Category |
Code |
Description |
Source |
Reference |
Active
|
Alias
|
ANALYSIS
|
CLP-ILM05.3
|
Inorganic Analysis (Metals, Including Mercury and Cyanide), Multi-Media, Multi-Concentration by ICP-AES, ICP-MS, CVAA, and colorimetry. Includes percent solids. EPA Contact Lab Program (CLP), ILM05.3
|
|
U.S. EPA, 2004. Contract Laboratory Program, Multi-Media, Multi-Concentration Inorganic Analysis, Office Superfund Remediation and Technology Innovation, Analytical Services Branch, January 2004.
|
Y
|
CLPILM05.3
|
Preparation
|
CLP-ILM04-ACIDPREP-S
|
Acid Digestion Procedure for ICP, Flame AA and Furnace AA Analyses in Soils and Sediments
|
|
U.S. EPA, 1995. Contract Laboratory Program Statement of Work for Inorganic Analysis, Multi-Media, Multi-Concentration, Version ILM04.0.
|
Y
|
|
ANALYSIS
|
CLP-ILM04
|
Inorganic Analysis, Multi-Media, Multi-Concentration, EPA Contract Lab Program (CLP) ILM04.0
|
|
U.S. EPA, 1995. Contract Laboratory Program Statement of Work for Inorganic Analysis, Multi-Media, Multi-Concentration, Version ILM04.0.
|
Y
|
|
ANALYSIS
|
CLP-ILM03
|
Inorganic Analysis, Multi-Media, Multi-Concentration, EPA Contract Lab Program (CLP) ILM03.0
|
|
U.S. EPA, 1992. Contract Laboratory Program Statement of Work for Inorganic Analysis, Multi-Media, Multi-Concentration, Version ILM03.0
|
Y
|
|
ANALYSIS
|
CLP-DLM02.0
|
Dioxins and Furans Analysis, Multi-Media, Multi-Concentration, EPA Contract Lab Program (CLP), DLM02.0
|
|
U.S. EPA, 2005. Contract Laboratory Program, Multi-Media, Multi-Concentration Dioxin and Furan Analytical Service for Superfund (DLM02.0), EPA Publication 540-F-05-003, September 2005.
|
Y
|
CLPDLM02.0
|
ANALYSIS
|
CLP-DIO-LO
|
Dissolved Inorganics, Low Concentration, EPA Contract Lab Program (CLP)
|
|
U.S. EPA, Contract Laboratory Program Statement of Work for Inorganic Analysis, Multi-Media, Multi-Concentration, ILM0x.x
|
Y
|
|
ANALYSIS
|
CLP-DIO
|
Dissolved Inorganics, EPA Contract Lab Program (CLP)
|
|
U.S. EPA, Contract Laboratory Program Statement of Work for Inorganic Analysis, Multi-Media, Multi-Concentration, ILM0x.x
|
Y
|
|
ANALYSIS
|
CHEM-K6203
|
Iron, Ferrous, in water by CHEMetrics K6203 field kit, 1,10 Phenanthroline Method, Vacu-vial ampoule, adapted from Standard Methods SM3500FeB
|
|
CHEMetrics, Inc., 4295 Catlett Road, Calverton, VA 20138, 800-356-3072, http://www.chemetrics.com/
|
Y
|
|
MEASUREMENT
|
CHELS-AQUA
|
UV AQUAtracka Submersible PMT Flourimeter for Hydrocarbon (360nm) or Gelbstoff (440nm) concentrations.
|
|
Chelsea Technologies Group, Surrey, UK, +44 (0)20 8481 9000, http://www.chelsea.co.uk.
|
Y
|
|
ANALYSIS
|
CEC-THOMAS
|
Cation Exchange Capacity of Soils (Ammonium Acetate)
|
|
Thomas, G.W. 1982. Exchangeable cations. In: A.L. Page et al. (Ed.) Methods of soil analysis, Part 2, 2nd Ed, pp. 159-165. Agronomy Monograph No. 9. American Society of Agronomy, Madison, WI.
|
Y
|
|
Analysis
|
CAS-MET-TISP-FD-TS
|
Freeze-drying tissue for total solids determination, Columbia Analytical Services
|
|
Standard Operating Procedure for Tissue Sample Preparation, SOP No. MET-TISP, Columbia Analytical Services, 2007
|
Y
|
|
PREPARATION
|
CAS-MET-TISP-FD
|
Freeze-drying for tissue analyses, Columbia Analytical Services
|
|
Standard Operating Procedure for Tissue Sample Preparation, SOP No. MET-TISP, Columbia Analytical Services, 2007
|
Y
|
|
Analysis
|
Carter2011-DI-IRMS
|
Dual-inlet isotope ratio mass spectrometry (DI-IRMS)
|
|
J. F. Carter and V. J. Barwick (Eds), Good practice guide for isotope ratio mass spectrometry, FIRMS (2011). ISBN 978-0-948926-31-0.
|
Y
|
|
Analysis
|
CARB435-17-M
|
California Air Resources Board Test Method 435 - Determination of Asbestos Content of Serpentine Aggregate, V2017, modified method.
|
|
California Air Resource Board, Monitoring and Laboratory Division, April 2017 https://ww2.arb.ca.gov/resources/documents/test-method-435
|
Y
|
|
Analysis
|
CAM SOP-00445/6
|
Determination of Moisture Content in Solids by Gravimetry, Maxxam Analytics SOP, September 22, 2011.
