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EC number: 204-800-2 | CAS number: 126-73-8
- 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
Toxicity to fish
The acute toxicity of tributylphosphate has been investigated in a number of studies in various fish species. The results of the studies are summarised below.
Species | LC50 (mg/L) | Time (h) | Comment | Reference |
Oryzias latipes | 9.6 | 96 |
| Sasaki et al, 1981a |
Carassius auratus | 8.8 | 96 |
| Sasaki et al, 1981b |
Leuciscus idus
| 7.6 | 96 |
| Juhnke & Luedemann, 1978 |
Oryzias latipes | 14.2 | 48 |
| CITI, 1992 |
Pimephales promelas | 8.18-11 | 96 |
| Geiger et al, 1986 |
Oryzias latipes | 17 | 96 |
| Yoshioka & Ose, 1993 |
Oryzias latipes | 5.85-18.5 | 24-48 | Effects of temperature | Tsuko et al, 1985 |
Oryzias latipes | 1.3 | 48 |
| Yoshioka et al, 1985 |
Oncorhynchus mykiss | 13 | 96 |
| Bowman & Schrier, 1990 |
Oncorhynchus mykiss | 11 | 96 |
| ABC Labs, 1978 |
Salmo gairdneri | 11.5-13.5 | 96 |
| Dave & Lidman, 1978 |
Pimephales promelas | 6.4 | 96 |
| ABC labs, 1978 |
Salmo gairdneri | 4.2-11.8 |
| Effects of temperature key value for chemical safety assessment | Dave et al, 1979 |
Dave et al (1981) report a 7 -day LC50 of 11.4 mg/L and a 10 -Day NOEC of 13.5 mg/L in Danio rerio. The same authors report a 50 -day NOEC for the embryo and larval stages of Oncorhyncus mykiss of 18.3 mg/L. In a proprietary study summarised in the OECD SIDS, a NOEC of 0.82 mg/L (key value for chemical safety assessment) is reported for a fish ELS toxicity test using Oncorhyncus mykiss.
Toxicity to aquatic invertebrates
The results of a large number of studies are available and are sumamrised below. In addition, the range-finding study for the 21-day reproduction test, Kuehn et al (1989) reports 24 -hour LC0 and LC50 values for tributylphosphate in Daphnia magna of 9.3 and 35 mg/L respectively.
Species | EC50 (mg/L) | Time (h) | Comment | Reference |
Daphnia magna | 30 | 96 |
| Bringmann & Kuehn, 1982 |
Daphnia magna | 5-28.75 | 96 |
| Bayer, 1985 |
Daphnia magna | 33 | 24 |
| Bringmann & Kuehn, 1977 |
Gammarus pseudolimnaeus | 1.7 | 96 |
| England & Cramer, 1991 |
Daphnia magna | 12.8 | 24 |
| Dave et al, 1981 |
Daphnia magna | 1.8 | 48 | key value for chemical safety assessment | ABC Laboratories, 1978 |
Daphnia magna | 52 | 6 |
| Wakabayashi et al, 1988 |
35 | 24 | |||
Daphnia magna | 2.6 | 48 |
| ABC Laboratories, 1990 |
Daphnia pulex | 6 | 93 |
| Wakabayashi et al, 1988 |
24 | 68 | |||
Hyalella azteca | 2.4 | 96 |
| England & Schrier, 1990 |
Moina macrocopa | 1.8 | 3 |
| Yoshioda et al, 1986 |
Dugesia japonica | 1.3 | 3 |
|
A 21-day reproduction test was carried out in Daphnia magna to determine the NOEC for tributyl phosphate (Kuehn et al, 1989). Evaluation parameters for fixing the NOEC were parent animal mortality, reproduction rate and the appearance of the first offspring during the test period. Animals were aged 24 hours at the start of the test. A semi-static procedure was used with open vessels maintained under fluorescent lighting, animals were fed daily with algae suspension (the test was carried out in accordance with an FEA guideline). The 24 hour EC50 value was also determined. The NOEC was found to be 1.3 mg/l (key value for chemical safety assessment) in the 21 day reproduction test.
The 21 day EC50 (immobilisation) of tributyl phosphate in Daphnia magna is also reported to be >2.1mg/l (ABC Laboratories, 1991).
Toxicity to aquatic algae and cyanobacteria
The results of a number of studies in different species are available and are summarised below. The lowest and thus most conservative LC50 value (Kuehn & Pattard, 1990, 96h-LC50: 1.1. mg/L based on biomass) was chosen as key value for chemical safety assessment.
Species | Endpoint | Time | Comment | Reference |
Microcystis aeruginosa | Toxicity threshold: 4.1 mg/L | 8d | Bringmann & Kuehn, 1978 | |
Scenedesmus subspicatus | Toxicity threshold: 3.2 mg/L | 8d | Bringmann & Kuehn, 1978 | |
Scenedesmus subspicatus | EC50 1.1-1.3 mg/L (biomass); 2.8-4.2 mg/L (growth) | 96h | key value for chemical safety assessment | Kuehn & Pattard, 1990 |
Selenastrum capricornutum | EC50 4.4 mg/L | 96h | Burgess & Wirth, 1990 | |
Chlorella emersonii | EC50 5-10 mg/L | 48h | Dave et al, 1979 | |
Phytoplankton species | EC100 50 mg/L LOEC 5 mg/L | 14d | Blanck et al, 1984 |
Toxicity to microorganisms
A number of studies have been performed in various organisms and are summarised below.
Species | Endpoint | Time | Comment | Reference |
Activated sludge | EC50: 100 mg/L | 3h | key value for chemical safety assessment | Yoshioka et al, 1986 |
Pseudomonas putida | Toxicity threshold: >100 mg/L | 16h |
| Bringmann & Kuehn, 1977 |
Tetrahymena pyriformis | EC 50: 20 mg/L | 24h |
| Yoshioka, 1985 |
Activated sludge | EC50: 300 mg/L | 3h |
| Bayer, 1985 |
Entosiphon sulcatum | Toxicity threshold: 14 mg/L | 72h |
| (Bringmann & Kuehn, 1979) |
Chilomonas paramecium | Toxicity threshold: 42 mg/L | 48h |
| (Bringmann et al, 1980) |
Uronema parduczi | Toxicity threshold: 21 mg/L | 20h |
| (Bringmann & Kuehn, 1980) |
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