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EC number: 201-280-9 | CAS number: 80-46-6
- 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)
Description of key information
The most reliable study result for the test substance has been identified as a study (Holcombe et al. 1984) which reports an LC50 for short term toxicity in fish of 2.5 mg/L.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 2.5 mg/L
Additional information
Reliable (Klimisch 1 or 2) short-term toxicity studies with fish have been conducted for p-tert-amylphenol and are included in this dossier.
Holcombe et al. (1984) conducted a reliable (Klimisch 1) study following methods similar to OECD 203. Fathead minnows (Pimephales promelas) 31-35 days old, were exposed to measured concentrations of p-tert-amylphenol in a flow-through system for 96 hours. The 96-hr LC50, based on mortality, was 2.5 mg/L.
Davoren and Fogarty (2005) conducted a reliable (Klimisch 2) study according to OECD 203 with sodium p-tert-amylphenol. Data obtained from tests using the salt is assumed to be representative of the parent substance due to its weak acid properties. Rainbow trout (Oncorhynchus mykiss) fry, were exposed to nominal concentrations (0.18-10.0 mg/L) of the test substance for 96 hours. The 96-hr LC50, based on mortality, for rainbow trout was 1.0 mg/L.
Broderius et al (1995) conducted a reliable (Klimisch 1) study following methods similar to OECD 203 with p-tert-amylphenol. Juvenile fathead minnows (Pimephales promelas) were exposed to the concentrations of the test substance for 96 hours. The 96-hr LC50, based on mortality, was 2.59 mg/L.
Gimeno et al. (1998) conducted a reliable (Klimisch 2) study with p-tert-amylphenol. Common carp (Cyprinus carpio), 0.5-1.1 g, were exposed to measured concentrations (nominal 0, 0.56, 0.75, 1.0, 1.3, 1.8, 2.4, and 3.2 mg/L) of the test substance in a static test for 96 hours. The 96-hr LC50, based on mortality, was 1.6 mg/L.
Hagino et al.( 2001) conducted a study (Klimisch 3) where adult medaka (Oryzias latipes) were exposed to p-tert-amylphenol for 96 hours. The 96-hr LC50, based on mortality, was 2.6 mg/L. Although the study was not conducted according to acceptable methods, it is presented here for comparison.
SafePharm (1992) conducted a study (Klimisch 2) using p-tert-amylphenol as the test substance. Rainbow trout (Oncorhynchus mykiss) 4.4cm long, were exposed to nominal concentrations of the test substance for 96 hours. The 96-hr LC50, based on mortality, was >1.0 mg/L.
Adequate reliable measured data exists for short-term toxicity to fish for p-tert-amylphenol and has been documented within this dossier. The most reliable study result for the test substance has been identified as a study (Holcombe et al. 1984) which reports an LC50 for short term toxicity in fish of 2.5 mg/L. Consequently this value will be taken as the short-term toxicity in fish endpoint for p-tert-amylphenol.
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