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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 700-748-4 | CAS number: 1226911-69-8
- 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: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 19 -21 February 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- This study was performed according to OECD Guideline 121 with GLP statement. All validity criteria were fulfilled.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.19 (Estimation of the Adsorption Coefficient (KOC) on Soil and Sewage Sludge Using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- UK GLP Compliance Programme (inspected on 10 July 2012 / signed on 30 November 2012)
- Type of method:
- HPLC estimation method
- Specific details on test material used for the study:
- STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Approximately 4 °C in the dark under nitrogen - Radiolabelling:
- no
- Test temperature:
- 30 °C
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: High performance liquid chromatograph and a cyanopropyl reverse phase HPLC column containing lipophilic and polar moieties
PREPARATION OF SOLUTIONS:
Preparation of the test item sample solution: Test item (0.1191 g) was diluted to 100 mL with methanol (MeOH) and this solution was diluted by a factor of 10 with MeOH to give a concentration of 119 mg/L.
Preparation of the reference item solutions: Solutions of reference items were prepared in MeOH (see following table 5.4.1/1).
MOBILE PHASES
- Type: methanol: water (55:45 v/v)
- pH of mobile phase: 8.15
DETERMINATION OF DEAD TIME
- The dead time was determined by measuring the retention time of formamide (purity 99.94%, 861 mg/L solution in MeOH:water 55:45 v/v).
REFERENCE SUBSTANCES
- Identity: See Table 5.4.1/1: Reference item solutions
DETERMINATION OF RETENTION TIMES
- The sample, dead time and reference standard solutions were injected in duplicate using the following HPLC parameters:
HPLC System: Agilent Technologies 1100 series, incorporating autosampler
Column: Waters XSelect HSS Cyano 5μm (150 x 4.6 mm id)
Column temperature: 30 ºC
Mobile phase: MeOH:water (55:45 v/v)
pH of mobile phase: 8.15
Flow-rate: 1.0 mL/min
Injection volume: 10 μL
UV detector length: dead time and reference standards: 210 nm; sample: 240 nm
EVALUATION
- A calibration curve was constructed from the retention time data of the dead time and reference standard solutions.
- Calculation of capacity factors k': (tr-t0)/t0
- Determination of the log Koc value:
Log10 Koc = (Log10k' - A) / B
A correlation of log k' versus log Koc of the reference standards was plotted using linear regression.
Note:
k' = capacity factor
tr = retention time (min)
t0 = dead time (min)
Koc = adsorption coefficient
A = intercept of the calibration curve
B = slope of the calibration curve - Key result
- Type:
- Koc
- Value:
- 719 dimensionless
- pH:
- 8.15
- Temp.:
- 30 °C
- Key result
- Type:
- log Koc
- Value:
- 2.86 dimensionless
- pH:
- 8.15
- Temp.:
- 30 °C
- Details on results (HPLC method):
- - Retention times of reference substances used for calibration: The retention times of the dead time and the retention times, capacity factors (k') and log10Koc values for the reference standards, determined at a constant HPLC column temperature of 30 °C are shown in tables 5.4.1/2 and 5.4.1/3
- Adsorption coefficient of the sample: The retention times, capacity factor and log10 Koc value determined for the sample at a constant HPLC column temperature of 30 °C, are shown in Table 5.4.1/4. - Validity criteria fulfilled:
- yes
- Conclusions:
- The adsorption coefficient (Koc) of the test item has been determined to be 719, log10 Koc 2.86.
- Executive summary:
The adsorption coefficient (Koc) for the test substance was determined using an HPLC screening method according to OECD 121 guideline with GLP compliance.
The test system utilized a high performance liquid chromatograph and a cyanopropyl reverse phase HPLC column containing lipophilic and polar moieties. The column temperature of 30 °C with a mobile phase consisting of 55 % methanol and 45 % water. A 119 mg/L sample of the test substance was analyzed using HPLC method. Calibrations were performed using 12 reference items; retention times, capacity factors (k') and log10Koc values for the reference standards were determined at a constant HPLC column temperature of 30 °C. Dead time of the HPLC-system was determined with Formamide. The retention times, capacity factor and log10 Koc value determined for the test substance at a constant HPLC column temperature of 30 °C.
