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EC number: 225-878-4 | CAS number: 5131-66-8
- 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
Endpoint summary
Administrative data
Description of key information
GLP-studies according to OECD guidelines 401, 403 and 402 (limit test) are available for PnB. Those key studies are supported by several non-GLP studies similar to the OECD guidelines.
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:
- 1987
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- GLP compliance:
- yes (incl. QA statement)
- 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:
- TEST ANIMALS
- Source: Charles River Wiga GmbH
- Age at study initiation: 8-9 weeks
- Weight at study initiation: 343 to 416 g (males) & 207 to 269 g (females)
- Fasting period before study: Animals were fasted overnight prior to dosing and were not allowed food until 5.5 hr after dosing.
- Housing: polycarbonate cages
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-21°C
- Humidity (%): 50-70%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- other: no vehicle; test material was tested indiluted
- Details on oral exposure:
- substance dosed undiluted via oral gavage
- Doses:
- 1800, 2400, 3200 mg/kg body weight
- No. of animals per sex per dose:
- 5
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: Subjects were observed for mortality and signs of toxicity several times on the day of dosing (Day 0) and on weekdays thereafter for up to 14 additional days.
- Frequency of observations and weighing: Body weights were recorded immediately prior to dosing, weekly thereafter, and at death.
- Necropsy of survivors performed: Non-survivors were necropsied as soon as possible and surviving animals were subjected to necropsy on day 14.
- Other examinations performed: clinical signs, body weight - Preliminary study:
- To establish an appropriate dose range four groups of animals, each comprising 1 male and 1 female, were dosed with an oral dose of the test substance at 1000, 1800, 3200 and 5600 mg/kg body weight, respectively. Mortalities occurred in the 3200 and 5600 mg/kg dose group (both animals). Major signs of toxicity were lethargy, hyperpnoea and dacryorrhoea. The observation period was 7 days.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 3 300 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- 2 800 - 4 500
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 5 500 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: no confidence limits
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 2 700 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- 2 400 - 3 600
- Mortality:
- 1800 mg/kg: 0/10
2400 mg/kg: 1/10
3200 mg/kg: 5/10 - Clinical signs:
- other: Signs of toxicity were lethargy, comatose, hypopnoea, gasping respiration amd rough coat. For surviving animals these signs were reversible within 2 days.
- Gross pathology:
- Maroscopic examination of animals at necropsy revealed haemorrhage of the stomach, bloody or yellow content of the small intestines, haemorrhage of the small intestines, bloody content of the bladder, hyperaemia of the bladder.
- Other findings:
- none
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Oral LD50 of 3300 mg/kg: no EU classification for acute oral toxicity.
- Executive summary:
Three groups of Wistar rats (5/sex/dose level) received
single oral doses of 1800, 2400, or 3200 mg/kg propylene
glycol n-butyl ether (PnB), administered undiluted using a
stainless steel stomach cannula attached to a syringe.No rats died from a dose of 1800 mg/kg PnB. One female died
after a dose of 2400 mg/kg. Four females and one male died
at 3200 mg/kg. The calculated oral LD50 for males alone was
5500 mg/kg (no 95% confidence limits), for females alone was
2700 mg/kg (95% CL: 2400 - 3600 mg/kg), and for both sexes
combined was 3300 (95% CL: 2800 - 4500 mg/kg).
