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EC number: 202-728-6 | CAS number: 99-08-1
- 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
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Justification for type of information:
- Due to insufficient reporting of the experimental details, this study was rated with a Klimisch score of 4 (‘not assignable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- Version: 1984
- Deviations:
- no
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Analytical purity: not specified
- Analytical monitoring:
- yes
- Test organisms (species):
- Daphnia magna
- Test type:
- semi-static
- Water media type:
- freshwater
- Remarks:
- tap water filtrated by activated carbon (pH7.4~7.9, Ca/Mg=3.5~4.l, Na/K=5.5~6.4, hardness 20~32)
- Total exposure duration:
- 48 h
- Test temperature:
- 20 ± 1 °C
- pH:
- 7.4-7.9
- Dissolved oxygen:
- 8-9 ppm
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 14.27 mg/L
- Remarks on result:
- other: ± 2.07 (CV=14.5)
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 9.74 mg/L
- Remarks on result:
- other: ± 1.20 (CV=12.3)
- Details on results:
- CV= coefficient of variation
It is not clearly indicated in the results table, whether the reported results for 3-nitrotoluene were obtained with or without surfactant. - Validity criteria fulfilled:
- not specified
- Executive summary:
Kodoma, 2003
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with OECD TG 202 (1984). The 48h-EC50 value was determined to be 9.74 mg/L and the 48h-LC50 value was reported as 14.27 mg/L. It is not clearly indicated in the results table, whether the reported results for 3-nitrotoluene were obtained with or without surfactant.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- significant methodological deficiencies
- Remarks:
- Basic data given. Restrictions of the method are: - Test period only 4 instead of 48h (represents only 8% of the in the OECD and other current guidelines suggested test period)-Temperature during the test was higher (25 °C) than the one suggested by OECD and other current guidelines (22 °C) - Yeast is not a standard food for Daphnia
- Justification for type of information:
- Due to methodological deficiencies, this study was rated with a Klimisch score of 3 (‘not reliable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87). Despite being considered not reliable (Klimisch 3), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Principles of method if other than guideline:
- not specified
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- purity more than 98%, purchased from E. Merck, Darmstadt, Germany.
- Test organisms (species):
- Daphnia pulex
- Details on test organisms:
- Daphnia (Daphnia pulex) was obtained from Plant Toxicology Department, Taiwan Agricultural Chemicals and Toxic Substances Research Institute, Taichung, Taiwan.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 4 h
- Test temperature:
- 25 ± 1°C
- pH:
- 6.6
- Dissolved oxygen:
- 4.9 mgL/L
- Salinity:
- hardness 215 mg/L as CaCO3
- Details on test conditions:
- Daphnia were fed with yeast in a 224 (diameter) x 46 (height)-cm circular plastic pool. Before the experiment, the test organisms were acclimatized in aquaria for 2 weeks under conditions similar to those under which the tests were performed.
Twenty daphnia, within 24 hr after hatching, were introduced in each 250-mL beaker containing 100 mL of test chemical solution with different concentrations. Adequate
concentrations of 2-nitrotoluene were prepared individually in duplicate for each test chemical. Mortality of daphnia was observed after an incubation period of 4 h. If the appropriate concentration for mortality was beyond the test range, the experiment was carried out once more with a more appropriate concentration. - Duration:
- 4 h
- Dose descriptor:
- LC50
- Effect conc.:
- 84.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Validity criteria fulfilled:
- not specified
- Remarks:
- Restrictions of the method: - Test period only 4 instead of 48h -Temperature during the test was higher (25 °C) than 22 °C - Yeast is not a standard food for Daphnia
- Executive summary:
Yen, 2002: In a short-term toxicity test on Daphnia pulex an LC50 value of 0.845 mg/l after a 4-h exposure period was obtained for 3-nitrotoluene. After request, one of the authors (Wang 2003) communicated that the reported values are below the observed values by a factor of 100. Thus, the correct LC50 is 84.5 mg/l. Despite being considered not reliable (Klimisch 3, Restrictions of the method: - Test period only 4 instead of 48h -Temperature during the test was higher (25 °C) than 22 °C - Yeast is not a standard food for Daphnia), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Remarks:
- Test procedure according to national standards.
- Justification for type of information:
- Due to insufficient reporting of the experimental details, this study was rated with a Klimisch score of 4 (‘not assignable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87)
- Principles of method if other than guideline:
- Method by US-EPA 1975 (EPA-660/3-75-009)
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-Nitrotoluene
- Analytical purity: no data; unknown source - Analytical monitoring:
- yes
- Details on test solutions:
- - Stock solution: The stock solution was prepared by dissolving a measured amount of chemical in a known volume of water.
