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EC number: 201-286-1 | CAS number: 80-51-3
- 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
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- 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
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:
- 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was performed in accordance with OECD guideline 401 and GLP standard.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- not specified
- Principles of method if other than guideline:
- NA
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: no data
- Age at study initiation: 5 weeks
- Weight at study initiation: 157-197g for male, 132-151g for female
- Fasting period before study: Rats were fasted for approximately 16 hours prior to dosing the test substance, but drinking water was freely ingested in the cage.
- Housing: no data
- Diet (e.g. ad libitum): no data
- Water (e.g. ad libitum): ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): no data
- Humidity (%): no data
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): no data
IN-LIFE DATES: no data - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle:
- Amount of vehicle (if gavage):
- Justification for choice of vehicle:
- Lot/batch no. (if required):
- Purity:
MAXIMUM DOSE VOLUME APPLIED:
DOSAGE PREPARATION (if unusual):
CLASS METHOD (if applicable)
- Rationale for the selection of the starting dose: - Doses:
- 0, 1000, 2000 and 3000 mg/kg
- No. of animals per sex per dose:
- 5 males and 5 females per dose group
- Control animals:
- yes
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: The animals were observed for clinical signs of toxicity just before the administration at 1, 2, 3, 4, 5, and 6 hrs after dosing on day 1 and once a day until day 14. Individual body weights of animals were measured just before the administration, on day 3, 7 and the day of necropsy.
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight,necropsy - Statistics:
- The body weight changes were analyzed using the Student’s t-test.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- >= 1 000 - <= 2 000 mg/kg bw
- Mortality:
- During the observation period, all males and four females died at both 2,000 and 3,000 mg/kg bw.
- Clinical signs:
- other: In case of dead rats, the paralysis of forelimb and hindlimb, cloudy eyeball, and lacrimation on day 2 after the administration were observed in those groups. The slight paralysis of hindlimb was observed in 2 males and 2 females at 1,000 mg/kg bw and 1 f
- Gross pathology:
- Dead animals of the 2,000 and 3,000 mg/kg groups showed dark-red discoloration of the brain and lung, and the atrophic thymus and spleen. In scheduled necropsy, however, no macroscopic abnormalities were seen in the surviving animals.
- Other findings:
- None
- Conclusions:
- The acute oral toxicity of OBSH was assessed in rats following a single administration of OBSH. The study was performed in compliance with OECD guideline 401. The acute oral median lethal dose (LD50) of OBSH was estimated to be between 1000 and 2000 mg/kg bw under the test conditions.
According to CLP criteria OBSH should be classified as Acute tox 4; H302. - Executive summary:
This study was conducted to assess the acute toxicity of OBSH following a single oral administration of 0, 1000, 2000 and 3000 mg/kg bw. This study is performed in accordance with the testing guideline OECD (401).
Groups of five males and five female fasted rats were given OBSH as a single dose on Day 1 by oral gavage at a dose level of 0, 1000, 2000 and 3000 mg/kg. OBSH was administrated in corn oil.
Following a single administration of OBSH to rats, the acute median lethal oral dose for male and female rats was estimated to be between 1000 and 2000 mg/kg bw under the test conditions.
According to CLP criteria OBSH should be classified as Acute tox 4; H302.
Reference
Table1. Mortality and clinical signsof the acute oral toxicity
Sex |
Group |
No. of animals |
Findings |
Days after treatment |
|||||||||||||
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
