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EC number: 204-793-6 | CAS number: 126-57-8
- 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
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- 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:
- key study
- Study period:
- 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken at 0, 24, 48, 72 and 96 hours old and new for all concentrations. A sample of the stock was also taken each day. Analysis indicated that mean measured concentrations were between 68 and 70 % of nominal over the duration of the test
- Vehicle:
- no
- Details on test solutions:
- At 0 hours 3.2 g of Priolube 3934 (Q038-03) was weighed out and dispersed in 5 Iitres of carbon filtered tap water by high-shear mixing at 20,000 rpm for 30
minutes in a 5 litre conical flask to maximize the shearing effect of the blade. This gave a 640 mg/I stock. This stock was prepared daily with the test solutions
prepared by appropriate dilution of the stock as outlined in Table 1 (see below) - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- The fish used in this study were taken from batch 36Z which hatched on 17/3/95.
They were reared in carbon-filtered tap water and fed on proprietary fish food.
There were no significant mortalities of the test fish in the week prior to the test.
A fish survey was carried out at the end of the test. Fish from the control tank indicated a mean weight of 0.20 g and a mean length of 3.1 cm.
In a deviation from SOP 108 04 not all of the fish surveyed were 2.0 ± 1.0 cm in length. This is not considered to have affected the outcome of the study. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- See table 2
- Test temperature:
- See table 2
- pH:
- See table 2
- Dissolved oxygen:
- See table 2
- Nominal and measured concentrations:
- See table 3
- Details on test conditions:
- The method was a static renewal procedure with test renewals every 24 hours. The test vessels were 6 litre capacity all-glass tanks containing 5 Iitres of test solution.
There were no replicates and all vessels were aerated. The fish were observed daily for any abnormalities in swimming activity and loss of balance. - Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 124 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- There were no mortalities at any of the test concentrations. There were no visible abnormalities, and fish behaviour was unaffected at any of the test concentrations.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Priolube 3934 is not acutely toxic to Zebra fish at a mean measured concentration of 124 mg/1. The 96 hour LC50 is greater than 124 mg/1. Observations of the fish
indicated that fish behaviour was not affected and there were no visible abnormalities at the tested concentrations. The 96 hour NOEC is > 124 mg/l.
LC50 (96h) >124 mg/L - Endpoint:
- short-term toxicity to fish
- Type of information:
- other: Read across on analogous substance
- Adequacy of study:
- supporting study
- Study period:
- 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1984
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples for analysis were taken at 0, 24, 48, 72 and 96 hours old and new for all concentrations. A sample of the stock was also taken each day. Analysis indicated that mean measured concentrations were between 27 and 36 % of nominal over the duration of the test
- Vehicle:
- no
- Details on test solutions:
- At 0 hours 3.2 g of the substance was weighed out and dispersed in 5 litres of carbon filtered tap water by high-shear mixing at 15,000 rpm for 30
minutes in a 5 litre conical flask to maximize the shearing effect of the blade. This gave a 640 mg/I stock. This stock was prepared daily with the test solutions prepared by appropriate dilution of the stock as outlined in Table 1. (see below) - Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- The fish used in this study were taken from batch 36Z which hatched on 17/3/95.
They were reared in carbon-filtered tap water and fed on proprietary fish food.
There were no significant mortalities of the test fish in the week prior to the test.
A fish survey was carried out at the end of the test. Fish from the control tank indicated a mean weight of 0.20 g and a mean length of 3.1 cm.
In a deviation from SOP 108 04 not all of the fish surveyed were 2.0 ± 1.0 cm in length. This is not considered to have affected the outcome of the study. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- See table 2
- Test temperature:
- See table 2
- pH:
- See table 2
- Dissolved oxygen:
- See table 2
- Nominal and measured concentrations:
- Nominal: 0, 18, 32, 56, 100 and 180 mg/L
Measured: 0, 6.5, 9.7, 16.1, 27.8 and 48.3 mg/L
See table 3 - Details on test conditions:
- The method was a static renewal procedure with test renewals every 24 hours. The test vessels were 6 litre capacity all-glass tanks containing 5 Iitres of test solution.
There were no replicates and all vessels were aerated. The fish were observed daily for any abnormalities in swimming activity and loss of balance.
TEST SYSTEM
- Test vessel:
- Material, size, fill volume: 6 L all-glass tanks containing 5 L of test solution
- Aeration: yes
- Renewal rate of test solution (frequency): every 24 hours
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Carbon filtered tap water
- Intervals of water quality measurement: Daily for pH, dissolved oxygen, total hardness and temperature.
OTHER TEST CONDITIONS
- Photoperiod: 16 h light/ 8 h dark
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): Mortalities and symptoms of toxicity were determined daily. The fish from the control were weighed and measured at the end of the exposure period - Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 48 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- There were no mortalities at any of the test concentrations. There were no visible abnormalities, and fish behaviour was unaffected at any of the test concentrations.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Priolube 3988 is not acutely toxic to Zebra fish at a mean measured concentration of 48 mg/l. The 96 hour LC50 is greater than 48 mg/l. Observations of the fish
indicated that fish behaviour was not affected and there were no visible abnormalities at the tested concentrations. The 96 hour NOEC is > 48 mg/l.
Referenceopen allclose all
Description of key information
Two studies have been conducted (one on the target substance TMP Pelargonate and one on the analogue TMP Triisostearate) indicating no effect at the maximum tested concentration, equivalent to nominal 180 mg/l.
The target substance is of extremely low water solubility (0.078 µg/L) and therefore the test was performed in supersaturated solution. No lethality / immobility / growth rate reduction could be observed up to the highest attainable test item concentration. Because no hazard was identified, no key values for chemical safety assessment are given below.
Key value for chemical safety assessment
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