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EC number: 203-870-1 | CAS number: 111-44-4
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption, other
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - Short description of test conditions: Glass columns were packed with a sandy soil with low organic matter (0.087% organic C) to a depth of 140 cm in a manner that preserved to the maximum extent possible the characteristics of the original soil profile. The columns received 14 cm/day of water containing a mixture of approximately 1.0 or 0.2 mg/L of each of various organic compounds. Quantities of compounds that volatilize from the soil surface were measured, as well as concentrations in the column effluent by GC-FID.
- GLP compliance:
- no
- Remarks:
- pre-GLP
- Media:
- soil
- Specific details on test material used for the study:
- TEST MATERIAL
- Names (as cited): Bis(2-chloroethyl)ether
- Purity: not specified - Radiolabelling:
- no
- Test temperature:
- 20+/-1°C
- Analytical monitoring:
- yes
- Remarks:
- GC-FID
- Details on sampling:
- - Sampling: sample of column effluent was collected for roughly 20 hours; the volume of sample, about 300 mL, represented approximately one-half the pore water volume of the columns.
- Matrix no.:
- #1
- Matrix type:
- other: sandy soil
- % Clay:
- > 1.5 - < 3.5
- % Silt:
- > 4 - < 8
- % Sand:
- > 89 - < 95
- % Org. carbon:
- > 0.02 - < 0.22
- pH:
- > 6.1 - < 6.6
- CEC:
- > 2.3 - < 4.8 not specified
- Bulk density (g/cm³):
- ca. 1.65
- Details on matrix:
- COLLECTION AND STORAGE
- Geographic location: Ada, Oklahoma
- Collection procedures: colllected in 10-cm increments from a soil profile
- Sampling depth (cm): 1-150 cm
- Storage length: as short as possible
- Soil preparation: to protect the biota, the soil was not dried or sieved
PROPERTIES
- Soil texture: Lincoln fine sand
- % sand: 92
- % silt: 5.9
- % clay: 2.1
- Horizon:
- Soil taxonomic classification: thermic Typic Ustifluvent
- pH: 6.4
- Organic carbon (%): 0.087
- CEC (meq/100 g): 3.5
- Insoluble carbonates (%):
- Bulk density (g/cm3): 1.65 g/cm3 - Details on test conditions:
- TEST CONDITIONS
- Buffer: None
- pH: 6.4
TEST SYSTEM
- Type, size and further details on reaction vessel: Columns of borosilicate glass process pipe, 5 cm i.d by 150 cm (Ace Glass Inc., Vineland, N.J.)
- Amount of soil: 140 cm
- Number of reaction vessels/concentration: 1
- Test performed in closed vessels due to significant volatility of test substance: no but fitted with a trap for volatile compounds - Key result
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- 1.88 dimensionless
- pH:
- 6.4
- Temp.:
- 20 °C
- Matrix:
- Sandy soil
- % Org. carbon:
- 0.087
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Under the conditions of this study, the Log Koc of Bis(2-chloroethyl)ether was determined to be 1.88 at 20°C and pH 6.4.
- Executive summary:
This study aimed to assess the rentention of 13 organic pollutants in a sandy soil with low organic matter (0.087% organic C). Glass columns were packed with soil to a depth of 140 cm in a manner that preserved to the maximum extent possible the characteristics of the original soil profile. The columns received 14 cm/day of water containing a mixture of approximately 1.0 or 0.2 mg/liter of each of the organic compounds. Quantities of compounds that volatilize from the soil surface were measured, as well as concentrations in the column effluent.
Bis(2-chloroethyl)ether did not degrade or significantly volatilize (86% of the material applied reached 140 cm). Its retardation factors (velocity of tritiated water through soil divided by apparent velocity of pollutant through soil) was < 1.5, which shows that it can percolate rapidly through the soil. This results is in good agreement with the low octanol/water partition coefficient of Bis(2-chloroethyl)ether. Under the conditions of this study, the Log Koc of Bis(2-chloroethyl)ether was determined to be 1.88 at 20°C and pH 6.4.
While no detailed results are provided, the methodology is described in sufficient details. In addition the publication has been subject to peer-rewiew. Accordingly, the data is considered acceptable and has been assigned a reliability score of 2.
Reference
The following table present the fate of Bis-(2 -chloroethyl)ether when applied to the sandy soil:
Concentration applied in mg/L (measured) | Volatilized (%) | Column effluent (%) | Degraded or not accounted for (%) |
0.86 | Not determined | 91 +/- 15 | 9 +/-31 |
0.16 | Not determined | 86 +/- 1 | 14 +/- 20 |
Description of key information
In a study aiming at assessing the rentention of 13 organic pollutants in a sandy soil with low organic matter (0.087% organic C), the Log Koc of Bis(2-chloroethyl) ether was determined at 1.88. Quantities of compounds that volatilize from the soil surface were measured, as well as concentrations in the column effluent. Bis(2-chloroethyl)ether did not degrade or significantly volatilize (86% of the material applied reached 140 cm). Its retardation factors (velocity of tritiated water through soil divided by apparent velocity of pollutant through soil) was < 1.5, which shows that it can percolate rapidly through the soil. This results is in good agreement with the low octanol/water partition coefficient of Bis(2-chloroethyl)ether.
Key value for chemical safety assessment
- Koc at 20 °C:
- 75.86
Additional information
A single study reports an experimental Log Koc estimate for Bis(2-chloroethyl) ether.
The study by Wilson et al. (J. Environ. Qual., 1981, 10(4):501-6) aimed at assessing the rentention of 13 organic pollutants in a sandy soil with low organic matter (0.087% organic C). Glass columns were packed with soil to a depth of 140 cm in a manner that preserved to the maximum extent possible the characteristics of the original soil profile. The columns received 14 cm/day of water containing a mixture of approximately 1.0 or 0.2 mg/liter of each of the organic compounds. Quantities of compounds that volatilize from the soil surface were measured, as well as concentrations in the column effluent.
Bis(2-chloroethyl)ether did not degrade or significantly volatilize (86% of the material applied reached 140 cm). Its retardation factors (velocity of tritiated water through soil divided by apparent velocity of pollutant through soil) was < 1.5, which shows that it can percolate rapidly through the soil. This results is in good agreement with the low octanol/water partition coefficient of Bis(2-chloroethyl)ether. Under the conditions of this study, the Log Koc of Bis(2-chloroethyl)ether was determined to be 1.88 at 20°C and pH 6.4.
While no detailed results are provided, the methodology is described in sufficient details. In addition the publication has been subject to peer-rewiew. Accordingly, the data is considered acceptable and has been assigned a reliability score of 2.
[LogKoc: 1.88]
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