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EC number: 926-273-4 | CAS number: -
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was given a reliability rating of 1 because it followed a standard test guideline, which describes a procedure to evaluate this endpoint, and the results were reviewed for reliability and assessed as valid. The study was also conducted under GLP.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- Individual treatment solutions were prepared as Water Accommodated Fractions (WAFs). This included adding test substance to glass vessels, which contained dilution water and mixing for approximately 24 hours with a magnetic stirrer to produce a series of geometrically-spaced loading rates (mg/L). After mixing, the WAFs were allowed to settle for an hour. Each aqueous phase was then drawn off and transferred to two
150 mL Erlenmeyer flasks which were completely filled. Two further flasks were filled with dilution water only and served as controls. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Organisms were supplied by in-house cultures. The laboratory culture is derived from a clone held at ICI Brixham Laboratory. The ICI clone was itself obtained from the Institut de Recherche Chimique Applique (I.R.Ch.A.), France. Test organisms age = <24 hours old; parents age = 15 - 28 days.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- Water hardness of the control dilution water was 174 mg/L as CaCO3.
- Test temperature:
- Test temperature was 20 – 22 ºC.
- pH:
- The pH ranged from 7.7 to 8.1.
- Dissolved oxygen:
- Dissolved oxygen was 8.3 to 8.6 mg/L for "new" solutions and 8.6 to 8.7 mg/L for "old" solutions.
- Salinity:
- freshwater
- Nominal and measured concentrations:
- Nominal treatment levels were control, 0.1, 0.4, 1.0, 3.0 and 10 mg/L, which at t=0 measured non detected (< 2.5 mg/L), NA (not analyzed), NA, NA, 3.3 mg/L and 8.2 mg/L, respectively.
- Details on test conditions:
- Ten Daphnia magna, less than 24 h old, were added to each flask. The flasks were sealed with black caps that excluded air from the vessel. After 24 and 48 h the numbers of immobilized D.magna were recorded. D.magna were considered to be immobile, if, when the contents of the flask were swirled they did not swim during a 15 second period of observation.
Photoperiod with a 16 h : 8 h light : dark lighting regime. - Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- >= 3 - <= 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- See Table in Remarks on Results
- Reported statistics and error estimates:
- Loading rates causing a 50% effect were determined by visual inspection of the data. They are expressed as being within a range bounded by loading rates that were tested. This is considered more appropriate for test materials that are mixtures of substances of different solubilities than is an interpolative statistical technique.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Water accommodated fractions of hydrocarbons, C10, aromatics, >1% naphthalene, produced a 48-hour LL50 value between 3 and 10 mg/L with Daphnia magna.
- Executive summary:
Water accommodated fractions of hydrocarbons, C10, aromatics, >1% naphthalene, produced a 48-hour LL50 value between 3 and 10 mg/L with Daphnia magna.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 16-Jan-1992 to 18-Jan-1992
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The reliability rating is a 1 because the study followed a standard guideline, which describes a procedure designed to evaluate this endpoint, and the results were reviewed for reliability and assessed as valid. The study was also conducted under GLP.
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 72-2 (Aquatic Invertebrate Acute Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- Samples were removed from the fresh solutions at initiation and on Day 1. Samples were also removed from the old solutions on Day 1.
- Vehicle:
- no
- Details on test solutions:
- Individual treatment solutions were prepared as either a water accommodated fraction (WAF) or serial dilution of a stock WAF. A WAF was prepared for the two highest treatments (1.0 and 4.0 mg/L) by adding test substance to 1.0 L of medium in a 1 liter flask, mixing for 24 hours, and then removing the WAF from below the surface using a siphon. The lower treatment solutions were prepared by making serial dilutions of a WAF prepared as described above at a loading of 1.0 mg/L. Serial dilutions were prepared for the lower treatment solutions because of the difficulty in accurately preparing the renewal solutions at these lower treatment levels. Each test solution was renewed after 24 hours with a freshly prepared WAF solution. Dilution water was laboratory blend water with a hardness of 40 to 48 mg/L CaCO3.
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- Test organisms came from in-house cultures. Original source was Academy of Natural Sciences of Philadelphia, Division of Environmental Research, Philadelphia, PA, USA. Test organisms were <24 hours old from 16 day-old parents.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- None
- Hardness:
- 40 to 48 mg/L as CaCO3.
- Test temperature:
- Test temperature was 19.6 Deg C.
- pH:
- The pH ranged from 7.8 to 8.0.
- Dissolved oxygen:
- Dissolved oxygen was 9.0 to 9.2 mg/L for "new" solutions and 8.3 to 9.1 mg/L for "old" solutions.
- Salinity:
- freshwater
- Nominal and measured concentrations:
- Nominal treatment levels were control, 0.01, 0.05, 0.1, 0.5, 1.0, and 4.0 mg/L, which measured non detected, NA (not analyzed), NA, 0.051, 0.228, 0.814, and 3.74 mg/L, respectively.