||||
Male |
C |
5 |
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
T1 |
5 |
N |
5 |
5 |
5 |
4 |
3 |
4 |
4 |
3 |
3 |
3 |
3 |
3 |
3 |
3 |
|
P* |
|
|
|
1 |
2 |
1 |
1 |
2 |
2 |
2 |
2 |
2 |
2 |
2 |
|||
T2 |
5 |
N |
5 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
P |
|
5 |
5 |
5 |
5 |
|
|
|
|
|
|
|
|
|
|||
C |
|
5 |
4 |
5 |
5 |
|
|
|
|
|
|
|
|
|
|||
L |
|
|
|
5 |
5 |
|
|
|
|
|
|
|
|
|
|||
D |
|
|
|
|
|
5 |
|
|
|
|
|
|
|
|
|||
T3 |
5 |
N |
5 |
|
1 |
1 |
1 |
|
|
|
|
|
|
|
|
|
|
P |
|
5 |
4 |
1 |
1 |
1 |
|
|
|
|
|
|
|
|
|||
C |
|
|
2 |
1 |
1 |
1 |
1 |
|
|
|
|
|
|
|
|||
H |
|
|
|
|
|
1 |
1 |
|
|
|
|
|
|
|
|||
L |
|
|
1 |
1 |
1 |
1 |
|
|
|
|
|
|
|
|
|||
D |
|
|
|
3 |
|
1 |
|
1 |
|
|
|
|
|
|
|||
Female |
C |
5 |
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
T1 |
5 |
N |
5 |
4 |
4 |
3 |
3 |
3 |
3 |
4 |
5 |
5 |
5 |
5 |
5 |
5 |
|
P* |
|
1 |
1 |
2 |
2 |
2 |
2 |
1 |
|
|
|
|
|
|
|||
T2 |
5 |
N |
5 |
|
|
|
|
|
|
|
|
|
|
|
|
1 |
|
P |
|
5 |
4 |
2 |
1 |
|
|
|
|
|
|
|
|
|
|||
C |
|
|
1 |
|
|
|
|
|
|
|
|
|
|
|
|||
P* |
|
|
|
1 |
2 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
|
|||
D |
|
|
1 |
1 |
|
2 |
|
|
|
|
|
|
|
|
|||
T3 |
5 |
N |
5 |
2 |
2 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
1 |
|
P |
|
3 |
3 |
4 |
3 |
1 |
|
|
|
|
|
|
|
|
|||
D |
|
|
|
|
1 |
2 |
1 |
|
|
|
|
|
|
|
Table 2. Body weights of male and female rats
Group |
|
Mean body weight (g) of males |
Mean body weight (g) of females |
||||||
Day 0 |
Day 3 |
Day 7 |
Day 14 |
Day 0 |
Day 3 |
Day 7 |
Day 14 |
||
C |
Mean |
153.3 |
194.7 |
232.1 |
296.6 |
125.1 |
153.2 |
172.8 |
195.7 |
|
S.D. |
11.1 |
12.0 |
15.1 |
20.7 |
4.2 |
6.9 |
8.6 |
13.3 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
T1 |
Mean |
160.9 |
172.2 |
201.8 |
274.6 |
127.7 |
142.0 |
165.1 |
196.5 |
|
S.D. |
7.1 |
23.9 |
41.8 |
39.2 |
5.0 |
10.4 |
7.1 |
9.8 |
|
N |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
T2 |
Mean |
163.7 |
141.1** |
0.0 |
0.0 |
123.2 |
109.6** |
120.4 |
162.4 |
|
S.D. |
8.0 |
10.9 |
0.0 |
0.0 |
5.7 |
3.8 |
0.0 |
0.0 |
|
N |
5 |
5 |
0 |
0 |
5 |
5 |
1 |
1 |
T3 |
Mean |
160.2 |
134.4** |
108.6 |
0.0 |
128.0 |
123.8* |
186.0 |
215.0 |
|
S.D. |
9.3 |
7.1 |
0.0 |
0.0 |
5.9 |
19.4 |
0.0 |
0.0 |
|
N |
5 |
5 |
1 |
0 |
5 |
5 |
1 |
1 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 500 mg/kg bw
- Quality of whole database:
- The study was performed in accordance with OECD guideline 401 and GLP standard - Klimisch score 1.
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- March 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 436 (Acute Inhalation Toxicity: Acute Toxic Class Method)
- Deviations:
- no
- Principles of method if other than guideline:
- NA
- GLP compliance:
- yes
- Test type:
- acute toxic class method
- Limit test:
- no
- Specific details on test material used for the study:
- Identity: 4,4’-Oxybis(benzenesulfonyl hydrazide) (OBSH)
CAS No. : 80-51-3
EC No.: 201-286-1
Test facility Code No.: K-5450
Batch/Lot No.: 201512001
Appearance White fine powder
Purity: 99.5 - 100%
Storage conditions: Room temperature, Protected from light, Protected from moisture
Expiry date: 2016.12 - Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Species Rat (Specific Pathogen Free)
Strain/Substrain Sprague-Dawley/Crl:CD (SD)
Number at receipt 20 (Male 10, Female 10)
Number on study start 12 (Male 6, Female 6)
Number on study end 12 (Male 6, Female 6)
Age range at receipt Approximately 8 weeks
Age range on study start Approximately 9 weeks (1st step) Approximately 10 weeks (2nd step) '
Body weight range Male: 312.4-337.2 g at the start of exposure (1st step) Male: 341.6-359.4 g at the start of exposure (2nd step) Female: 196.0-213.5 g at the start of exposure (1st step) Female: 204.1-217.6 g at the start of exposure (2nd step)
Supplier Orient Bio Inc. 322, Galmachi-ro, Jungwon-gu, Seongnam-si, Gyeonggi-do 13201, Republic of Korea Method of identification Color marking, Tail tattoo, Cage card
Acclimation period 5 days Pre-treatment period 2 days (1st step) 6 days (2nd step)
Replacement There was no replacement of the animals.