No carrier was used. The mixing time was about 24 h. The stock solution was filtered through a 5 µm filter and analyzed for the chemical. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The invertebrate species were from stocks reared in the laboratory at SRI International where the study was performed.
No food provided during the test. - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Hardness:
- 33.8 ± 19 mg/L as CaCO3
- Test temperature:
- 20°C
- pH:
- 7.7 ± 0.35
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 28.1 mg/L
- Remarks on result:
- other: 25.3-31.6
- Executive summary:
Liu, 1983
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with US-EPA method 1975 (EPA-660/3-75-009). The 48h-EC50 (mobility) was determined to be 28.1 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Remarks:
- Test procedure in accordance with national standard methods, with acceptable restrictions
- Justification for type of information:
- Due to insufficient reporting of the experimental details, this study was rated with a Klimisch score of 4 (‘not assignable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.' (guidance document How to prepare registration and PPORD dossiers, p. 87)
- Principles of method if other than guideline:
- Protocol of the Dutch Standards Organisation NEN 6501
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-nitrotoluene
- Analytical purity: > 98% - Analytical monitoring:
- not specified
- Details on test solutions:
- synthetic test medium (NPR 6503, 1980)
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- < 24 h old
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Hardness:
- 200 mg/L as CaCO3
- Test temperature:
- 20 ± 0.5
- pH:
- 8.4 ± 0.1
- Dissolved oxygen:
- not less than 7.9 mg/L
- Duration:
- 48 h
- Dose descriptor:
- IC50
- Effect conc.:
- 7.5 mg/L
- Details on results:
- Results expressed as Log IC50=1.74 to show 48-h IC50 in µmol/l to the waterflea, Daphnia magna
- Executive summary:
Deneer et al., (1989) performed a 48-h immobilisation test for D. magna in static test conditions, according to the protocol of the Dutch Standards Organization, NEN 6501 (1980). During the tests, daphnids were fed with Chlorella pyrenidosa, which at the start of the experiments was present at a concentration of 1·108 cells/l. All daphnids used were <24 hours old at the beginning of the experiments. A 48h-LC50 of 7.5 mg/l was determined.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Justification for type of information:
- Due to insufficient reporting of the experimental details, this study was rated with a Klimisch score of 4 (‘not assignable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.' (guidance document How to prepare registration and PPORD dossiers, p. 87)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: OECD proposal (1979)
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-Nitrotoluene
- Analytical purity: > 99.5 % - Analytical monitoring:
- yes
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Details on test conditions:
- closed system due to stability (see details on analytical methods).
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 17.6 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 7.4 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Executive summary:
Canton et al. 1985
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with the OECD proposal (1979). The 48h-EC50 (mobility) was determined to be 7.4 mg/L and the 48h-LC50 was determined to be 17.6 mg/L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Method not validated; test conducted for 24 hs.
- Justification for type of information:
- Due to methodological deficiencies, this study was rated with a Klimisch score of 3 (‘not reliable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87). Despite being considered not reliable (Klimisch 3), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Principles of method if other than guideline:
- 24-hour immobilization test; static method
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-nitrotoluene
- Analytical purity: > 95% - Analytical monitoring:
- no
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- - Daphnids were cultured parthenogenetically in an environmental chamber at 22 ± 1 °C
- Photoperiod of 14 hours daylight, 10 hours darkness
- Daphnids were fed with a diet of green algae
- 6 to 24 hours old daphnids were used for toxicity test - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 24 h
- Test temperature:
- 22 ± 1 °C
- Details on test conditions:
- - 5 replicates for every concentration
- Results were considered valid, when oxygen concentration was > 60 % of saturation, and if immobilization in controls was zero at the end of experiment
- Endpoint: immobilization - Duration:
- 24 h
- Dose descriptor:
- IC50
- Effect conc.:
- 20.8 mg/L
- Basis for effect:
- mobility
- Remarks on result:
- other: observed value
- Validity criteria fulfilled:
- yes
- Remarks:
- - Results were considered valid, when oxygen concentration was > 60 % of saturation, and if immobilization in controls was zero at the end of experiment
