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EC number: 200-741-1 | CAS number: 70-55-3
- 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
Endpoint summary
Administrative data
Description of key information
p-TSA is of low acute toxicity. Acute oral LD50 is 2330 mg/kgbw and dermal toxicity much lower.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1978
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: A 2 page study report is available. The study was performed pre-GLP. The study was performed according to a method similar to OECD401.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Principles of method if other than guideline:
- Very high dose volume. Animals were only observed for signs of intoxication and necropsy was performed on surviving animals.
- GLP compliance:
- no
- Remarks:
- pre-GLP
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Source: TNO
Body weight: males 242 to 380 g, females 120 to 180 g.
The rats were housed in groups of five in screem-bottomed stainless steel cages, in a well-ventilated room, maintained at 23-250 C.
Before dosing the rats were fasted overnight. - Route of administration:
- oral: gavage
- Vehicle:
- propylene glycol
- Doses:
- 2075, 2500, 3000, 3600, 4325 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- Dosing: By gavage as 25 % (w/v) suspension in propylene glycol to groups of five males and five females in single doses of 8.3, 10.0, 12.0, 14.4 or 17.3 ml per kg body weight.
They were observed for signs of intoxication during a 14-day period, after which autopsies were carried out on the survivors. - Statistics:
- The LDso was calculated according to the method of Wei! (Biometrics 8, (1952) 249-263).
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 2 330 mg/kg bw
- 95% CL:
- 2 080 - 2 600
- Interpretation of results:
- Category 5 based on GHS criteria
- Remarks:
- Migrated information
- Conclusions:
- From the mortality-figures the LD50 of para-toluene sulphonamide was calculated to be 2.33 g per kg body weight, with 2.08 and 2.60 as the 95% confidence limits. Therefore, the test substance can be classified in Category V according to GHS.
- Executive summary:
An acute oral toxicity study was performed according to a method similar to OECD401 and pre-GLP. 5 male and 5 female rats were dosed with 8.3, 10.0, 1.20, 14.4 or 17.3 ml/kg bw. The animals were observed for signs of intoxication during a 14-day period, after which autopsies were carried out on the survivors. Within a few hours after dosing the rats showed sluggishness, followed by loss of consciousness. Death occurred between 4 and 50 hours after dosing. Later on the survivors recovered gradually and looked quite healthy again at the end of the observation period. Macroscopic examination of the survivors at autopsy revealed dark discolouration of the liver in the rats of all dose groups. Some of the rats showed mottled kidneys. No other signs of treatment-related gross alterations were seen. From the mortality-figures the LD50 of para-toluene sulphonamide was calculated to be 2.33 g per kg body weight, with 2.08 and 2.60 as the 95% confidence limits. Therefore, the test substance can be classified in Category V according to GHS.
Reference
Results:
Within a few hours after dosing the rats showed sluggishness, followed by loss of consciousness. Death occurred between 4 and 50 hours after dosing. Later on the survivors recovered gradually and looked quite healthy again at the end of the observation period. Macroscopic examination of the survivors at autopsy revealed dark discolouration of the liver in the rats of all dose groups. Some of the rats showed mottled kidneys. No other signs of treatment-related gross alterations were seen.
Dose |
Mortality |
|||
Suspension ml/kg |
Test substance g/kg |
males |
females |
% |
8.3 |
2.08 |
1/5 |
3/5 |
40 |
10.0 |
2.50 |
1/5 |
4/5 |
50 |
12.0 |
3.00 |
4/5 |
5/5 |
90 |
14.4 |
3.60 |
3/5 |
5/5 |
80 |
17.3 |
4.33 |
5/5 |
5/5 |
100 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 330 mg/kg bw
- Quality of whole database:
- Although of low quality, the results are in-line with other available information.
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- 1957
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Limited reporting, none GLP, only one rabbit was dosed per dose level.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- 6 rabbits were dosed with increasing amounts of test substance applied on the skin and observed for evidence of toxicity
- GLP compliance:
- no
- Test type:
- other:
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- BW of rabbits between 1.6 and 2.3 kg
- Type of coverage:
- not specified
- Vehicle:
- corn oil
- Details on dermal exposure:
- A 25% suspension in corn oil was applied to the closely clipped, intact skin of New Zealand rabbits and observations made for evidence of toxicity. The treated areas were covered with plastic shields and a leather collar placed around the neck of each animal to prevent access to the sample.
