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EC number: 810-394-3 | CAS number: 76326-99-3
- 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 fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- April 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- GLP compliance:
- yes
- Remarks:
- The guidelines of chemical testing good laboratory practices (HJ/T 155)”,
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- other: Gobiocypris rarus
- Details on test organisms:
- The Rare minnow, Gobiocypris rarus was used in the test on the basis of such important practical criteria as, for example, their ready availability throughout the year, ease of maintenance, convenience for testing and any relevant economic, biological or ecological factors. The test species of Rare minnow, Gobiocypris rarus (Batch No.: F20160215G), were obtained from a commercial fish supplier of Institute of Hydrobiology, Chinese Academy of Sciences.
Feeding fry were held at least for 12 days in holding tanks supplied with a continuous flow of aerated water before being used for testing. Fish to be used in the test were held for 7 days in water of the quality and temperature to be used in the test. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- 174 - 181 mg/L CACO3
- Test temperature:
- 22.8 - 23.3 °C
- pH:
- 7.62 - 7.76
- Dissolved oxygen:
- 76 - 95 %
- Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- yes
- Conclusions:
- The results showed that under valid static test conditions, the 96 h-LC50 of Genamin DMG 75 to fish (Rare minnow, Gobiocypris rarus) is greater than the nominal concentration of 100 mg/L (measured water samples concentration was 102 mg/L), while the maximum concentration causing no mortality (96 h-LC0) was equal to the nominal concentration of 100 mg/L (measured water samples concentration was 102 mg/L). i.e.:
96 h-LC50 > 100 mg /L (measured water samples concentration was 102 mg/L);
96 h-LC0 = 100 mg/L (measured water samples concentration was 102 mg/L). - Executive summary:
Under static conditions,the acute toxicity of test substance(Genamin DMG 75)toRare minnow (Gobiocypris rarus)was conductedaccording to:“The guidelines for the testing of chemicals” (HJ/T 153-2004) and“The Guidelines for the Testing of Chemicals-Effects on Biotic Systems” (the 2nd edition.:Environment Press. 2013);with reference toProcedure 203 of the“Guidelines for Testing of Chemicals”of the OECD:“Fish, Acute Toxicity Test” (1992).
A range-finding test and then a limit test were performed respectively. Nominal concentrations of 1.00, 10.0 and 100mg/Lwere used in the range-finding test, while the nominal concentration of100 mg/Lwas used in the limit Test. Water samples taken from the control and the treatments in the limit test (0h, 24h, 48h, 72h & 96h) were analysed.Themean measured concentration of samples was 102mg/L.The analytical results showed that the concentration of the test substance was consistent in the test medium throughout the 96-hour test period(deviation within 20%). Thus a static procedure was reasonable.
In the range-finding test, 5 fish per treatment and no replicates were used. And 7 fishper treatmentwith 3 replicates were used in the limit Test.The testfishwereexposed for 96 hours to the testsolution.
During thelimittestperiod,the pHvaluesof the control mediumsand test mediums werebetween 7.62 and 7.76, the Dissolved Oxygen (DO) values varied from 76 % and 97 % of theair saturationat the test temperature, and the total hardness was in the range of 174 mg (CaCO3)/L to 181 mg (CaCO3)/L. During the test, the temperature of the test mediums were maintained in the range of 22.8 ºC to 23.2 ºC, and all fishes in the control group were normal. With thesameconditions, potassium dichromate (K2Cr2O7)wasused as thepositive controlsubstance, and the resulting 24 h-LC50was327mg/L.So the study met the acceptability criteria prescribed by the protocol and Test Guidelines (The mortality of control ≤ 10%;pH:6.0~8.5; dissolved oxygenconcentration:>60% of the air saturation value;total hardness:10~250 mg(CaCO3)/L; temperature: (23±2) ºC;24 h-LC50ofK2Cr2O7inthe range of 200 to 400 mg/L). Therefore the test was considered valid.
During the test period, all fishin the control groups and treated groupswere alive and appeared normal.The results showed that undervalidstatic test conditions, the 96 h-LC50ofGenamin DMG 75to fish (Rare minnow,Gobiocypris rarus)was greater than the nominal concentration of 100mg/L(measured water samples concentration was 102 mg/L), while the maximum concentration causing no mortality (96 h-LC0) was equal to the nominal concentration of 100mg/L(measured water samples concentration was 102 mg/L). i.e.:
96 h-LC50>100 mg/L(measured water samples concentration was 102 mg/L);
96 h-LC0=100 mg/L(measured water samples concentration was 102 mg/L).
Reference
Description of key information
The results showed that under valid static test conditions, the 96 h-LC50 of Genamin DMG 75 to fish (Rare minnow, Gobiocypris rarus) is greater than the nominal concentration of 100 mg/L (measured water samples concentration was 102 mg/L), while the maximum concentration causing no mortality (96 h-LC0) was equal to the nominal concentration of 100 mg/L (measured water samples concentration was 102 mg/L). i.e.:
96 h-LC50 > 100 mg /L (measured water samples concentration was 102 mg/L);
96 h-LC0 = 100 mg/L (measured water samples concentration was 102 mg/L).
Key value for chemical safety assessment
Additional information
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