Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 695-977-9 | CAS number: 1309955-79-0
- 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: long-term
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 2009-07-17 to 2009-09-15
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- See section 13.2 for the read-across justification.
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 222 (Earthworm Reproduction Test (Eisenia fetida/Eisenia andrei))
- Version / remarks:
- DIN ISO 11268-2: 1998 (E), BBA Guideline (1994)
- Deviations:
- yes
- Remarks:
- Earthworms were also fed weekly after removing adult earthworms at day 28. The soil moisture of all test vessels deviated by more than 10 % of the initial value at the end of the test.
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of mixing into soil (if used): The test item was weighed out and was evenly distributed in 10 g quartz sand per replicate. The treated quartz sand was given to the natural soil. Demineralised water was added to adjust the humidity of the natural soil to a moisture content of 54 % of the maximum water holding capacity.
Thereafter, the test medium was mixed for at least three minutes and about 600 g soil dry weight were filled into each test vessel.
- Controls: Natural soil moistened with demineralised water without test or reference item was used as control medium. - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: Eisenia fetida SAVIGNY 1826, subspecies Eisenia fetida fetida
- Source: Own breeding
- Age at test initiation (mean and range, SD): synchronized earthworm culture, not deviating more than 1 month
- Weight at test initiation (mean and range, SD): 0.46
ACCLIMATION
- Acclimation period: 2 days prior to test start
- Acclimation conditions (same as test or not): same as test
- Health during acclimation (any mortality observed): healthy - Study type:
- laboratory study
- Substrate type:
- natural soil
- Limit test:
- no
- Total exposure duration:
- 56 d
- Remarks:
- Removement of adults after 28 days
- Test temperature:
- 20 +/- 2°C
- pH:
- Application rate
[mg test item/kg soil DW] pH-value
day 0 day 56
Control 6.34 6.43
62.5 6.30 6.46
125 6.32 6.47
250 6.31 6.41
500 6.34 6.39
1000 6.49 6.32 - Moisture:
- Application rate
[mg test item/kg soil DW] Moisture [%] of dry weight
day 0 day 60
Control 23.4 31.2*
62.5 23.2 31.2*
125 23.0 29.8*
250 23.3 31.0*
500 23.0 29.5*
1000 23.8 33.8* - Details on test conditions:
- TEST SYSTEM
- Test container (material, size): Round plastic boxes with an inner diameter of 15.0 cm corresponding to a bottom surface area of 177 cm2 and a height of 14 cm contained about 600 g soil dry weight. Transparent perforated lids enabled sufficient gas exchange, light input and prevented the substrate from drying.
- Amount of soil or substrate: 600 g
- No. of organisms per container (treatment): 10 (40)
- No. of replicates per treatment group: 4
- No. of replicates per control: 8
- No. of replicates per vehicle control: -
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Geographic location: Speyer, South Germany
- Pesticide use history at the collection site: Pesticides:
Sampling year and 4 former years: None
Plants:
Sampling year (2009): Meadow
2008: Meadow
2007: Meadow
2006: Meadow
2005: Meadow
Fertilization:
No organic fertilization
Sampling year (2009): None
2008: None
2007: 600 kg/ha CaO
+ 250 kg/ha MgO
2006: None
2005: None
- Soil texture (if natural soil)
-sand: 0.63 – 2.0 mm % 0.7 ± 0.2
0.2 – 0.63 mm % 44.5 ± 2.6
0.063 – 0.2 mm % 35.5 ± 2.2
- % silt: 0.02 – 0.063 mm % 5.8 ± 1.1
0.006 – 0.02 mm % 4.0 ± 0.6
0.002 – 0.006 mm % 3.0 ± 0.6
- % clay: < 0.002 mm % 6.4 ± 0.9
- Soil taxonomic classification: loamy sand (lS)
- Soil classification system: German DIN classification
- Organic carbon (%): 2.09 +/- 0.4
- Maximum water holding capacity (in % dry weigth): 46.5 +/- 6.0
OTHER TEST CONDITIONS
- Photoperiod: 16 h
- Light intensity: 400 - 800 lx
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
The bodyweight of the adult earthworms were individually determined at day 0 and day 28.
After the first four weeks the adult earthworms were removed and mortality and morphological changes of the adult worms were recorded. After further four weeks, the number of offspring hatched from the cocoons were counted.
