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EC number: 403-830-5 | CAS number: 89331-94-2 B 290; BK 400; CK 34; DIBUTYL-N-102; DX-20; FAT NR. 40391/A; FLUORAN BLACK BD 869; FLUORAN SCHWARZ BD 869; NOIR FLUORANE BD 869; ODB-2; PSD-290; SENOR-2; TG-31; TH-108; WINCON-2
- 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
Toxicity to soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: short-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1991-05-08 to 1991-05-22
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of mixing into soil: The test item was applied as dry sand premixes. The dose concentrations were calculated to give the same weight of sand at all dose levels. For each group the premix was thoroughly mixed with a small proportion of soil prior to incorporation with the main soil bulk. Water was gradually mixed with the treated soil to give a moisture content equivalent to 35 % of the dry weight.
- Controls: Negative control soil was treated with an equivalent weight of dry sand. - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: earthworm
- Source: Local Supplier, Houghton, St. Ives, Cambridgeshire, England, UK
- Age at test initiation: adult with clitella
- Weight at test initiation: 529 - 643 mg
ACCLIMATION
- Acclimation period: 1 day
- Acclimation conditions: same as test
- Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 14 d
- Test temperature:
- 20 - 21 °C
- pH:
- 5.7 (addition of calcium carbonate)
- Moisture:
- 35 % of the dry weight
- Details on test conditions:
- TEST SYSTEM
- Test container (material, size): glass container (1 L)
- Amount of soil or substrate: 729 g
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
SOURCE AND PROPERTIES OF SUBSTRATE
- Composition (% w/w):
Quartz sand 70
Kaolin clay 20
Sphagnum peat 10
OTHER TEST CONDITIONS
- Photoperiod: continous
- Light intensity: 400 lux
EFFECT PARAMETERS MEASURED:
Counts of worms, on day 7 and 14
Health and mortalities: Daily
Weights: on day 0 and 14
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.8
- Test concentrations: 0, 95, 171, 309, 556, 1000 ppm - Nominal and measured concentrations:
- 0, 95, 171, 309, 556, or 1000 ppm
- Reference substance (positive control):
- yes
- Remarks:
- chloroacetamide
- Key result
- Duration:
- 14 d
- Dose descriptor:
- LC50
- Effect conc.:
- > 1 000 other: ppm
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Details on results:
- - Mortality at end of exposure period:
No mortalities were detected at the day 7 count. By day 14, one mortality had occurred in the 309 ppm dose group. This mortality was not considered to be treatment-related. No mortalities occurred in any other group.
- Changes in body weight of live adults at end of exposure period: Weight losses were observed in all groups. However, there was no clear evidence of any treatment-related effect. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: The LC50 values for chloroacetamide, tested previously as a positive control between 15 and 29 May 1985 were found to be:
Day 7 LC50: 43.1 ppm (95 % confidence limits 34.0 – 57.6 ppm)
Day 14 LC50: 24.6 ppm (95 % confidence limits 20.2 – 30.5 ppm) - Reported statistics and error estimates:
- As outlined in OECD Method No. 207
- Validity criteria fulfilled:
- yes
- Conclusions:
- It was not possible to determine the LC50 values of ODB-2 to the earthworm at Days 7 and 14. The LC50 is above 1000 ppm, the maximum treatment level tested.
- Executive summary:
In a 14 -day acute toxicity study, earthworms (Eisenia fetida) were expsoed to the test substance at 0, 95, 171, 309, 556, or 1000 ppm (Huntingdon, 1991). The reference chemical used was chloroacetamide. The experiment was carried out in accordance with OECD guideline 207.
No mortalities were detected at the day 7 count. By Day 14, one mortality had occurred in the 309 ppm dose group. This mortality was not considered to be treatment-related. No mortalities occurred in any other group. Weight losses were observed in all groups. However, there was no clear evidence of any treatment-related effect.
The LC50 values for chloroacetamide, tested previously as a positive control were found to be:
Day 7 LC50: 43.1 ppm (95 % confidence limits 34.0 – 57.6 ppm)
Day 14 LC50: 24.6 ppm (95 % confidence limits 20.2 – 30.5 ppm)
Because of the limited number of mortalities it was not possible to determine the LC50 values of the test item to the earthworm at Days 7 and 14. These values must lie in excess of 1000 ppm, the maximum treatment level used. The test substance is therefore regarded as non-toxic to earthworms above a concentration of 1000 ppm.
Reference
Table 1: Weight Development
Treatment |
Concentration (ppm) |
Weight (mg) |
% Decrease |
|||
Day 0 |
Group mean |
Day 14 |
Group mean |
|||
Neg. Control |
0 |
643 |
592 |
478 |
451 |
23.8 |
529 |
428 |
|||||
596 |
442 |
|||||
600 |
456 |
|||||
Test Item |
95 |
639 |
602 |
478 |
489 |
23.8 |
601 |
460 |
|||||
572 |
439 |
|||||
595 |
459 |
|||||
Test Item |
171 |
605 |
602 |
470 |
479 |
20.4 |
582 |
432 |
|||||
628 |
488 |
|||||
594 |
525 |
|||||
Test Item |
309 |
582 |
603 |
447 |
488 |
19.1 |
594 |
528 |
|||||
623 |
496 |
|||||
613 |
485 |
|||||
Test Item |
556 |
584 |
603 |
492 |
498 |
17.4 |
594 |
497 |
|||||
614 |
508 |
|||||
620 |
496 |
|||||
Test Item |
1000 |
615 |
601 |
486 |
474 |
21.1 |
615 |
490 |
|||||
587 |
449 |
|||||
585 |
471 |
Description of key information
It was not possible to determine the LC50 values of the test substance to the earthworm on days 7 and 14. The LC50 is above 1000 ppm, the maximum treatment level tested.
Key value for chemical safety assessment
Additional information
In a 14 -day acute toxicity study, earthworms (Eisenia fetida) were exposed to the test substance at 0, 95, 171, 309, 556, or 1000 ppm (Huntingdon, 1991). The reference chemical used was chloroacetamide. The experiment was carried out in accordance with OECD guideline 207.
No mortalities were detected at the day 7 count. By day 14, one mortality had occurred in the 309 ppm dose group. This mortality was not considered to be treatment-related. No mortalities occurred in any other group. Weight losses were observed in all groups. However, there was no clear evidence of any treatment-related effect.
The LC50 values for chloroacetamide, tested previously as a positive control were found to be:
Day 7 LC50: 43.1 ppm (95 % confidence limits 34.0 – 57.6 ppm)
Day 14 LC50: 24.6 ppm (95 % confidence limits 20.2 – 30.5 ppm)
Because of the limited number of mortalities it was not possible to determine the LC50 values of the test substance to the earthworm on days 7 and 14. These values must be above 1000 ppm, the maximum treatment level used.
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