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EC number: 232-304-6 | CAS number: 8002-26-4 A complex combination of tall oil rosin and fatty acids derived from acidulation of crude tall oil soap and including that which is further refined. Contains at least 10% rosin.
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1998-05-25 to 1998-05-28
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study without restrictions. The study was conducted according to the appropriate OECD test guideline, and in compliance with GLP.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: Concentrations of total organic carbon (TOC) were determined at the start of the test and after 24 hours exposure in the 10000 mg/L WAF.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: The test substance was a poorly soluble complex mixture and therefore the test media were water-accommodated fractions (WAF) prepared by stirring for 23 hours with a vortex depth not exceeding 10% of the liquid depth. The media were then allowed to stand for 1 hour before drawing off the WAFs for testing.
WAFs were prepared at nominal loading rates of 625, 1250, 2500, 5000 and 10000 mg/L. The WAFs were renewed after each successive 24 hour exposure period.
- Controls: Dilution water - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Strain: Clone 5
- Source: Daphnia magna (Clone 5) originally obtained from the German Environment Ministry
- Age at study initiation (mean and range, SD): <24 hours
- Method of breeding: Laboratory stock culture
- Feeding during test: none
ACCLIMATION
- Acclimation conditions: same as test
- Type and amount of food: The daphnia were fed 2-3 times daily with algae (Scenedesmus subspicatus) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- 2.5 mmol/L
- Test temperature:
- 20+/-2.0ºC
- pH:
- 5.8-7.2
- Dissolved oxygen:
- 7.9-8.6 mg/L
- Salinity:
- not applicable
- Nominal and measured concentrations:
- Nominal loading rates: 0 (Control), 625, 1250, 2500, 5000 and 10000 mg/L.
Concentrations of total organic carbon (TOC) were determined at the start of the test and after 24 hours exposure in the 10000 mg/l WAF. The measured concentrations were 31 and 36 mg/L respectively (Table 2).
The test results are reported with reference to nominal loading rates. - Details on test conditions:
- TEST SYSTEM
- Test vessel:
- Type (delete if not applicable): open beakers
- Material, size, fill volume: glass, 50 ml with 20 ml of test medium
- Aeration: none
- Renewal rate of test solution (frequency/flow rate): static test
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- Biomass loading rate: 1 daphni/4 ml
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: demineralized water with added salts, macro-nutrients and trace elements. Comparable to that described in OECD Guideline 202.
- Alkalinity: 0.8 mmol/l
- Ca/mg ratio: 4:1
- Culture medium different from test medium: no
- Intervals of water quality measurement: Start of test and then after 24 and 48 hours
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 14 h light, 10 h dark
- Light intensity: not reported
EFFECT PARAMETERS MEASURED: Observations of immobilised daphnids, daphnids trapped at the surface, weak daphnids and carapace moults were made at least three times per day throughout the test.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2 - Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- NOELR
- Effect conc.:
- 5 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- water-accommodated fraction loading rate
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- > 5 000 - < 10 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- water-accommodated fraction loading rate
- Basis for effect:
- mobility
- Details on results:
- - Immobilisation of control: 0
- Other adverse effects control: none
- Abnormal responses: none
- Effect concentrations exceeding solubility of substance in test medium: The tested loading rates exceeded the aqueous solubility of the substance. - Reported statistics and error estimates:
- The test results were not subjected to statistical analysis
- Validity criteria fulfilled:
- yes
- Conclusions:
- A 48 h EL50 of between 5000 and 10000 mg/L and a NOELR of 5000 mg/L have been determined for the effects of the test substance on mobility of Daphnia magna.
Reference
Table 1. Test results - cumulative percentage immobilisation in each treatment over the course of the test
Time (h) | Control | 625 mg/L | 1250 mg/L | 2500 mg/L | 5000 mg/L | 10000 mg/L |
24 | 0 | 0 | 0 | 0 | 0 | 5 |
48 | 0 | 0 | 0 | 5 | 0 | 85 |
Table 2. Results of analysis of test media - concentrations of Total Organic Carbon (TOC, mg/L) at the start and end of the first 24 hour exposure period in the 10000 mg/L nominal treatment
Time (h) | 10000 mg/L treatment |
0 | 31.3 |
24 | 36.2 |
Description of key information
The results for short-term toxicity to aquatic invertebrates are summarised in Table 7.2. A 48h EL50 of between 5000 and 10000 mg/L and a NOELR of 5000 mg/L have been determined for the effects of DTO on mobility of Daphnia magna. These values are the lowest of those obtained in three reliable tests conducted on different samples of DTO.
The test organisms were exposed to water-accommodated fractions of the substance. The values are supported by similar results from two other reliable studies.
Key value for chemical safety assessment
Additional information
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