- Executive summary:
Zhao, 1995
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 24 h static test. The 24h-IC50 (mobility) was determined to be 20.8 mg/L. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Method not validated; test conducted for 24 hs
- Justification for type of information:
- Due to methodological deficiencies, this study was rated with a Klimisch score of 3 (‘not reliable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87). Despite being considered not reliable (Klimisch 3), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Principles of method if other than guideline:
- other: 24-h immobilization test according to Bringmann G and Kuehn R
- GLP compliance:
- no
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-Nitrotoluol
- Analytical purity: no data - Analytical monitoring:
- no
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 24 h
- Hardness:
- corresponding to 286 mg/l CaCO3
- Test temperature:
- 20-22 °C
- pH:
- 7.6-7.7
- Reference substance (positive control):
- yes
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- 24 mg/L
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- 13 mg/L
- Duration:
- 24 h
- Dose descriptor:
- EC100
- Effect conc.:
- 51 mg/L
- Validity criteria fulfilled:
- not specified
- Executive summary:
Bringmann and Kühn (1982) carried out an acute short test on Daphnia magna. The effects of 3-nitrotoluene were measured on 24-h individuals after 24-h exposure period. Following results are provided: an EC0 of 13 mg/l, an EC50 of 24 mg/l and an EC100 of 51 mg/l. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: Method not validated; test conducted for 24 hs
- Justification for type of information:
- Due to methodological deficiencies, this study was rated with a Klimisch score of 3 (‘not reliable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.’ (guidance document How to prepare registration and PPORD dossiers, p. 87). Despite being considered not reliable (Klimisch 3), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Principles of method if other than guideline:
- other: 24 h-immobilization test according to Bringmann G and Kuehn R
- GLP compliance:
- no
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-Nitrotoluol
- Analytical purity: no data - Analytical monitoring:
- no
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 24 h
- Hardness:
- corresponding to 286 mg/l CaCO3
- Test temperature:
- 20-22 °C
- pH:
- 7.6-7.7
- Duration:
- 24 h
- Dose descriptor:
- LC50
- Effect conc.:
- 35 mg/L
- Duration:
- 24 h
- Dose descriptor:
- LC0
- Effect conc.:
- 11 mg/L
- Duration:
- 24 h
- Dose descriptor:
- LC100
- Effect conc.:
- 88 mg/L
- Validity criteria fulfilled:
- not specified
- Executive summary:
Bringmann and Kühn (1977) carried out an acute short test on Daphnia magna. The effects of 3-nitrotoluene were measured on 24-h individuals after 24-h exposure period. Following results are provided: an LC0 of 11 mg/l, an LC50 of 35 mg/l and an LC100 of 88 mg/l. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- documentation insufficient for assessment
- Justification for type of information:
- Due to insufficient reporting of the experimental details, this study was rated with a Klimisch score of 4 (‘not assignable’). As none of the available studies can serve as a key study with a sufficiently detailed reporting justifying a Klimisch score of 1 or 2 for the given endpoint, several independent sources were used in a weight of evidence approach. ‘Using weight of evidence implies that no single study of sufficient quality and reliability exists, and that information from several independent sources is required to be able to reach a conclusion on a particular property of the substance.' (guidance document How to prepare registration and PPORD dossiers, p. 87)
- Principles of method if other than guideline:
- NEN 6501: Determination of acute toxicity with Daphnia magna (1980) with slight modifications (Van Leeuwen et al. 1985).
48 h-LC50 value and the 95 % confidence interval were calculated according to Litchfield JT and Wilcoxon F (1949). - GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): 3-nitrotoluene
- Analytical purity: > 98 %
- Molecular weight: 137.14 - Analytical monitoring:
- not specified
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- For each concentration, 10 daphnids were used, one animal per jar containing 50 ml medium.
The daphnids were fed on 1x10E+8 cells/L unicellular green algae (C. pyrenidosa). - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 7.5 mg/L
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks on result:
- other: 95% CL; (5.6-10)
- Executive summary:
Maas-Diepeveen and van Leeuwen, 1986
A test on the acute toxicity of 3-nitrotoluene to the invertebrate Daphnia magna was performed according to the Dutch Standardization Organization Method NEN 6501. For a test period of 48 hours an LC50 value of 7.5 mg/l was reported.
Referenceopen allclose all
Measured result was reported to be log 1/IC50 = 3.82, calculated result was reported to be log 1/IC50 = 3.98.
