Water-quality data from 2002 to 2003 and analysis of data gaps for development of total maximum daily loads in the lower Klamath River basin, CaliforniaDIANE Publishing |
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Page 1
... salmonid or sucker health because of occasional high water temperatures, low dissolved oxygen, and condi- tions that supported abundant populations of algae and aquatic plants. The results were also used to assess gaps in data by ...
... salmonid or sucker health because of occasional high water temperatures, low dissolved oxygen, and condi- tions that supported abundant populations of algae and aquatic plants. The results were also used to assess gaps in data by ...
Page 7
... salmonid populations occurs at levels of 4.25 mg / L or less , with initial oxygen distress occurring at 6 mg / L ( Davis , 1975 ) and chronic stress occurring at 7 mg / L ( Campbell , 1995 ) . The water - quality objectives for salmonids ...
... salmonid populations occurs at levels of 4.25 mg / L or less , with initial oxygen distress occurring at 6 mg / L ( Davis , 1975 ) and chronic stress occurring at 7 mg / L ( Campbell , 1995 ) . The water - quality objectives for salmonids ...
Page 8
... salmonid stress ( 21 ° C ) Chronic salmonid stress ( 16 ° C ) Figure 3. Water temperatures at continuous monitoring stations along the Klamath River in the Lower Klamath River Basin , California . A , 2002. B , 2003 . 987654 5/01 ...
... salmonid stress ( 21 ° C ) Chronic salmonid stress ( 16 ° C ) Figure 3. Water temperatures at continuous monitoring stations along the Klamath River in the Lower Klamath River Basin , California . A , 2002. B , 2003 . 987654 5/01 ...
Page 9
... salmonid stress ( 4.25 mg / L ) Chronic salmonid stress ( 7 mg / L ) ORLEANS SEIAD IRONGATE SHOVEL Figure 4. Dissolved oxygen at continuous monitoring stations along the Klamath River in the Lower Klamath River Basin , Cali- fornia . A ...
... salmonid stress ( 4.25 mg / L ) Chronic salmonid stress ( 7 mg / L ) ORLEANS SEIAD IRONGATE SHOVEL Figure 4. Dissolved oxygen at continuous monitoring stations along the Klamath River in the Lower Klamath River Basin , Cali- fornia . A ...
Page 10
... salmonid stress ( 21 ° C ; 4.25 mg / L ) Chronic salmonid stress ( 16 ° C ; 7 mg / L ) Figure 5. Measurements of ( A ) water temperature and ( B ) dissolved oxygen at continuous water - quality monitoring stations along the Shasta River ...
... salmonid stress ( 21 ° C ; 4.25 mg / L ) Chronic salmonid stress ( 16 ° C ; 7 mg / L ) Figure 5. Measurements of ( A ) water temperature and ( B ) dissolved oxygen at continuous water - quality monitoring stations along the Shasta River ...
Common terms and phrases
air temperature algal Alkalinity ARCATA biofouling calibration California chlorophyll-a Climatic Data Center concentrations constituents continuous monitoring CREEK Data Center NCDC data collected data gaps degrees Celsius discharge Dissolved oxygen Dissolved Oxygen Data diurnal Doyle EDGEWOOD evaluate EXPLANATION flow Grenada HATFIELD station HOOPA Horizontal coordinate information HWY3 information is referenced Iron Gate Dam IRONGATE July Klamath River Basin KLAMATH station locations Lost River Lower Klamath River mathematical model maximum measured meters mg/L microsiemens per centimeter milligrams milligrams per liter MONTAGUE Monthly water-quality sampling National Climatic Data NHO,N nutrients Oregon organic nitrogen orthophosphate percent pheophytin-a phosphorus processes river system salmonid sediment oxygen demand SEIAD ORLEANS sensor September 2002 Shasta River simulate SOD rate Specific conductance Station ID Station name stream Table tion TMDLs Total organic carbon total phosphorus Trinity River Tualatin River Tule Lake TULE station U.S. Geological Survey Upper Klamath Lake upstream USGS Water-quality data YREKA µg/L
Popular passages
Page vi - Celsius (p,S/cm at 25°C). Concentrations of chemical constituents in water are given either in milligrams per liter (mg/L) or micrograms per liter (цд/L).
Page vi - Horizontal coordinate information is referenced to the North American Datum of 1983 (NAD 83). Altitude, as used in this report, refers to distance above the vertical datum.
Page 29 - ... within the lake or reservoir. A desired goal for the prevention of plant nuisances in streams or other flowing waters not discharging directly to lakes or impoundments is...
Page 29 - BIOSTIMULATORY SUBSTANCES Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses.
Page 47 - OREGON. Dissolved oxygen in the Tualatin River, Oregon, during winter flow conditions, 1991 and 1992, by VJ Kelly. Prepared in cooperation with Unified Sewerage Agency of Washington County.
Page 46 - Bothwell, ML (1989) Phosphorus-limited growth dynamics of lotie periphyton diatom communities: areal biomass and cellular growth rate responses.
Page 47 - Flint, AL, and Childs, SW, 1987, Calculation of solar radiation in mountainous terrain: Journal of Agricultural and Forest Meteorology, v. 40, p. 233-249.
Page 25 - California, 1997-2000 [Number below the compound is the data parameter code, which is a 5-digit number used in the US Geological Survey computerized data system, National Water Information System (NWIS), to uniquely identify a specific constituent or property; ft...
Page 46 - Chemical and isotopic evidence of nitrogen transformation in the Mississippi River, 1997-98: Hydrological Processes, v.
Page 47 - Cole, TM, and Wells, SA, 2002, CE-QUAL-W2: A twodimensional, laterally averaged, hydrodynamic water-quality model, version 3.1.