Injection
Retention Time (mins)
Capacity Factor (k')
Log10 k'
Log10 Koc
Mean Log10 Koc
Adsorption Coefficient
1
6.395
2.402
0.380
2.85
2.86
719
2
6.419
2.414
0.383
2.86
The adsorption coefficient (Koc) of the test item has been determined to be 719, log10 Koc 2.86.
Reference
Table 5.4.1/2: Retention times of the dead time
Dead Time
|
Retention Time (mins) |
Mean Retention Time (mins) |
|
Injection 1 |
Injection 2 |
||
Formamide |
1.880 |
1.880 |
1.880 |
Table 5.4.1/3: Retention times, capacity factors (k') and log10Koc values for the reference standards
Reference Item |
Retention Time (mins)
|
Mean Retention Time (mins) |
Capacity Factor (k')
|
Log10 k'
|
Log10 Koc
|
|
Injection 1 |
Injection 2 |
|||||
Acetanilide |
2.726 |
2.726 |
2.726 |
0.450 |
-0.347 |
1.25 |
Phenol |
2.590 |
2.590 |
2.590 |
0.377 |
-0.423 |
1.32 |
Atrazine |
3.984 |
3.970 |
3.977 |
1.12 |
0.047 |
1.81 |
Isoproturon |
4.329 |
4.320 |
4.325 |
1.30 |
0.114 |
1.86 |
Triadimenol |
6.166 |
6.156 |
6.161 |
2.28 |
0.357 |
2.40 |
Linuron |
6.307 |
6.312 |
6.310 |
2.36 |
0.372 |
2.59 |
Naphthalene |
5.282 |
5.301 |
5.292 |
1.81 |
0.259 |
2.75 |
Endosulfan-diol |
8.231 |
8.270 |
8.251 |
3.39 |
0.530 |
3.02 |
Fenthion |
10.053 |
10.107 |
10.080 |
4.36 |
0.640 |
3.31 |
α-Endosulfan |
14.966 |
14.995 |
14.981 |
6.97 |
0.843 |
4.09 |
Diclofop-methyl |
16.385 |
16.385 |
16.385 |
7.71 |
0.887 |
4.20 |
Phenanthrene |
10.952 |
10.933 |
10.943 |
4.82 |
0.683 |
4.09 |
Table 5.4.1/4: Adsorption coefficient of the sample
Injection
|
Retention Time (mins) |
Capacity Factor (k')
|
Log10 k'
|
Log10 Koc
|
Mean Log10 Koc
|
Adsorption Coefficient
|
1 |
6.395 |
2.402 |
0.380 |
2.85 |
2.86 |
719 |
2 |
6.419 |
2.414 |
0.383 |
2.86 |
The test item contains no functional groups which would dissociate in the normal environmental pH range (approximately pH 5.5 to pH 7.5); therefore testing was performed without adjusting the pH of the mobile phase.
As the slope of the calibration curve for the reference standards showed good first order correlation and as the retention times between duplicate injections for each solution was consistent, the HPLC method was considered valid for the determination of adsorption coefficient. Based on the chromatographic data, the test item was considered to be stable during the test procedure.
Description of key information
OECD Guideline 121, EU Method C.19, GLP, key study, validity 1:
log Koc = 2.86
Koc = 719
The mobility of the substance is considered as low (according to the criteria developed by P.J. McCall et al., 1981).
Key value for chemical safety assessment
- Koc at 20 °C:
- 719
Additional information
To assess the adsorption potential of the registered substance on soil and on sewage sludge, one key study is available.
This study (WIL, 2015) was performed on the registered substance according to OECD Guideline 121 and EU Method C.19 (HPLC screening method) under GLP conditions. According to this study, the adsorption coefficient log Koc of the registered substance was determined at 2.86. The results indicate that the substance has low mobility (according to P.J. McCall et al., 1981).
1McCall P.J., Laskowski D.A., Swann R.L., and Dishburger H.J., (1981), “Measurement of sorption coefficients of organic chemicals and their use, in environmental fate analysis”, in Test Protocols for Environmental Fate and Movement of Toxicants. Proceedings of AOAC Symposium, AOAC, Washington DC.
Mobility classification scheme:
of Koc |
Mobility class |
0 - 50 |
Very high |
50 - 150 |
High |
150 - 500 |
Medium |
500 - 2000 |
Low |
2000 - 5000 |
Slightly |
> 5000 |
Immobile |
[LogKoc: 2.86]
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.