All deaths occurred within one day of dosing. Adverse signs
included weight loss, lethargy, coma, hypopnea, gasping, and
dacryorrhea. Surviving rats showed no adverse signs by day
2. At necropsy, surviving rats showed no grossly observable
lesions. Rats dying from treatment exhibited hemorrhage of
the stomach and small intestine, bloody content of the small
intestine and bladder, yellow liquid within the small
intestine, and hyperemia of the bladder.- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 26.06.2001 To 09.10.2001
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 tris (Acute Oral Toxicity - Acute Toxic Class Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1100 (Acute Oral Toxicity)
- Deviations:
- no
- GLP compliance:
- yes
- Remarks:
- Department of Experimental Toxicology and Ecology, BASF AG
- Test type:
- acute toxic class method
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland GmbH, Sandhofer Weg 7, 97633 Sulzfeld
- Age at study initiation: male animals approx. 8-12 weeks, female animals approx. 14 -18 weeks
- Weight at study initiation: mean 215 g (males), 208 g (females)
- Fasting period before study: at least 16 hours before admínístratíon, but water was available ad libitum
- Housing: single housing in stainless steel wire mesh cages, type DK-III (Becker & Co., Castrop-Rauxel, FRG)
- Diet (e.g. ad libitum): Kliba-Labordiät; Provimi Kliba SA, Kaiseraugst, Switzerland; ad libitum
- Water (e.g. ad libitum): tap water; ad libitum
- Acclimation period: at least 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 30 - 70
- Photoperiod (hrs dark / hrs light): 12 / 12 - Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 20 g/100 ml
- Amount of vehicle (if gavage): 10 ml/kg bw
- Justification for choice of vehicle: aqueous formulation corresponds to the physiological medium
MAXIMUM DOSE VOLUME APPLIED: 10 ml/kg bw
CLASS METHOD (if applicable)
- Rationale for the selection of the starting dose: based on the physical and chemical characteristics of the test substance and its composition, no pronounced acute oral toxicity was expected - Doses:
- 2000 mg/kg
- No. of animals per sex per dose:
- 6
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: recording of signs and symptoms several times on the day of administration, at least once each workday for the individual animals. Individual body weights shortly before administration (day 0), weekly thereafter and at the end of the study (before fasting
period). Additionally, at day of death in animals that died or were sacrificed moribund starting with study day 1.
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight, mortality - Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Mortality:
- One female animal and 1 male animal died during hour 2 and on study day 3, respectively.
- Clinical signs:
- other: Males: impaired and poor general state, dyspnoea, apathy, squatting posture, abdominal and lateral position, staggering, ataxia, atonia, paresis, narcotic-like state, absent pain and corneal reflex, piloerection, and smeared fur were observed from hour 0
- Gross pathology:
- Several black erosions/ulcers of the glandular stomach were observed in males that died.
No histopathological abnormalities were found in the other animals. - Interpretation of results:
- GHS criteria not met
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 3 300 mg/kg bw
- Quality of whole database:
- Good (Klimisch 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:
- 10/1987 to 01/1989
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Principles of method if other than guideline:
- Method: other: Protocol guideline not specified in report. However, protocol meets criteria specified in OECD 403 "Acute Inhalation Toxicity."
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratory, Kingston, NY
- Age at study initiation: 11 weeks
- Weight at study initiation: ca. 150 g (females) and ca. 240 g (males)
- Fasting period before study: none
- Housing: 2 per cage in suspended stainless steel wire mesh cages
- Diet (e.g. ad libitum): ad libitum except during exposure
- Water (e.g. ad libitum): ad libitum except during exposure
- Acclimation period: 4 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 25°C (during exposure)
- Humidity (%): 48% (during exposure)
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: none
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Rochester-type stainless steel and glass exposure chambers under dynamic air flow conditions
- Exposure chamber volume: 112 liter
- Source and rate of air: 30 l/min
- Method of conditioning air: Vapors of PnB were generated using a glass J-tube method. Liquid test material was metered into the J-tube. Compressed air, heated with a flameless torch (FHT-4, Master Appliance, Racine, WI) to the minimum extent necessary, passed through the J-tube to volatilize the test material.
- Treatment of exhaust air:
- Temperature, humidity: 25°C, 48%
TEST ATMOSPHERE
Air flow through each chamber was determined with a rotameter. The rotameter was calibrated with an AL-1400 gas meter prior to the start of the study. The temperature in the chamber was controlled by a system designed to maintain temperature at approximately 22°C. Temperature, air flow and relative humidity values were recorded every 30 minutes during the four-hour exposure period.