- Details on test conditions:
- Lighting was 67 to 76 ft candles with 16 hrs light and 8 hrs dark. Test vessels were 250 ml glass beakers in duplicate filled with 240 ml of solution. All test vessels were covered. Each replicate contained 10 organisms.
- Reference substance (positive control):
- no
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- 1.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95% CI = 0.95 - 1.8
- Details on results:
- 48-hour EL50 = 1.1 mg/L (95% CI 0.95 to 1.8 mg/L) based upon nominal values 48-hour EC50 = 0.95 mg/L (95% CI 0.76 to 1.48 mg/L) based upon measured values.
- Reported statistics and error estimates:
- The 48-hr EC50 values were determined using the Probit Procedure of SAS.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Water accommodated fractions of hydrocarbons, C10-C13, aromatics, >1% naphthalene, produced a 48-hour EL50 value of 1.1 mg/l with the water flea (Daphnia magna).
- Executive summary:
Water accommodated fractions of hydrocarbons, C10-C13, aromatics, >1% naphthalene, produced a 48-hour EL50 value of 1.1 mg/l with the water flea (Daphnia magna).
Referenceopen allclose all
Nominal Loading | Measured Conc | Daphnia Immobilized |
(mg/L) | (mg/L) | (@ 24, 48 hrs)* |
Control | <LoD | 0,0 |
0.1 | <LoD | 0, 0 |
0.4 | <LoD | 0, 0 |
1.0 | <LoD | 0, 0 |
3.0 | 3.3 – 3.1 ** | 0, 0 |
10.0 | 8.2 – 7.8 ** | 10, 10 |
*10 daphnids added to each of the control and treatment levels (both in duplicate) at test initiation
** Measured concentrations refer to the t=0h (fresh) and t=48 h (old) samples
Nominal Loading Total
or Concentration Daphnia Immobilized
(mg/L) (@ 24, 48 hrs)*
Control 0, 0
0.01 (nominal)** 1, 1
0.05 (nominal)** 0, 0
0.05 (measured) 0, 0
0.23 (measured) 0, 1
0.81 (measured) 0, 7
3.74 (measured) 17, 20
*20 daphnids added to each of the control and treatment levels at test initiation.
**Test solutions were not analyzed or included in the statistical analyses due to lack of significant mortality.
Description of key information
There is data available for this substance. Additionally, key and supporting data is available for the structural analogue Hydrocarbons, C10, aromatics, >1% naphthalene. The data for this substance is presented in the dossier. The data is read across to this substance based on analogue read across and a discussion and report on the read across strategy is provided as an attachment in IUCLID Section 13.
Hydrocarbons, C10, aromatics, >1% naphthalene, presented a 48-h EL50 (mobility) for Daphnia magna of between 3 and 10 mg/L (WAF) (Shell 1993b) and 10 mg/L (WAF) (Exxon 2006b).
Hydrocarbons, C10-C13, aromatics, >1% naphthalene, presented a 48-h EL50 (mobility) for Daphnia magna of 1.1 mg/L (WAF).
Key value for chemical safety assessment
Additional information
Three study reports were available and input as endpoint records.
The study from Shell (1993b) examined the short-term toxicity of the test substance Hydrocarbons, C10, aromatics, >1% naphthalene, to Daphnia Magna. Groups of 10 daphnids (in duplicate) were exposed to nominal treatment levels of 0, 0.1, 0.4, 1.0, 3.0 or 10.0 mg/L of the test substance. Daphnids were exposed for 48h and after 24 and 48 h the numbers of immobilized Daphnia Magna were recorded. The 48h EL50 for Daphnia Magna was between 3 and 10 mg/L (WAF).
The study from Exxon (2006b) examined the short-term toxicity of the test substance Hydrocarbons, C10-C13, aromatics, >1% naphthalene, to Daphnia Magna. Five daphnids were added to each replicate and the replicates sealed. The test was performed under static conditions with no aeration. Daphnids were exposed to nominal treatment levels of 0, 0.45, 1.8, 4.3, 12.0 or 26.0 mg/L of the test substance. Daphnids were exposed for 48h and after 24 and 48 h the numbers of immobilized Daphnia Magna were recorded. The 48h EL50 for Daphnia Magna was 10 mg/L.
The study from Exxon (1992) examined the short-term toxicity of the test substance Hydrocarbons, C10, aromatics, >1% naphthalene, to Daphnia Magna. 20 daphnids were added to each of the control and treatment levels at test initiation. Nominal treatment levels were control, 0.01, 0.05, 0.1, 0.5, 1.0, and 4.0 mg/L. Each test solution was renewed after 24 hours with a freshly prepared WAF solution. Daphnids were exposed for 48h and after 24 and 48 h the numbers of immobilized Daphnia Magna were recorded. The 48h EL50 for Daphnia Magna was 1.1 mg/L (WAF).
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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