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EC number: 200-087-7 | CAS number: 51-28-5
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Data have been obtained from secondary sources (EPA databank, pubblications).
2,4-dinitrophenol seems to be toxic for soil macroorganisms as worms (LC50 for worms is 0.6 (0.5-0.7) ug/cm2 based on mortality endpoint).
A complete study on Dinoseb is available (Carine Staempfli, Joseph Tarradellas, Kristin Becker-van Slooten, , 2006). Dinoseb is an herbicide and insecticide belonging to the dinitrophenol family and the structural formulas of 2,4-dinitrophenol and Dinoseb are similar. They have the same mode of action, uncoupling the ATP synthesis by canceling the cell membrane potential.
Dinitrophenols may also originate as impurities in certain pesticides such as Dinoseb (Wegman RCC, Wammes JI. 1983). The endpoint measured revealed toxicity to Collemboan arthropods at low doses after 21-28 days of exposure. (20 µg/kg soil dw of NOEC, EC50 reproduction of 14.4 µg dinoseb/kg soil dw).
Once in soil, it can be uptake from plants and seeds and be toxic for the germination. The EC50 for terrestrial plants Raphanus sativus is 7.07 (unit 1e-5 M). High concentrations of dinitrophenols are toxic to the growth and development of plants, especially at lower pH, because it can be uptake not ionized (Overcash et al., 1982).
Furthermore, modifications of the soil microbial activity were observed. An IC50 (mg/l) nitrate reductase activity: 45.62 and a concentration IC50 (mg/l) nitrate reductase activity: > 200 were defined for 2,4-dinitrophenol (Okolo et al., 2007). Other observations during biodegradation in soil and sediment tests with observation of the toxicity lever for microorganisms defined that above the level of c.a 100 mg/L, 2,4 -dinitrophenol may be toxic to the degrader microorganisms (Bartha et al. 1967; Namkoong et al. 1988; Schmidt and Gier 1989).
Terrestrial data don't contribute to environmental classification, but due to the specific cellular endpoint (ATP synthesis) with a wide range of effects on organs, all terrestrial organisms could be affected.
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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