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EC number: 201-818-2 | CAS number: 88-30-2
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1975
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- abstract
- Qualifier:
- no guideline available
- Version / remarks:
- In 1975 no guideline was available
- Principles of method if other than guideline:
- Principle of test: In a static test with 10 concentrations the effect of the test item on the mobility of daphnia magna was tested.
- GLP compliance:
- no
- Remarks:
- Study was conducted in 1975
- Specific details on test material used for the study:
- TFM (39.45 % active ingredient) was used.
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- The test item was measured gravimetrically and diluted with deionized water to prepare stock solutions.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The test organisms were collected in ponds and streams and retained for a minimum of 7 days in water identical with test conditions. Only vigorous individuals of uniform sizes were used in the tests.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- appr. 20 mg/L
- Test temperature:
- 17 °C
- pH:
- 6.8 - 7.0
- Nominal and measured concentrations:
- At least 10 concentrations and 1 water control
- Details on test conditions:
- Test system: The test were conducted in small jars containing 3 liters of test water. The jars were immersed in a water bath to the level of the test fluids; the water bath was equipped with a commercial chilling device.
Effect parameters: Mortality determinations were made on a appropriate basis, and dead organisms were removed after each examination. Mortalities are based on immobility or lack of response of test organisms to various mechanical stimuli.
Test medium: Spring water to which lime was added to bring the total hardness to 20 mg/L. - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 29 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% confidence interval: 21.0 - 41.1 mg/L
- Reported statistics and error estimates:
- The statistical procedures of Litchfield and Wilcoxon (1949) were used to calculate the concentration of toxicant necessary to produce 50% mortality (LC5O's) and to obtain 95% confidence intervals.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In a static test with Daphnia magna the LC50 value after 96 hours was determined to be 29 mg/L.
- Executive summary:
In a static test with 10 concentrations the effect of the test item on the mobility of Daphnia magna was tested. Test medium was spring water with added lime. The LC50 value was determined to be 29 mg/L after 96 hours with a 95 % confidence interval of 21.0 - 41.1 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1975
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- abstract
- Qualifier:
- no guideline available
- Version / remarks:
- In 1975 no guideline available
- Principles of method if other than guideline:
- Principle of test: In a static test the effect of the test item on the mobility of Chironomus tentans was tested.
- GLP compliance:
- no
- Remarks:
- Study was conducted in 1975
- Analytical monitoring:
- no
- Vehicle:
- yes
- Details on test solutions:
- The test item was dissolved in 50 % acetone, total amount of acetone added to each vessel and control was 0.5 mL.
- Test organisms (species):
- other aquatic arthropod: Chironomus tentans
- Details on test organisms:
- TEST ORGANISM
- Source: Stock culture was propagated in the laboratory
- Feeding during test: yes
- Type: The food and substrate mixture consisted of ground Trainers Dog Rewards® (Horlick's Corp., Racine,Wisconsin) and macerated paper hand towels (Crown Zellerback Corp., San Francisco, California).
- Frequency: periodically
- Acclimatisation: yes, for 48 hours
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- 40 - 48 mg/l as CaCO3
- Test temperature:
- 22 ± 1 °C
- pH:
- 7.2 - 7.6
- Nominal and measured concentrations:
- not availabe
- Details on test conditions:
- TEST SYSTEM
- Test vessel: beaker
- Aeration: no
- No. of organisms per vessel: 10 - 20 organisms per beaker
- No. of vessels per concentration (replicates): at least 3
- No. of vessels per control (replicates): at least 3
- Biomass loading rate: 10 - 20 onrganisms per beaker
TEST MEDIUM / WATER PARAMETERS
- Preparation of dilution water: The test water was prepared as characterized by Marking (1970).
EFFECT PARAMETERS MEASURED:
Immobility was noted after 8 24, 48, 72 and 96 hours. - Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.534 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % confidence interval: 0.415 - 0.668
- Reported statistics and error estimates:
- Using the Litchfield and Wilcoxon (1949) method, the EC5O's were calculated from the combined data of at least three independent tests. (The EC50 is defined as the concentration of toxicant, based on total formulation weight, that immobilized 50% of the test organisms within the prescribed period of exposure.) Results of tests in which more than 20% of the control organisms died were discarded. From 114 to 590 animals were used to determine the EC5O's for each chemical or combination of chemicals.
- Validity criteria fulfilled:
- yes
- Conclusions:
- In a static test with Chironomus tentans the LC50 value after 96 hours was determined to be 0.534 mg/L.
- Executive summary:
In a static test the effect of the test item on the mobility of Chironomus tentans was tested. The LC50 value was determined to be 0.534 mg/L after 96 hours with a 95 % confidence interval of 0.415 - 0.688 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1975
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- abstract
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: standard toxicity test (Sanders 1970)
- GLP compliance:
- no
- Remarks:
- Test was conducted in 1975
- Analytical monitoring:
- no
- Vehicle:
- not specified
- Test organisms (species):
- Gammarus sp.
- Details on test organisms:
- TEST ORGANISM
- Common name: Gammarus pseudolimnaeus Bousfield
- Source: collected rom sreams and ponds near the Fish-Pesticide Research Laboratory, Columbia, Missouri
- Feeding during test: no
ACCLIMATION
- Acclimation period: at least 7 days
- Acclimation conditions: same as test conditions - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- 270 mg/L as CaCO3
- Test temperature:
- 21 °C
- pH:
- 7.2 - 7.4
- Nominal and measured concentrations:
- not available
- Details on test conditions:
- TEST MEDIUM / WATER PARAMETERS
- Source of dilution water: water from a deep well
- Reference substance (positive control):
- no
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 22 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks on result:
- other: 95 % confidence interval: 16 - 31 mg/L
- Details on results:
- not available
- Reported statistics and error estimates:
- The LC50 values were calculated on the basis of the total formulation. Toxic effects were measured in terms of the median lethal concentration (LC50), the toxicant concentration in water which is lethal to 50% of the test animals under the test conditions. Toxicity estimates (LC50 values) and corresponding 95% confidence intervals were determined by the Litchfield Wilcoxon method (1949).
- Validity criteria fulfilled:
- yes
- Conclusions:
- In a static test with Gammarus pseudolimnaeus the LC50 value after 96 hours was determined to be 22 mg/L.
- Executive summary:
In a static test the effect of the test item on the mortality of Gammarus pseudolimnaeus was tested. The LC50 value was determined to be 22 mg/L after 96 hours with a 95 % confidence interval of 16 - 31 mg/L.
Referenceopen allclose all
Description of key information
Daphnia magna: LC50 (96 hours): 29 mg/L
Chironomus tentans: LC50 (96 hours): 0.534 mg/L
Gammarus pseudolimnaeus: LC50 (96 hours): 22 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.534 mg/L
Additional information
As the test item is registered since 1964 for limited use in tributaries of the Great Lakes in the US for control of the parasitic sea lamprey, numerous studies on aquatic invertebrates are available. Only the most important studies are presented here: The test with the lowest LC50 (Chironomus tentans) and two standard species for the endpoint (Daphnia magna and Gammarus pseudolimnaeus). No guidelines were available in 1975 and in the publications the description of the methods are insufficient. But as all results are in the same range (LC50: 0.5 – 29 mg/L) they are considered valid. Additionally they match with the data given in the RED document of the test item of EPA (Reregistration Eligibility Decision, United States Environmental Protection Agency, November 1999, 7508C) where a LC50 of 3.8 - 22.3 mg/L is given.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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