Observation parameter: a) no obvious pathological symptoms
b) no reaction to touching
c) no negative phototactical reaction
d) spasmodic winding
e) spontaneous segmentation and separation
f) yellow excretion from the oral aperture
g) ulcer and skin bleedings
t) dead earthworms
VEHICLE CONTROL PERFORMED: no
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study: No
- Nominal and measured concentrations:
- Nominal application rates: 62.5 - 125 - 250 - 500 - 1000 mg test substance/kg soil dry weight (DW)
- Reference substance (positive control):
- yes
- Remarks:
- 1.0 - 2.5 - 5.0 mg Carbendazim/ kg soil DW
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 500 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Remarks:
- reduction of body weight
- Details on results:
- - Mortality at end of exposure period: No mortality was observed in any of the tested test item and control groups
- Total mass of adults at beginning of test: 0.46
- Changes in body weigth of live adults (% of initial weight) at end of exposure period: please refer to the respective table
- No. of offspring produced: please refer to the respective table
- No. of unhatched cocoons: Not determined
- Morphological abnormalities: None
- Behavioural abnormalities: None
- Other biological observations: None - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: 1.0 mg Carbendazim/kg soil DW - Reported statistics and error estimates:
- One Way Analysis of Variance (ANOVA) was carried out for the determination of statistically significant differences compared to the control. A Normality Test and an Equal Variance Test were conducted prior to running the ANOVA. P-values for both Normality and Equal Variance Test are 0.05. The a-value for ANOVA test (acceptable probability of incorrectly concluding that there is a difference) is a = 0.05.
- Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of this study, Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9) did not induce mortality or pathological symptoms of adult earthworms after an exposure to the test item concentrations of 62.5, 125, 250, 500 and 1000 mg/kg soil dry weight for 28 days. The biomass increase of the adult earthworms after 28 days did not statistically significant differ compared to the control at 62.5, 125, 250 and 500 mg/kg soil dry weight. However, at 1000 mg/kg soil dry weight the biomass increase was statistically significantly reduced compared to the control. In addition, after eight weeks of exposure the earthworm reproduction was not statistically significantly reduced at 62.5, 125, 250 and 500 mg/kg soil dry weight. At 1000 mg/kg soil dry weight the earthworm reproduction was statistically significantly reduced compared to the control.
Thus, the No Observed Effect Concentration (NOEC) of Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9) with respect to mortality, body weight and reproduction of Eisenia fetida fetida after 8 weeks of exposure in artificial soil was determined to be 500 mg/kg soil dry weight. - Executive summary:
Effects of Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9)(Batch no. S001018) on mortality, biomass and the reproductive potential of the earthworm species Eisenia fetida(Savigny) were determined according to the guidelines DIN ISO 11268-2 (1998), OECD 222 (2004) and BBA (1994) from July 17th to September 15th, 2009 at Dr.U.Noack-Laboratorienin 31157 Sarstedt, Germany. The study was conducted under static conditions over 8 weeks with five different application rates (62.5 – 125 – 250 – 500 – 1000 mg/kg soil dry weight), which were mixed into natural soil. Eighty sexually mature earthworms were inserted into 8 control replicates (10 earthworms per replicate) and forty sexually mature earthworms were divided into 4 replicates for the test item concentrations. They had an individual body weight between 0.30 and 0.60 g.
After 28 days no mortality was seen in the control and at all tested application rates (Table 1). Also, no evident pathological symptoms or changes in the behaviour of adult earthworms were seen in the control and at all tested application rates. The earthworm biomass increased in the control and at all tested application rates over 28 days without any statistically significant differences at 62.5, 125, 250 and 500 mg/kg soil dry weight compared to the control. However, at 1000 mg/kg soil dry weight the biomass increase was statistically significant reduced compared to the control. After further four weeks the reproduction rate (average number of juveniles) was 332 in the control and ranged between 254 and 359 at the test item application rates. Compared to the control, the reproduction rate was statistically significantly reduced at 1000 mg/kg soil dry weight. All other tested application rates showed no statistically significant reduction compared to the control (Table 1).
Overall, the NOEC of Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9) concerning mortality, biomass and reproduction of earthworms was determined to be at 500 mg/kg soil dry weight (Table 2).
All validity criteria recommended by the test guidelines were fulfilled.
Summary of All Observed Effects in the Tested Doses
Effects
Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9)
mg/kg soil dry weight
62.5
125
250
500
1000
Mortality of adult earthworms
No
No
No
No
No
Reduction of body weight
No
No
No
No
Yes
Reduced reproduction rate
(Number of juveniles)
No
No
No
No
Yes
Summary of all effects
No
No
No
No
Yes
NOEC and LOEC for Reproduction, Mortality and Body Weight
Bis (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9)
Application rate
mg/kg soil dry weight
NOECreproduction, mortality, body weight
500
LOECreproduction, mortality, body weight
1000
Reference
Description of key information
No terrestrial test have been performed with di (2-hydroxypropyl)tallow amine. The data available for di (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9) will as a worst-case be used for read-across. Justification for this read-across is presented in IUCLID chapter 13. For Di (2-hydroxyethyl) oleyl amine (CAS No 25307-17-9) one chronic earthworm test has been performed resulting in a NOEC of 500 mg/kg dw.
Key value for chemical safety assessment
- Long-term EC10, LC10 or NOEC for soil macroorganisms:
- 500 mg/kg soil dw
Additional information
No effects observed in a chronic terrestrial test up to 500 mg/kg dw.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.