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EC number: 208-792-1 | CAS number: 541-73-1
- 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
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from peer-reviewed handbook or collection of data.
Data source
Referenceopen allclose all
- Reference Type:
- review article or handbook
- Title:
- Reaxys ID 956618
- Author:
- Reaxys
- Year:
- 2 015
- Bibliographic source:
- https://www.reaxys.com/reaxys/secured/start.do
- Report date:
- 2015
- Reference Type:
- publication
- Title:
- PREDICTION ADSORPTION COEFFICIENTS (KOC) FOR AROMATIC COMPOUNDS BY HPLC RETENTION FACTORS (K')
- Author:
- Hong, H., Wang, L. and Han, S.
- Year:
- 1 996
- Bibliographic source:
- Chemosphere, Vol. 32, No. 2, pp. 343-351, 1996
- Report date:
- 1995
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- GLP compliance:
- no
- Type of method:
- HPLC estimation method
- Media:
- soil
Test material
- Reference substance name:
- 1,3-dichlorobenzene
- EC Number:
- 208-792-1
- EC Name:
- 1,3-dichlorobenzene
- Cas Number:
- 541-73-1
- Molecular formula:
- C6H4Cl2
- IUPAC Name:
- 1,3-dichlorobenzene
- Test material form:
- other: liquid
- Details on test material:
- purity not specified
Constituent 1
Study design
HPLC method
- Details on study design: HPLC method:
- - Instrument:
The HPLC system (Shimadzu, Japan) consisted of a SCL-8A system monitor, a LC-8A pump, a C-R4A integrator and a SPD-6AV ultraviolet
spectrophotometer as the detector.
- Determination of capacity factors:
A YWG C18 column (20 x 0. 46 cm, 10 µm) was used. Mobile phases were made by mixing methanol with water in the proportions 90:10, 85:15, 80:20, 75:25 and 70:30 (v/v). The flow rate was 1.0 mL /min.
Methanol solution of uracil was used for the measurement of dead time. All measurements were made at least in triplicate. The average reproducibility of each determination was better than 1.0 % relative. The capacity factors obtained at different mobile phase composition are
log K' (90 %) = 0.085
log K' (85 %) = 0.274
log K' (80 %) = 0.473
log K' (75 %) = 0.695
log K' (70 %) = 0.889
log K' (Ø %) = 3.730
Results and discussion
Adsorption coefficient
- Type:
- log Koc
- Value:
- 2.5
Any other information on results incl. tables
Using retention data from apolar stationary phase can get good prediction tool for estimating adsorption coefficients an soil for both non-polar and polar chemicals by adding a second variable that takes nonhydrophobic interactions into account. Either the Δ°x term or the hydrogen-bonding indicator variable can be used as the second variable. The predicted values of log Koc from Eq. 2 and 9, and the differences between the experimental values are shown in the table.
Log Koc values obtained by HPLC and differences from reported values:
Compound | exp. | cal. by eq.2 | cal. by eq. 9 |
1,3- dichlorobenzene | 2.50 | 2.62 | 2.62 |
Due to the disadvantages of Kow relationships mentioned in the introduction part, and more important, chromatographic parameters have some advantages:
(a) the chromatographic method is simple and rapid;
(b) it requires little material, which is important with compounds that are expensive and/or difficult to synthesize;
(c) the material does not need to be very pure, the use of chromatography in prediction of environmental parameter is very promising.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The absorption of 1,3-dichlorobenzene in soil was determined as log Koc = 2.50.
- Executive summary:
The absorption of 1,3-dichlorobenzene in soil was determined as log Koc = 2.50.
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