The analytical concentration of PnB in the breathing zone of the animals was determined by gas chromatography using a flame ionization detector. The gas chromatographic conditions were as follows: helium flow = 30 ml/min, hydrogen flow = 30 ml/min, air flow = 300 ml/min, oven = 110°C and detector = 180°C. A 6 foot x 1/8 inch stainless steel column packed with 10% OV-101 on 100/120 mesh Chromosorb WHP was used for separation of the test material from air. The gas chromatographwas calibrated with air standards of PnB which were prepared by injecting measured volumes of PnB into SARAN bags containing measured volumes of dry, compressed air. - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- 651 ppm
- No. of animals per sex per dose:
- 5
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Animals were observed for overt signs of toxicity during the exposure period (day 1) and after for 14 additional days. Rats were weighed prior to exposure and on days 2, 4, 8, 11 and 15.
- Necropsy of survivors performed: yes (including examination of the eyes)
- Other examinations performed: clinical signs, body weight, ophthalmological examination, behaviour pattern and nervous system activity - Statistics:
- Means and standard deviations of animal body weights, chamber temperatures, relative humidities, and chamber air flows were calculated for descriptive purposes.
- Sex:
- male/female
- Dose descriptor:
- LC0
- Effect level:
- > 651 ppm
- Exp. duration:
- 4 h
- Mortality:
- no deaths
- Clinical signs:
- other: No clinical signs were observed either during the exposure or throughout the subsequent two-week observation period.
- Body weight:
- Body weights appeared normal during the observation period.
- Gross pathology:
- Gross pathologic examination at the end of the two-week observation period revealed no treatment-related lesions.
- Other findings:
- none
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The LC0 is greater than 651 ppm: no EU classification for acute inhalation toxicity.
- Executive summary:
A single group of Fischer 344 rats (5/sex) was exposed in whole-body inhalation chambers for 4 hours to vapors of propylene glycol n-butyl ether at a measured concentration of 651 ppm. Chambers were 112 liters in volume and airflow was 30 liters/min. Animals were observed for overt signs of toxicity during the exposure period (day 1) and after for 14 additional days. Rats were weighed prior to exposure and on days 2, 4, 8, 11 and 15.
No rats died when exposed to 651 ppm propylene glycol n-butyl ether for 4 hours. No signs of toxicity during or after exposure were noted and no lesions were observed at necropsy except for a unilateral distension of the ovarian
bursa in one female. This lesion was considered unrelated to exposure since it occasionally occurs in unexposed
females.The highest attainable concentration of PnB under ambient conditions of exposure was not toxic to rats following a single four-hour exposure. Therefore, the potential for acute inhalation toxicity is very low for this material.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- Good (Klimisch 1)
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1987
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Wiga GmbH
- Age at study initiation: ca. 8 weeks
- Weight at study initiation: ca. 217 g (females) and 327 g (males)
- Fasting period before study: none
- Housing: individually housed in polycarbonate cages
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-21°C
- Humidity (%): 30-70%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12 - Type of coverage:
- semiocclusive
- Vehicle:
- other: Test material was tested undiluted.
- Details on dermal exposure:
- TEST SITE
- Area of exposure: upper dorso-lateral area
- % coverage: 10
- Type of wrap if used: surgical gauze fixed to aluminium foil
REMOVAL OF TEST SUBSTANCE
- Washing (if done): After removal of the semi-occlusive bandage the remaining test substance was on the treated surface was gently removed with tissues moistened with tap-water.
- Time after start of exposure: 24 hours
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): dose volume was calculated based on the specific gravity of 0.88 g/ml
- Concentration (if solution): undiluted
- Constant volume or concentration used: constant concentration
VEHICLE
no vehicle used - Duration of exposure:
- 24 hours
- Doses:
- 2000 mg/kg body weight
- No. of animals per sex per dose:
- 5
- Control animals:
- not specified
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: On the day of treatment (day 0), animals were observed for toxicity and morbidity approximately every two hours. Subjects were checked once daily thereafter except for weekends and holidays. Individual body weights were recorded on test days 0, 7, and 14. The treated areas of skin were examined on test days 4, 7, and 14 for signs of irritation.