During pre-treatment period, 1 time of holder adaptation training was performed according to KIT SOP in order to decrease a stress that could be resulted from nose-only inhalation exposure
Housing and Animal Care:
Animal and exposure room No.
Animal room No.: F103, Exposure room No.: F102 (Inhalation toxicology building)
Housing
Animals were housed in groups of up to 3 animals in suspended, stainless-steel cage (255W×465L×200H mm) for the acclimation period, pre-treatment and exposure period.
Environment
The animal room environment was automatically controlled according to SOPs (target range: temperature 22 ± 3°C, relative humidity 30-70%, approximately 12 hours light cycle with 150-300 Lux, and ventilation 10-20 times/hour). Temperature and relative humidity were monitored continuously. Animal room and cage cleaning was performed according to KIT SOPs.
Identification for cage and animal room and exposure room
Cage card were attached to the cages. The animal room use record was displayed in the animal room and the exposure room use record use record was also displayed in the exposure room.
Food and Water
A standard rat and mouse pellet diet (Lab Diet® #5053, PMI Nutrition International, USA; irradiated by gamma-ray) was provided to the animals ad libitum. Microbial monitoring for diet was performed at test facility and a certificate of analysis for the diet was provided by the supplier. The animals have had ad libitum access to filtered, ultraviolet light-irradiated municipal tap water at all times. The drinking water was analyzed every 6 months for specified contaminants in the Gwangju Health & Environment Research Institute (149, Hwajeong-ro, Seo-gu, Gwangju, 61986, Republic of Korea). There were no known contaminants in the food or water at levels that would be expected to interfere with the results of the study and the data were maintained in the raw data. - Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- nose only
- Vehicle:
- not specified
- Remark on MMAD/GSD:
- Mass median aerodynamic diameters (MMADs) were 2.22 and 2.26 μm and geometric standard deviations (GSDs) were 2.02 and 1.92 for 1st step exposure, respectively.
Mass median aerodynamic diameters (MMADs) were 2.47 and 2.48 μm and geometric standard deviations (GSDs) were 2.00 and 2.03 for 2nd step exposure, respectively. - Details on inhalation exposure:
- Exposure method of test item:
Test item was generated using dust generator [DF-3 Special, Sibata] and then supplied to the nose-only exposure inhalation experiment device [SIS-30BN, Sibata].
Chamber and conditions inside chamber:
Nose-only exposure inhalation experiment device [SIS-30BN, Sibata] Temperature was targeted to be maintained at 22 ± 3°C and relative humidity was targeted to be maintained in the range of 50 ± 20%. As well, oxygen concentration was targeted to be maintained above 19% and carbon dioxide concentration was targeted to be maintained below 1%.
Measurement and Monitoring of Exposure:
Nominal concentration: Total amount of test items used for generation of test item / Total volume of air supplied into chamber
Actual concentration: Exposure concentration of test item was measured 3 times by gravimetric analysis using microglass fiber filter during exposure, and then actual concentration (mass concentration) of exposed test item was assessed.
Environmental conditions of inhalation chamber:
Temperature, relative humidity, chamber airflow, chamber pressure, oxygen concentration and carbon dioxide concentration were monitored and recorded at least hourly during exposure.
Oxygen concentration was measured by multi-gas monitor [M40, ISC] and carbon dioxide concentration was measured by carbon dioxide meter [PGM-6208, RAE Systems].
Particle size distribution:
Particle size of the generated and exposed test item was measured 2 times during exposure by cascade impactor [Mini MOUDI 135-6S, MSP Corporation].
Mass median aerodynamic diameter (MMAD) with geometric standard deviation (GSD) was assessed based on measured values using Microsoft Excel® software (Microsoft Corporation, USA).
Method Verification (Inhalation Exposure Validation):
The chamber homogeneity on generated and exposed test item was performed during acclimation period. - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- The rats were assigned to two groups (3 animals/sex/group) and were exposed nose-only to target concentrations of 1.00 mg/L (1st step exposure) or 5.00 mg/L (2nd step exposure) of 4,4’-Oxybis(benzenesulfonyl hydrazide) (OBSH) for 4 hours.
Mean exposure concentration (actual concentration) of test item of 1st step and 2nd step were 1.06 ± 0.07 mg/L and 4.78 ± 0.30 mg/L for 4 hours, respectively - No. of animals per sex per dose:
- 3 animals per sex per dose
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: At receipt, at randomization, on day 1, 2, 5, 8 and 14 and at necropsy.
