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EC number: 261-222-3 | CAS number: 58353-68-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Density
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- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
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- Endpoint summary
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- Environmental data
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- 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
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
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- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
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- Additional toxicological data

Endpoint summary
Administrative data
Description of key information
No subcacute toxicity data were available for the registered substance, however read-across substance Butanoic acid, 4-amino-4-oxo-2(or3)-sulfo-, N-(C16-C18 (even numbered), C18unsaturated alkyl)), disodium salts was tested in a key repeated dose/reproduction and developmental toxicity screening study at oral gavage doses of 60, 120 and 300 mag act.ingr./kg bw. At 300 mg/kg bw/day, clinical signs, decreased body weight and food consumption, haematological changes and organ weights changes of several organs were noted in male and female rats. NOAEL-levels were 120 mg/kg bw for paternal/maternal toxicity; 120 mg/kg bw for reproductive toxicity and 300 mg/kg bw for developmental toxicity.
No subchronic data were available for the registered substance, however subchronic (and subacute) data were available from read-across substance 'Butanoic acid, 4-amino-4-oxosulfo-, N-tallow alkyl derivs., disodium salts' (CAS No. 68988-69-2) at dietary doses of 0.50, 2.00 and 8.00 g act.ingr./kg bw/day, of which the high dose was reduced to 4 g/kg feed/day after 6 weeks. NOEL for the test item in the rat was < 500 mg act. ingr. /kg bw/day. Various changes were seen at the highest dose levels, however the mid dose level could be considered as NOAEL, corresponding with 500 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- reliable (Klimisch 2)
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
No data were available for registered substance, however data were available for read-across substances
-
'Butanoic acid, 4-amino-4-oxo-2(or 3)-sulfo-, N-(C16-C18 (even
numbered), C18 unsaturated alkyl), disodium salts'
- CAS No. 68988-69-2: 'Butanoic acid, 4-amino-4-oxosulfo-, N-tallow
alkyl derivs., disodium salts'.
Justification for read-across with category members is provided in
Section 13.
Subacute
toxicity and combined repeated dose toxicity wiht the
reproductive/developmental toxicity screening
-
Key data for repeated dose toxicity were available from read-across
substance 'Butanoic acid, 4-amino-4-oxo-2(or 3)-sulfo-, N-(C16-C18 (even
numbered), C18 unsaturated alkyl), disodium salts' in a combination
repeated dose/reproduction and developmental toxicity screening study
according to OECD TG 422 (Key study; Hansen, 2013a). The test item was
administered orally by gavage as a test item containing 25.5% active
ingredient to rats at dose levels of 60, 120 or 300 mg act.ingr./kg
bw/day. The application started two weeks before mating on test day one
and ended on the day or one day before sacrifice. Day of sacrifice was
on test day 37 for the male rats and on lactation day 4 or shortly
thereafter for the female rats. One of 10 male and one of 10 female
animals both at 120 and 300 mg/kg bw/day) died prematurely. At 300 mg/kg
bw/day clinical signs in form of salivation, pilo-erection and/or
breathing sounds were noted in a few male and female animals for 1 or 2
test days. A statistically significant reduction in body weight was
noted in both sexes at 300 mg/kg bw/day. Accordingly, food consumption
and body weight were statistically significantly reduced in both sexes
at 300 mg/kg bw/day. Haematology showed statistically significant
changes at 300 mg test item/kg bw/day, including increased MCH and
decreased aPTT time (male animals) and increased No. white blood cells
and lymphocytes (female animals). Changes in the relative or absolute
organ weights of several organs were noted for the male animals dosed at
300 mg test item/kg bw/day, most remarkably for the relative liver
weight which increased for almost 20%. The macroscopic and microscopic
examinations revealed no test item related changes.
NOAEL-levels were as follows: 120 mg/kg bw for paternal/maternal toxicity; 120 mg/kg bw for reproductive toxicity (see Section 7.8.1); 300 mg/kg bw for developmental toxicity (see Section 7.8.2).
- A supporting 14 -day dose range finding study was conducted with ' Butanoic acid, 4-amino-4-oxo-2(or 3)-sulfo-, N-(C16-C18 (even numbered), C18 unsaturated alkyl), disodium salts' in rats given test item containing 25.5% active ingredient; the animals were treated once daily with 100, 300 and 1000 mg act.ingr./kg bw/day by oral administration (Hansen, 2013b). One of 5 male animals dosed at 300 mg/kg bw/day and 3 of 5 male animals and 1 of 5 female animals dosed at 1000 mg /kg bw/day died prematurely. Premortal symptoms in form of pilo-erection, reduced motility, increased respiratory rate, cold to touch, decreased respiratory rate and a reduced drinking water consumption. Pilo-erection, a thickened abdomen, pultaceous faeces, an anus soiled with faeces and breathing sounds were noted for the male and female animals treated with 1000 mg/kg bw/day. The body weight of the male animals dosed at 300 or 1000 mg/kg bw/day and of the female animals treated with 1000 mg/kg bw/day was reduced. Body weight gain and body weight at autopsy were reduced accordingly. A reduced food consumption was noted for male and female animals treated with 1000 mg/kg bw/day. At macroscopic inspection at necropsy, one of 5 male animals treated with 300 mg/kg bw/day showed reddened lungs. Furthermore, changes in the gastrointestinal tract (filled with gas, distended, with liquid content, nearly empty, (mucosa) reddened, soft content, haemorrhagic foci, detachment of mucosa), lungs (reddened), spleen (reduced in size) and external observation (thickened / soft abdomen, anus smeared with faeces, pilo-erection) were noted for the male and female animals (including deceased animals) treated with 1000 mg /kg bw/day. The relative and absolute kidney weights of the animals were decreased starting at 100 mg /kg bw/day for the male animals and at 1000 mg/kg bw/day for the female animals. After consideration of these data, the following dose levels were selected for the combined repeated dose toxicity and reproduction/developmental toxicity screening test: 60, 120 and 300 mg/kg bw/day.
