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EC number: 205-766-1 | CAS number: 150-68-5
- 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:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Principles of method if other than guideline:
- no method provided
- GLP compliance:
- no
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Mugil cephalus
- Test type:
- not specified
- Water media type:
- not specified
- Remarks:
- Most likely saltwater sine this is a marine species
- Total exposure duration:
- 48 h
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 16.3 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Mugil cephalus 48-h LC50: 16.3 mg/L
- Executive summary:
According to Butler (1965; cited in US-EPA document EPA-504 -1 -75 -028 ; 1975, page 53) Monuron has an acute toxicity (48 -h LC50) to striped mullet (Mugil cephalus) of 16.3 mg/L
Further details were not reported. Since this information is obtained form a peer reviewed document from an international accepted authority the result is considered reliable with restrictions for the further assessment.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Principles of method if other than guideline:
- no method provided
- GLP compliance:
- no
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- other: Coho salmon; channel catfish, largemouth bass, smallmouth bass, bluegill, green sunfish, brown sunfish, carp, fathead minnow, Sacramento squawfish and golden shiner
- Details on test organisms:
- Data for a variety of fish species is reported
- Test type:
- not specified
- Water media type:
- not specified
- Total exposure duration:
- 48 h
- Remarks on result:
- other: Results are provided under "Details on results"
- Details on results:
- In the report following statement is made:
"Lawrence (1964) has summarized the 48-hr effect of monuron on fish; Coho salmon survived 110 ppm; channel catfish survived 39.8 ppm; largemouth bass, smallmouth bass, bluegill, green sunfish, brown sunfish, carp, fathead minnow, Sacramento squawfish and golden shiner all survived 32 ppm". - Validity criteria fulfilled:
- not specified
- Conclusions:
- Oncorhynchus mykiss 48-h LC50: 80 mg/L
- Executive summary:
In the report following statement is made:
"Lawrence (1964) has summarized the 48-hr effect of monuron on fish; Coho salmon survived 110 ppm; channel catfish survived 39.8 ppm; largemouth bass, smallmouth bass, bluegill, green sunfish, brown sunfish, carp, fathead minnow, Sacramento squawfish and golden shiner all survived 32 ppm".
Further details were not reported. Since this information is obtained form a peer reviewed document from an international accepted authority the result is considered reliable with restrictions for the further assessment.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Principles of method if other than guideline:
- no method provided
- GLP compliance:
- no
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Oncorhynchus kisutch
- Test type:
- not specified
- Water media type:
- not specified
- Total exposure duration:
- 48 h
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 110 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Oncorhynchus kisutch 48-h LC50: 110 mg/L
- Executive summary:
The acute 48-h toxicity of Monuron to Oncorhynchus kisutch was reported to be 110 mg/L (LC50).
Further details were not reported. Since this information is obtained form a peer reviewed document from an international accepted authority the result is considered reliable with restrictions for the further assessment.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Principles of method if other than guideline:
- no method provided
- GLP compliance:
- no
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Test type:
- not specified
- Water media type:
- not specified
- Total exposure duration:
- 48 h
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Key result
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 80 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Oncorhynchus mykiss 48-h LC50: 80 mg/L
- Executive summary:
According to Alabaster (1969; cited in US-EPA document EPA-504 -1 -75 -028 ; 1975, page 53) Monuron has an acute toxicity (48 -h LC50) to rainbow trout (Oncorhynchus mykiss) of 80 mg/L (100 mg/L for the 80% formulation).
Further details were not reported. Since this information is obtained form a peer reviewed document from an international accepted authority the result is considered reliable with restrictions for the further assessment.
Referenceopen allclose all
Description of key information
The lowest 48 -hour LC50 for marine and freshwater species was 16.3 mg/L (Mugil cephalus).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 16.3 mg/L
Additional information
There is several data on the short term toxicity to fish from reports from authorities for freshwater and marine fish. All data are for 48 hour exposure. The lowest 48 -hour LC50 was 16.3 mg/L ( Mugil cephalus). Further 48-hour LC50 data were > 32 mg/L for 10 freshwater fish species ( Coho salmon; channel catfish, largemouth bass, smallmouth bass, bluegill, green sunfish, brown sunfish, carp, fathead minnow, Sacramento squawfish and golden shiner) and 110 mg/L for Oncorhynchus kisutch. Experimental details were not reported for these studies. Since these data are obtained form peer reviewed documents prepared by international accepted authorities the results are considered reliable with restrictions for the further assessment.
These data were used for the WoE approach. The lowest reported LC50 value is 16.3mg/L. This value indicates that fish are orders of magnitude less sensitive than algae. It is considered scientifically unlikely that a prolongation of the exposure of the fish from 48 hours to 96 hours will lower the LC50 to values which will make fish more sensitive than algae. Therefore, the 48 -hour data are considered to be sufficiently relevant for the further assessment.
Since various freshwater and marine species were investigated the lowest 48-hour LC50 value is considered to be sufficiently conservative and a further factor for considering a factor for the "prolongation of exposure" to 96 hours is not needed.
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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