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight and macrosopic findings - Key result
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 5 mg/L air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Mortality:
- There were no unscheduled deaths in both sexes of 1st or 2nd step exposure group during the study period.
- Clinical signs:
- other: There were no test item-related clinical signs in both sexes of 1st or 2nd step exposure group during the study period
- Body weight:
- After acute inhalation exposure, body weights in both sexes of 1st and 2nd step exposure groups were transiently decreased on Day 2. Body weight gains in both sexes of 1st and 2nd step exposure groups were also transiently delayed on Day 2. But afterward, these were recovered.
- Gross pathology:
- There were no test item-related gross changes in both sexes of 1st or 2nd step exposure group
- Other findings:
- NA
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The acute inhalation toxicity of 4,4’Oxybis(benzenesulfonyl hydrazide) (OBSH) was evaluated in accordance to OECD 436 in both sexes of Sprague-Dawley rats. The rats were assigned to two groups (3 animals/sex/group) and were exposed nose-only to target concentrations of 1.00 mg/L (1st step exposure) or 5.00 mg/L (2nd step exposure). No effects were seen, thus the LC50 was > 5.00 mg/L (actual concentration 4.78 mg/L) and GHS criteria for classification was not meet.
- Executive summary:
The acute inhalation toxicity of 4,4’Oxybis(benzenesulfonyl hydrazide) (OBSH) was evaluated in accordance to OECD 436 in both sexes of Sprague-Dawley rats. The rats were assigned to two groups (3 animals/sex/group) and were exposed nose-only to target concentrations of 1.00 mg/L (1st step exposure) or 5.00 mg/L (2nd step exposure) for 4 hours.
The mean exposure concentration (actual concentration) of OBSH for the 1st step and 2nd step were 1.06 ± 0.07 mg/L and 4.78 ± 0.30 mg/L for 4 hours, respectively. Mass median aerodynamic diameters (MMADs) were 2.22 and 2.26 μm and geometric standard deviations (GSDs) were 2.02 and 1.92 for 1st step exposure, respectively. Mass median aerodynamic diameters (MMADs) were 2.47 and 2.48 μm and geometric standard deviations (GSDs) were 2.00 and 2.03 for 2nd step exposure, respectively.
No unscheduled death were seen as well as no clinical signs or gross changes. Transient body weight decreases were observed in males and females of 1st and 2nd exposure groups at Day 2 but it was recovered afterward.
In conclusion, no effects were seen, thus the LC50 was > 5.00 mg/L (actual concentration 4.78 mg/L) and GHS criteria for classification was not meet in this study.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Quality of whole database:
- A recently performed OECD 436 study performed in accordance to GLP standards - Klimisch score 1.
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
- Quality of whole database:
- No reliable dermal acute toxicity study is available. A dermal toxicity study (reliability score 4) is available using 200 mg/kg of OBSH. No effeccts were seen after 24 hours. The original reference is not available. This study was not conducted according to GLP standard.
Additional information
The acute oral toxicity of OBSH was assessed in rats following a single administration of OBSH. Two studies were performed in compliance with OECD guideline 401.
In one study, groups of five males and five female fasted rats were given OBSH as a single dose by oral gavage at a dose level of 0, 1000, 1500 and 2000 mg/kg. OBSH was administered in corn oil. LD50 was just above 2000 mg/g bw. In another study, groups of five males and five female fasted rats were given OBSH as a single dose on Day 1 by oral gavage at a dose level of 0, 1000, 2000 and 3000 mg/kg. OBSH was administered in corn oil. Based on the results from these studies, the acute oral median lethal dose (LD50) of OBSH was estimated to be between 1000 and 2000 mg/kg bw under the test conditions.
The acute inhalation toxicity of OBSH was evaluated in accordance to OECD 436 in both sexes of Sprague-Dawley rats. The rats were assigned to two groups (3 animals/sex/group) and were exposed nose-only to target concentrations of 1.00 mg/L (1st step exposure) or 5.00 mg/L (2nd step exposure). No effects were seen, thus the LC50 was > 5.00 mg/L (actual concentration 4.78 mg/L) and GHS criteria for classification was not meet.
No reliable dermal acute toxicity study is available.
Justification for selection of acute toxicity – oral endpoint
The study is a key study
Justification for selection of acute toxicity – inhalation endpoint
The study is a key study
Justification for selection of acute toxicity – dermal endpoint
A dermal toxicity study (reliability score 4) is available using 200
mg/kg of OBSH. No effeccts were seen after 24 hours. The original
reference is not available. This study was not conducted according to
GLP standard.
Justification for classification or non-classification
According to CLP criteria OBSH should due to the oral LD50 value in the range of 1000-2000 mg/kg bw be classified as Acute tox 4; H302.
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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