- In conclusion, a (parental) NOAEL of 120 mg/kg bw was found in the conbined repeated/reproductive and developmental toxicity study with structurally similar stubance administered by gavage. Therefore it can also be assumed for reigstered substance.
Subchronic
toxicity
No
subchronic data were available for the registered substance, however
subchronic (and subacute) data were available from read-across substance
'Butanoic acid, 4-amino-4-oxosulfo-, N-tallow alkyl derivs., disodium
salts' (CAS No. 68988-69-2).
-In
a supporting 30 -day subacute oral repeated dose study (Shaffer and
Golz, 1956b) the test item containing 35% active ingredient was added to
the diet of three groups of young male albino rats (10 animals per
group) to give concentrations of 0.25%, 0.50% and 1.00% in terms of
solids content (act. ingr.) of the sample. In the course of the study,
these dietary levels resulted in mean daily dosages of 0.23 g/kg, 0.46
g/kg and 0.88 g act. ingr./kg, respectively. No deaths occurred as a
result of feeding of the product, and there were no characteristic signs
of toxicity. However, at the highest dosage level, mean daily food
intake was significantly reduced and mean body weight gain for the
30-day period was only about one-half that of the controls. Mean kidney
weight at this dose was slightly but significantly reduced. At the 0.50%
level, mean body weight gain was significantly lower, but food intake
was comparable to that of the controls. At the lowest level, neither
food intake, nor weight gain were affected, and appearance and behavior
of the animals were normal. All animals were sacrificed at the
conclusion of the study and no gross pathology was found at autopsy that
could be related to feeding of the material. Mean kidney weight was
slightly but significantly decreased at the highest dose level. NOAEL
was 230 mg act. ingr./kg bw /day.
- In a key subchronic oral repeated dose study (Tegeris and Underwood,
1976a) the test item containing 35% active ingredient was fed to albino
rats for ninety days at doses of 0.50, 2.00 and 8.00 g act.ingr./kg
bw/day. The rats were carefully observed for the duration of the
experiment, body weight and feed intake /conversion were measured and
pertinent haematological and biochemical parameters were conducted after
6 weeks and after termination. At the conclusion of the experiment all
rats were necropsied and all organs and/or tissues were examined
histologically from ten rats (five male and five female). Due to
mortality of 4 rats at 8 g/kg bw/day, dosing was reduced to 4 g/kg
feed/day after 6 weeks. These studies have further shown that the test
item, when fed to rats under the conditions of this experiment,
decreased the rate of body weight gain and food intake, at all levels
and caused acute gastro-enteritis and/or acute nephritis within six
weeks at 8.00 g/kg/day. When this dose was decreased to 4.00 g/kg/day
and given for seven weeks some rats displayed zonal fatty infiltration
in the liver. At the lowest dose level, decreases in body weight (gain)
and feed intake were minimal (<10%) and were not considered relevant.
Decreased organ weights were observed for heart, liver, kidneys, adrenal
an thyroid weight at the medium and high doses. From the data presented
in this study it appears that the NOEL for the test item in the rat was
< 500 mg act. ingr. /kg bw/day. A NOAEL of 500 mg act.ingr./kg bw/day
however can be considered.
- In a supporting subchronic oral repeated dose study (Tegeris and
Underwood, 1976b) the test item containing 35% active ingredient was fed
to purebred beagle dogs for ninety days. Thirty two purebred beagle dogs
were dosed at 0.062 ,0.250 g and 1.000 g act. ingr./ kg bw/day
thoroughly mixed in the diet. The test material interfered with the feed
consumption and feed efficiency and decreased the rate of body weight
gain of dogs when fed the compound at 0.250 and 1.000 g/kg bw/day,
leading to the decision to decrease the highest dose to 0.500 g/kg bw
after 2 weeks and stop dosing in this high dose group after six weeks.
There was no biological effect on any parameter at 0.062 g active
ingredient/kg of body weight per day. The
dog study was not considered adequate due to the young age of the
animals at start of dosing (3 -4 months). Decreased body weights and
feed intake at the higher doses were attributed to higher sensitivity of
the gastro-intestinal tract, by which systemic toxicity could not
appropriately be determined.
- In conclusion, a NOAEL of 500 mg/kg bw was observed in the key subchronic toxicity study in the rat wiht structurally related subsance, administered by diet. Therefore it can also be assumed for the registered substance.
Conclusion
-
The NOAEL of 120 mg act. ingr./kg bw in the OECD 422 study was
considered as the most conservative value, therefore this was selected
as the descriptor for DNEL calculations with registered substance.
- Further information supporting the safety of the test substance is provided in the read across justification for the N1 subgroup (justification with data matrix separately attached in Section 13).
Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
Key study according to most recent standards
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: liver
Justification for classification or non-classification
As there was no toxicity below classification threshold, classification for repeated dose toxicity is not needed according to the EC Directive (No.93/21/EEC) and CLP (No. 1272/2008 of 16 December 2008).
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