|
|
Maxxam Analytics Inc, Burnaby BC Canada, September 22, 2011. Based on Soil Sampling and Methods of Analysis. Canadian Society of Soil Science. Martin R. Carter 1993. Chapter 51: Soil Water Content. Pg 542-543
|
Y
|
|
Derivation
|
CALCNH3UN
|
Is calcualted from NH4, pH and Temperature.
|
|
|
Y
|
|
Derivation
|
CALC_IRON
|
Ferric Iron by calculation (Total Iron – Ferrous Iron)
|
|
|
Y
|
|
Derivation
|
CALC_FLOW
|
Streamflow by calculation.
|
|
|
Y
|
|
Derivation
|
CALC-FLOW-VOLUME
|
Total volume of flow over time
|
|
|
Y
|
|
Derivation
|
CALC-351.2-350.1
|
Ammonia or Organic Nitrogen calculated via Total Kjeldahl Nitrogen by EPA351.2 (Semiautomated Colorimetry) and Ammonia by EPA350.1 (Nitrogen as Ammonia, Colorimetric, Automated Phenate)
|
|
|
Y
|
|
Measurement
|
CAL-FLOW
|
Flow by The California Pipe Method of Water Measurement
|
|
Vanleer, B.R., The California Pipe Method of Water Measurement, Engineering News Record, August 3, 1922, and August 21, 1924.
|
Y
|
|
COLLECTION
|
BUGBAG500UM
|
Benthic macroinvertebrate collection by placing rock bags instream for colonization over a period of time. Samples are sifted through a 500 um mesh net.
|
|
|
Y
|
|
Collection
|
BottomTrawl
|
Fish collection by dragging a net along the bottom. Also known as benthic trawling.
|
|
|
Y
|
|
Collection
|
BOTTLEDIPTRANS
|
Bottle dip and transfer to individual sample bottles to fill, type unspecified
|
|
|
Y
|
|
COLLECTION
|
BOTTLEDIP
|
Bottle, direct dip/fill, type unspecified
|
|
|
Y
|
|
COLLECTION
|
BONGONET1
|
Plankton net, paired Bongo, 0.1 m2
|
|
|
Y
|
|
ANALYSIS
|
BOD5INH
|
Inhibited Biochemical Oxygen Demand (BOD)
|
Ecology-MEL
|
|
Y
|
|
ANALYSIS
|
BOD5
|
Biochemical Oxygen Demand (BOD) 5 day test
|
|
|
Y
|
|
ANALYSIS
|
BLIGHDYER59
|
Rapid method of total lipid extraction and purification, Bligh and Dyer, 1959
|
|
Bligh, E.G. and Dyer, W.J. A rapid method of total lipid extraction and
purification. Can. J. Biochem. Physiol. 37: 911-917, 1959.
|
Y
|
|
Analysis
|
BIOO-ELISA-1034-01
|
Saxitoxin (Paralytic Shellfish Poisons) by BIOO MaxSignal Enzyme-Linked Immunoabsorbent Assay (ELISA) Test Kit (1034-01)
|
|
Bioo Scientific Corp., 3913 Todd Lane Suite 312, Austin, TX, 1-888-208-2246, http://www.biooscientific.com
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric053
|
Number of taxa in the sample that produces a single generation per year
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric052
|
Number of Trichoptera Taxa present in the sample
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric051
|
Total number of taxa present in the sample
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric050
|
The number of taxa in the sample represented by organisms that can control the speed and direction of movement in the water column.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric049
|
The percent of the sample represented by organisms that can control the speed and direction of movement in the water column.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric048
|
The percent of organisms in the sample that have a pollution tolerance value greater than 8 (Klemm et al 2002).
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric047
|
Measures diversity by reporting the chance that any two randomly drawn individuals from a sample are the same species. This measure is heavily influenced by relative abundance of each taxa. The measure scores between 0 and 1, with a more diverse community reflected by a score close to 1.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric046
|
Compares diversity by accounting for both richness and evenness of the sample. Generally this metric scores between 0 and 4.5. A higher score represents higher diversity. It is not used to compare sites, however since it is affected by changes in both the number of taxa and the relative abundance of those taxa.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric045
|
Compares diversity by accounting for both richness and evenness of the sample. Generally this metric scores between 0 and 4.5. A higher score represents higher diversity. It is not used to compare sites, however since it is affected by changes in both the number of taxa and the relative abundance of those taxa.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric044
|
Number of taxa in the sample that requires more than a year to complete one generation
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric043
|
Number of organisms in the sample that are tolerant to perturbation
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric042
|
Percent of organisms tolerant of perturbation
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric041
|
Number of organisms in the sample that are sensitive to perturbation
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric040
|
Percent of organisms that are sensitive to perturbation
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric039
|
The percent of the sample represented by organsims that feed on attached periphyton (Scrapers) and organisms that feed on coarse organic matter from the substrate.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric038
|
The ratio of organisms that feed on attached periphyton (Scrapers) to the number of Scrapers and Filterers (organisms that feed by filtering organic matter from the water column) combined.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric037
|
The ratio of organsims that feed on attached periphyton (Scrapers) to the number of organisms that feed by filtering organic matter from the water column (Filterers).
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric036
|
The number of taxa in the sample representing organisms that consume other organisms
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric035
|
The percent of the sample made up of organisms that consume other organsims.
|
|
|
Y
|
|
MEASUREMENT
|
BIOHabitatMetric034
|
Percent of organisms considered to be tolerant of various types of perturbation
|
|
|
Y
|
|
1504 records
|