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Mortality:
- no deaths
- Clinical signs:
- other: No signs of systemic toxicity were observed during exposure and the following 14-day observation period. The treated skin surface of the animals showed no abnormalities.
- Gross pathology:
- Macroscopic examination of all animals at the end of the study revealed no test substance related gross abnormalities.
- Other findings:
- none
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- The acute dermal LD50 for PnB is >2000 mg/kg bodyweight: no EU classification for acute dermal toxicity.
- Executive summary:
A group of 5 male and 5 female Wistar rats was treated with a single application of 2,000 mg/kg propylene glycol n-butyl ether applied topically to the clipped, intact skin under
occlusion for a period of 24 hours. Subjects were observed for clinical signs of toxicity and mortality during the
application period and for a period of 14 days after removal of the test material. The skin of the rats at the site of
application was also evaluated for signs of irritation over the course of the study. The undiluted test material was
applied at a single dose of 2,000 mg/kg to approximately 10% of the total body surface area of skin (clipped,
non-abraded) of the rats. The test material was applied to gauze patches, which were then affixed to the clipped area
of the skin and covered with foil and wrapped with a bandage around the torso. The test material was held in contact
with the skin for a period of 24 hours whereupon it was removed and the treated area was washed with water to remove remaining test material. On the day of treatment (day 0), animals were observed for toxicity and morbidity
approximately every two hours. Subjects were checked once daily thereafter except for weekends and holidays.
Individual body weights were recorded on test days 0, 7, and 14. The treated areas of skin were examined on test days 4, 7, and 14 for signs of irritation. Animals were sacrificed on day 14 and subjected to gross necropsy.No deaths, clinical signs of toxicity, or skin irritation occurred over the course of the study. The dermal LD50 for
propylene glycol n-butyl ether is greater than 2,000 mg/kg for male and female Wistar rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- Good (Klimisch 1)
Additional information
The studies with a Klimisch rating 1 have been selected as key studies for the hazard assessment.
Oral - The oral LD50 value for propylene glycol butyl ether in experiments in rats ranges from 2500 to 5200 mg/kg. There are two key studies conducted on rats identified for acute oral toxicity - Dow, 1987 with combined (male and female) LD50 value of 3300 mg/kg and BASF SE (2001) with the combined (male and female) LD50 value of > 2000 mg/kg, based on the most reliable study (Klimisch 1) will be taken forward for the risk assessment.
Inhalation - No mortality was observed in any of the acute inhalation studies in rats. The key study identified is the Dow, 1989 study in rats and the LC0 value was > 651 ppm or 3515 mg/m3 (highest attainable concentration under ambient conditions of exposure), this value will be taken forward for the risk assessment.
Dermal - Dermal LD50 values in rats range from 1400 to 3133 mg/kg. The key study identified for acute dermal toxicity is the Dow, 1989 study in rats with the LD50 value of > 2000 mg/kg, based on the most reliable study (Klimisch 1) will be taken forward for the risk assessment. This was supplemented with one supporting publication (Smyth et al., 1974) in rabbits with a dermal LD50 of 3133 mg/kg body weight.The lowest value of 1400 mg/kg in rabbits is from the Smyth, 1969 publication and there is not much information with regards to the purity of the material tested and hence this value will not be used for risk assessment.
Justification for selection of acute toxicity – oral endpoint
GLP study according to OECD guideline
Justification for selection of acute toxicity – inhalation endpoint
GLP study according to OECD guideline
Justification for selection of acute toxicity – dermal endpoint
GLP study according to OECD guideline
Justification for classification or non-classification
LD50 values for oral and dermal route > 2000 mg/kg/bw.
Inhalation exposure to the highest attainable vapor concentration of PnB (651ppm/3515mg/m3) did not reveal any substance related adverse effects.
According to the EU criteria for classification and labeling, PnB is not classified for acute toxicity for any route of exposure.
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