Registration Dossier
Registration Dossier
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: 202-697-9 | CAS number: 98-74-8
- 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:
- 2017-11-21 to 2017-11-21
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- 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
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- other: HPLC column
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: M16LB4523
- Expiration date of the lot/batch: 2018-02-09 (retest date)
- Purity test date: 2017-11-29 (certificate of analysis release date)
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: At room temperature - Radiolabelling:
- no
- Test temperature:
- Column temperature 35°C ± 1°C.
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: Acquity UPLC system (Waters, Milford, MA, USA)
- Type: Acquity UPLC TUV detector (Waters)
- Type, material and dimension of analytical (guard) column: Acquity UPLC HSS Cyano, 100 mm x 2.1 mm i.d., dp = 1.8 µm (Waters)
- Detection: 210 nm (UV)
- Column temperature: 35°C ± 1°C
MOBILE PHASES
- Type: 55/45 (v/v) methanol/water
- Solutes for dissolving test and reference substances:
* Solution of the unretained compound:
A 5.0 g/L stock solution of formamide (99.2%, [75-12-7], Alfa Aesar, Karlsruhe, Germany) in methanol was used. The stock solution was diluted to obtain an end solution of 55/45 (v/v) methanol/water.
The formamide blank solution was 55/45 (v/v) methanol/water.
* Reference substance solutions:
Stock solutions of the reference substances at concentrations of approximately 1 g/L in methanol or acetonitrile were used. The stock solutions were diluted to obtain an end solution of 55/45 (v/v) methanol/water.
The blank solution for the mixture of reference substances was 55/45 (v/v) methanol/water.
* Test solution:
A 1000 mg/L stock solution of the test item was prepared in acetonitrile. The stock solution was 100-times diluted to obtain an end solution of 55/45 (v/v) methanol/water. The final concentration of the test item solution was 10.0 mg/L.
The test item blank solution was 55/45 (v/v) methanol/water.
An additional dilution of the stock solution was prepared in acetonitrile at concentration level 50 mg/L, to see whether the peaks determined are test item or its degradation products.
REFERENCE SUBSTANCES
- Identity: combined reference solution containing Acetanilide, Monuron, 2,5-Dichloroaniline, Napthalene, Benzoic acid phenylester, Fenthion, Phenanthrene and 4,4'-DDT
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 10 mg/L.
- Quantity of reference substances: 1 g/L in methanol or acetonitrile
- Intervals of calibration: no data
REPETITIONS
- Number of determinations: 2 times (test item solution and reference substance), 1 time (blank solution)
EVALUATION
- Calculation of capacity factors k': from retention time of reference items, the test item, and then on-sorbed chemical item
- Determination of the log Koc value: a correlation of log k' versus log Koc of the reference items is plotted using linear regression - the log k' value of the test item is then used to calculate its log Koc value - Key result
- Type:
- log Koc
- Value:
- < 1.26 dimensionless
- pH:
- 7
- Remarks on result:
- other: peak 1 (degradation product)
- Key result
- Type:
- log Koc
- Value:
- 1.83 dimensionless
- pH:
- 7
- Remarks on result:
- other: peak 2 (degradation product)
- Key result
- Type:
- Koc
- Value:
- < 18 dimensionless
- pH:
- 7
- Remarks on result:
- other: peak 1 (degradation product)
- Key result
- Type:
- Koc
- Value:
- 67 dimensionless
- pH:
- 7
- Remarks on result:
- other: peak 2 (degradation product)
- Details on results (HPLC method):
- - Retention times (tr,1 and tr,2) of reference substances used for calibration:
* Formamide (t=0):
tr,1: 0.686 min; tr,2: 0.686 min
* Acetanilide:
tr,1: 0.910 min.; tr,2: 0.912 min.
* Monuron:
tr,1: 1.125 min.; tr,2: 1.127 min.
* 2,5-Dichloroaniline:
tr,1: 1.281; tr,2: 1.284 min.
* Naphthalene:
tr,1: 1.495 min.; tr,2: 1.499 min.
* Benzoic acid phenylester:
tr,1: 1.769 min; tr,2: 1.776 min.
* Fenthion:
tr,1: 2.380 min.; tr,2: 2.393 min.
* Phenanthrene:
tr,1: 2.629 min; tr,2: 2.642 min.
* 4,4'-DDT:
tr,1: 6.572 min; tr,2: 6.620 min.
- Details of fitted regression line (log k' vs. log Koc): log k’ = 0.322 x log Koc – 0.818 (r = 0.98, n = 16)
- Average retention data for test substance:
* peak 1: 0.400 min
* peak 2: 1.089 min
- Koc test substance:
* peak 1: < 18
* peak 2: 67 - Transformation products:
- not measured
- Validity criteria fulfilled:
- yes
- Conclusions:
- The HPLC method using soil-adsorption-reference data was applied for the determination of the adsorption coefficient (Koc) of JNJ-39722280-AAA (4-nitrobenzene-1-sulfonyl chloride).
In the chromatogram of the test solution, two peaks were observed. Comparing it to the chromatogram in acetonitrile, it was concluded that both peaks were degradation products of the test item.
The mean log Koc of the main degradation products of 4-nitrobenzene-1-sulfonyl chloride at neutral pH were determined to be <1.26 and 1.83, peak 1 and peak 2 respectively using the HPLC estimation method according to OECD guideline 121. The results of the test can be considered reliable without restriction.
Reference
Calculation of pKavalues
As the nitro group could not be correctly defined in Pallas, no calculation result could be reported. .Therefore, the UPLC analysis was performed at neutral pH.
Description of key information
This endpoint is covered with a GLP-study (Reingruber, 2018) performed according to standard test guideline OECD 121. The mean log Koc of the main degradation products of 4-nitrobenzene-1-sulfonyl chloride were determined to be <1.26 and 1.83, peak 1 and peak 2, respectively, using the HPLC estimation method. The partition coefficients in soil, sediment, suspended matter and raw sewage sludge were calculated from the Koc value and the fraction of organic carbon in the compartment as stipulated in the ECHA guidance Chapter 16 - Table R.16-11.
The log Kow of the second peak (log kow = 1.83) was considered as key value for the safety assessment
Key value for chemical safety assessment
- Koc at 20 °C:
- 67
Additional information
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.
