34 | 0.87 | 1.51 | 26.33 | 25 | - | 43 | 55 |
Salmon Cr | Upper Salmon Cr | Salmon 3 | 1995 | 32 | 0.87 | 2 | - | - | - | - | - |
Salmon Cr | Upper Salmon Cr | Salmon 2 | 1995 | 30 | 0.87 | 0.74 | - | - | - | - | - |
Salmon Cr | Upper Salmon Cr | Salmon 1 | 1995 | 34 | 0.9 | 1.05 | - | - | 15 | - | - |
Salmon Cr | Upper Salmon Cr | Salmon 1 | 1996 | 29 | 0.91 | 1.67 | - | - | - | 26 | 33 |
Salmon Cr | Upper Salmon Cr | Salmon 2 | 1996 | 27 | 0.8 | 0.76 | - | - | - | 26 | 44 |
Salmon Cr | Upper Salmon Cr | Salmon 3 | 1996 | 31 | 0.91 | 1.82 | - | - | - | 46 | 61 |
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