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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Workers - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
68.18 mg/m³
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
Overall assessment factor (AF):
100
Dose descriptor starting point:
NOAEL
Modified dose descriptor starting point:
NOAEC
AF for differences in duration of exposure:
2
AF for other interspecies differences:
10
AF for intraspecies differences:
5
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
9.74 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
100
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - workers

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
17 mg/m³
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
200
Modified dose descriptor starting point:
NOAEC
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

General Population - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
9.74 mg/kg bw/day
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
other:
Overall assessment factor (AF):
200
Dose descriptor starting point:
NOAEL
Value:
974 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
1 948 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

Default (DNEL calculator)

AF for dose response relationship:
1
AF for differences in duration of exposure:
6
AF for interspecies differences (allometric scaling):
4
AF for other interspecies differences:
2.5
AF for intraspecies differences:
10
AF for the quality of the whole database:
1
AF for remaining uncertainties:
1
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
exposure based waiving

General Population - Hazard via oral route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
4.87 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
other:
Overall assessment factor (AF):
200
Dose descriptor starting point:
NOAEL
Value:
974
Modified dose descriptor starting point:
NOAEL
Value:
974
AF for dose response relationship:
1
AF for differences in duration of exposure:
2
AF for interspecies differences (allometric scaling):
4
AF for other interspecies differences:
2.5
AF for intraspecies differences:
10
AF for the quality of the whole database:
1
AF for remaining uncertainties:
1
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - General Population

In line with chapter R.7 c (ECHA, 2012) the main toxicokinetic properties of sodium ethylenesulphonate (SVS, CAS-No. 3039-83-6) are assessed on the basis of its physico-chemical properties and with special regard to the results of the standard toxicity studies performed with this substance. Specific toxicokinetics or dermal absorption studies are not available for the substance.


 



  1. Relevant physico-chemical properties of SVS
    Molecular weight: 130.1 g/mol
    Physical state: liquid (RT)
    logPow: -1.01
    Water solubility: > 1000 g/L (20 °C)
    Vapour pressure: 0.000391 Pa (20 °C)


Information on absorption, distribution, metabolism and excretion is derived from available information. Available information: The results of the physico-chemical properties of SVS indicate that the oral route is the most likely route of exposure. The vapour pressure of SVS is low (0.000391 Pa at 20°C) which indicate that the inhalation route will not be the major route of exposure. SVS has a log P < -1 which suggest that the substance is not likely to be sufficiently lipophilic to cross the stratum corneum, therefore dermal absorption is likely to be low. These are the results of the toxicity test, which can contribute to toxicokinetic information. The results of the acute dermal toxicity test report a LD50 of > 2000 mg/kg bw and the skin irritation/corrosion test states that SVS is not an irritating substance. The oral acute toxicity test report a LD50 >15000 mg/kg bw. The oral repeated dose toxicity test exposed Wistar rats for 90 days. No effects were allocated at any of the parameters observed: e.g. mortality, body weight, biochemistry, mating period, gestation length, hematology, organ weight changes, gross pathology, histopathology. The NOAEL of SVS is greater than 1000 mg/kg bw. The hydrolysis test demonstrates that SVS was hydrolytically stable at pH 4, 7 and 9. Conclusion: Based on the available information, we can conclude that the oral route is the major route of exposure. The toxicity studies do not show any effects on e.g. organs, which cannot contribute to any information on the distribution of the substance. The hydrolysis study shows no major breakdown of SVS what may indicate that there are no major metabolites present in the environment and toxicity studies.