- Duration of exposure:
- No data
- Doses:
- 2.0, 3.5, 5.0, 6.0, 7.5 and 7.5 g/kg bw based on tests substance (Highest dose level of 7.5 g/kg was applied to both a male and a female animal)
- No. of animals per sex per dose:
- 1. Only highes dose 2 (one male and one female)
- Control animals:
- not required
- Details on study design:
- Examinations included: observations on clinical signs and body weight changes during 5 days.
- Sex:
- male/female
- Dose descriptor:
- LD0
- Effect level:
- 7 500 mg/kg bw
- Based on:
- test mat.
- Mortality:
- No mortality obsrved
- Clinical signs:
- other: No signs of systemic toxicity developed. Appetite and activity remained about normal. There was no evidence of paralysis such as developed when rabbits were fed the product orally.
- Gross pathology:
- Not performed
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- No mortality or systemic toxicity was observed following dermal application of 7500 mg/kg bw of o/p-TSA when applied as a 25% suspension in corn oil.
- Executive summary:
The substance tested is a mixture of ortho-toluene sulfonamide (o-TSA: 30%) and para-toluenesulfonamide (p-TSA: 70%).
A 25% suspension in corn oil was applied to the closely clipped, intact skin of New Zealand rabbits and observations made for evidence of toxicity. The treated areas were covered with plastic shields and a leather collar placed around the neck of each animal to prevent access to the sample.
The following dose levels were applied on one animal each: 2.0, 3.5, 5.0, 6.0, 7.5 (male) and 7.5 (female) g/kg bw. Examinations included: observations on clinical signs and body weight changes during 5 days.
The highest application of 7.5 g/kg bw was non lethal. No signs of systemic toxicity developed. Appetite and activity remained about normal. There was no evidence of paralysis such as developed when rabbits were fed the product orally.
The test article was not acutely toxic when applied to the skin of rabbits.
Reference
Animal |
sex |
BW in kg |
Dose g/kg bw |
BW change after 5 days |
Results |
1 |
Female |
1.7 |
2.0 |
4.0% |
survived |
2 |
Male |
2.1 |
3.5 |
6.0% |
survived |
3 |
Female |
1.6 |
5.0 |
0.0% |
survived |
4 |
Female |
1.9 |
6.0 |
5.0% |
survived |
5 |
Male |
2.3 |
7.5 |
0.0% |
survived |
6 |
Female |
2.0 |
7.5 |
3.0% |
survived |
The highest application of 7.5 g/kg bw was non lethal. No signs of systemic toxicity developed. Appetite and activity remained about normal. There was no evidence of paralysis such as developed when rabbits were fed the product orally.
The test article was not acutely toxic when applied to the skin of rabbits.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- discriminating dose
- Value:
- 7 500 mg/kg bw
- Quality of whole database:
- Substance is of low acute oral toxicity, not requiring classification. Also no classification is required for skin or eye irritation. Information on absorption indicates that p-TSA is rapidly and completely absorbed by oral route, en only 20% by dermal route. Further acute testing by dermal route is therefore scientifically unjustified.
Additional information
Oral:
There are two studies available evaluating the acute oral toxicity:
An acute oral toxicity study was performed according to a method similar to OECD401 and pre-GLP. 5 male and 5 female rats were dosed with 8.3, 10.0, 1.20, 14.4 or 17.3 ml/kg bw. The animals were observed for signs of intoxication during a 14-day period, after which autopsies were carried out on the survivors. Within a few hours after dosing the rats showed sluggishness, followed by loss of consciousness. Death occurred between 4 and 50 hours after dosing. Later on the survivors recovered gradually and looked quite healthy again at the end of the observation period. Macroscopic examination of the survivors at autopsy revealed dark discolouration of the liver in the rats of all dose groups. Some of the rats showed mottled kidneys. No other signs of treatment-related gross alterations were seen. From the mortality-figures the LD50 of para-toluene sulphonamide was calculated to be 2.33 g per kg body weight, with 2.08 and 2.60 as the 95% confidence limits.
Similar results were obtained by a more recent Japanese study performed in 1994. Although the study was very extensive, reporting is only available from OECD SIDS dossier and a poor English translation of the Japanese report. The study evaluated the acute oral toxicity of p-TSA rats. Groups of 5 female animals received dose levels of 889, 1333, 2000 and 3000 mg/kg, and a group of 5 males 2000 mg/kg males. Observations included detailed clinical signs, body weights, and gross pathological examination. For the dead animals, all females of the 3000 mg/kg group and the 2000 mg/kg treated males the major organs and tissues were fixated for histopathological examination.