- Effect endpoint: immobilization
- Effect values refer to nominal test substance concentrations
- Effect endpoint: immobilization
- Effect values refer to nominal test substance concentrations
Description of key information
In order to fulfill the data requirements a weight of evidence (WoE) approach (REACh Regulation (EC) No. 1907/2006, Annex XI Section 1.2) was chosen. This approach is a possible adaptation to the standard information requirements which ‘should be undertaken to maximise the use of existing data and minimise the commissioning of new in vivo testing’ (ECHA Guidance R.7a, 2017, p. 364). The WoE approach serves to reduce or avoid animal testing, which should only be performed as last resort (REACh, article 25). The individual study reports were conducted in accordance with standardized guidelines. The study reports nevertheless show some deficiencies with respect to the comprehensiveness of the presented experimental details. Therefore, a reliability of 1 or 2 and thus adequacy as key study was not assignable for any of the individual studies. Consequently, the studies were assigned a Klimisch score of 4 (according to guidance document R.4, ‘not assignable: studies or data […] which do not give sufficient experimental details […]). Collectively, these experimental studies can be used to conclude on this endpoint and to satisfy the information requirement.
Maas-Diepeveen and van Leeuwen, 1986
A test on the acute toxicity of 3-nitrotoluene to the invertebrate Daphnia magna was performed according to the Dutch Standardization Organization Method NEN 6501. For a test period of 48 hours an LC50 value of 7.5 mg/l was reported.
Canton et al. 1985
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with the OECD proposal (1979). The 48h-EC50 (mobility) was determined to be 7.4 mg/L and the 48h-LC50 was determined to be 17.6 mg/L.
Deneer et al., (1989) performed a 48-h immobilisation test for D. magna in static test conditions, according to the protocol of the Dutch Standards Organization, NEN 6501 (1980). During the tests, daphnids were fed with Chlorella pyrenidosa, which at the start of the experiments was present at a concentration of 1·108 cells/l. All daphnids used were <24 hours old at the beginning of the experiments. A 48h-EC50 (immobilization) of 7.5 mg/l was determined.
Liu, 1983
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with US-EPA method 1975 (EPA-660/3-75-009). The 48h-EC50 (mobility) was determined to be 28.1 mg/L.
Yen, 2002
In a short-term toxicity test on Daphnia pulex an LC50 value of 0.845 mg/l after a 4-h exposure period was obtained for 3-nitrotoluene. After request, one of the authors (Wang 2003) communicated that the reported values are below the observed values by a factor of 100. Thus, the correct LC50 is 84.5 mg/l. Despite being considered not reliable (Klimisch 3, Restrictions of the method: - Test period only 4 instead of 48h -Temperature during the test was higher (25 °C) than 22 °C - Yeast is not a standard food for Daphnia), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
Kodoma, 2003
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 48 h study performed in accordance with OECD TG 202 (1984). The 48h-EC50 value was determined to be 9.74 mg/L and the 48h-LC50 value was reported as 14.27 mg/L. It is not clearly indicated in the results table, whether the reported results for 3-nitrotoluene were obtained with or without surfactant.
The results obtained by Zhao et al. (1995) and those obtained by Bringmann et al. (1982, 1977) were included in the WoE approach despite being considered not reliable (Klimisch 3) due to methodological deficiencies. The reported 24-h EC50 values are in the same order of magnitude.
Zhao, 1995
The toxicity of 3-nitrotoluene to the aquatic invertebrate Daphnia magna was evaluated in a 24 h static test. The 24h-IC50 (mobility) was determined to be 20.8 mg/L. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
Bringmann and Kühn (1982) carried out an acute short test on Daphnia magna. The effects of 3-nitrotoluene were measured on 24-h individuals after 24-h exposure period. Following results are provided: an EC0 of 13 mg/l, an EC50 of 24 mg/l and an EC100 of 51 mg/l. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
Bringmann and Kühn (1977) carried out an acute short test on Daphnia magna. The effects of 3-nitrotoluene were measured on 24-h individuals after 24-h exposure period. Following results are provided: an LC0 of 11 mg/l, an LC50 of 35 mg/l and an LC100 of 88 mg/l. This result has been included as additional information. Despite being considered not reliable (Klimisch 3, the exposure time was too short: 24 h instead of the required 48h), the experimental value obtained in this study still supports the WoE conclusion confirming that the EC50 is in the order of magnitude of the concluded key value.
Conclusion
The EC50 and LC50 values obtained from these studies are in a similar order of magnitude.
48h-EC50: 7.4 mg/l - 28.1 mg/L
48h-LC50: 7.5 mg/l - 17.6 mg/L
24h-EC50: 20.8 - 24 mg/L
24h-LC50: 35 mg/l
The most conservative 48h-LC50 value of 7.5 mg/L (Deneer 1989, Maas-Diepeveen 1986) is chosen as key value for assessment.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Dose descriptor:
- LC50
- Effect concentration:
- 7.5 mg/L
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