One animal from the 3000 mg group and two females of the 2000 mg group died on day 1 or 2. In the males treated at 2000 mg no mortality occurred. Directly following dosing there were clinical signs observed in all groups consisting of reduced activity, apathy, hunched posture and abnormal gait. Also haematuria was observed. Histopathology effects were seen in renal tubular epithelial cells and epithelial cells in urethra or bladder, and pulmonary oedema. In the surviving animals clinical signs were resolved from day 3. The LD50 was concluded to be > 2000 mg/kg bw for both males and females. Possibly there is a sex difference in toxicity.
All information, including from literature is presented in the below:
Route |
Species (sex and strain) |
LD50/LC50 |
Reference(s) |
p. o. |
Rat (male & female/ Wistar) |
LD50 = 2330 mg/kg bw |
TNO (1978) |
Rat (male & female; Sprague Dawley Crj: CD(SD) |
LD50 >2000 mg/kg |
(MHW, cited by OECD, 1994) Hatano (1991) |
|
Mouse (sex and strain n. p.) |
LD50 = 400 mg/kg |
Sax and Lewis (undated, cited by OECD, 1994) |
|
Rat and/or rabbit (sex and strain n. p.) |
LD100 ~ 4.7 g/kg (in 15% suspension of 2% aqueous solution of methyl cellulose) |
Monsanto Co. (1947) |
|
Rat (sex and strain n. p.) |
LD100 ~ 3.2 g/kg (in 15% olive oil) |
||
Rat (sex and strain n. p.) |
LD50 = 2400 mg/kg bw for mixture (41%o-TSA; 51%p-TSA) |
EMEA (1999) |
|
Wild bird species (sex and strain n. p.) |
LD50 = 75 mg/kg |
Schafer (1972; cited by OECD, 1994); RTECS (2000) |
|
Rabbit (sex and strain n. p.) |
LD100 ~ 1.4 g/kg (in 15% olive oil) |
Monsanto Co. (1947) |
The information from literature is generally of very low validity: very old, with no information available on test methods and product tested.
Additional information available from cross-reading (o-TSA and mixture of o/p-TSA) also support these findings generally low acute systemic toxicity.
Dermal:
Data is available from cross-reading with a product containing a mixture of ortho-toluene sulfonamide (o-TSA: 30%) and para-toluenesulfonamide (p-TSA: 70%) itself. The report is of low validity, but it indicates that levels of 7500 mg/kg bw do not result to any signs of toxicity when exposed to the skin as 25% suspension in corn oil. Besides the cross-reading to o-TSA, this also indicates no toxicity from at least 5000 mg p-TSA that is present at about 70% in the final product.
Further support is available from information on dermal absorption: p-TSA is of low acute oral toxicity, not requiring classification. Also no classification is required for skin or eye irritation. Information on absorption indicates that p-TSA is rapidly and completely absorbed by oral route, but only 20% by dermal route. Further acute testing by dermal route is therefore scientifically unjustified.
Inhalation:
vp is (less than) 2.86*10-7 kPa (= 0.0003 Pa) @ 20°C, and the respirable fraction (≤ 4 µm) of the crystalline solid is 0 %. Additionally, the likelihood of exposures by aerosols from the use of the substance is also low (water solubility is low with 3.1 g/L at 20°C).
Although no data is available via inhalation route, similar low toxicity can be expected.
Justification for selection of acute toxicity – oral endpoint
Key study.
Justification for selection of acute toxicity – inhalation endpoint
In accordance with column 2 of REACH Annex VIII, the test for acute inhalation toxicity (required in section 8.5) does not need to be conducted. Vp is low ( less than 2.86*10-7 kPa (= 0.0003 Pa) @ 20°C), and the crystalline solid is of low dustiness (the respirable fraction (≤ 4 µm) is 0%). In combination of low likelihood of exposures by aerosols from the use of the substance and the general low acute toxicity, testing of acute toxicity by inhalation is not necessary.
Justification for selection of acute toxicity – dermal endpoint
Data from cross-reading and limited validity. No other data available.
Justification for classification or non-classification
Available information indicates no toxicity by dermal route, and low oral toxicity with an LD50 of 2330 mg/kg resulting to a GHS classification for acute oral toxicity of Cat.5. In the EU however no classification is needed.
By inhalation route no data is available, but similar low toxicity can be expected.
Consequently no classification for acute toxicity is required for EU CLP.
The acute oral studies show effects of neurodepression at near lethal doses. Due to low dermal absorption, and unlikely exposures via inhalation (very low vp, solid with no respirable fraction) and general low exposures, no narcotic effects will occur in humans. Classification for STOT-SE Cat.3 for narcotic effects is therefore not indicated.
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.
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