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EC number: 406-880-6 | CAS number: 88917-22-0 ACETATE DPMA ACROSOLV; ACROSOLV DPMA ACETAT; ACROSOLV DPMA ACETATE; DOWANOL DPMA; DOWANOL DPMA GLYCOL ETHER; DOWANOL DPMA GLYKOL ETHER; ETHER DE GLYCOL DPMA DOWANOL
- 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
A GLP-study according to OECD guideline 407 is available for dipropylene glycol methyl ether acetate. This data is supported by GLP-studies equivalent to OECD guidelines 407 and 413 for dipropylene glycol methyl ether. Further, several studies according to or similar to OECD guidelines 411 and 413 are provided for propylene glycol methyl ether and dipropylene glycol methyl ether.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline 407.
- Qualifier:
- according to guideline
- Guideline:
- other: Annex V, Published in the official journal of E.C.(No. L25I, 19 September 1984)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River ( UK )
- Age at study initiation: 5-6 week
- Weight at study initiation: Male -144-150 gms and Female - 107 - 111 gms
- Housing: Rats were housed 2 or 3 of one sex per cage in suspended polypropylene cages with stainless steel wire grid tops and bottoms
- Diet ( ad libitum): SQC Expanded rat and mouse maintenance diet No. 1 supplied by special diet services limited,Stepfield, Witham, Essex, CM8 3 AB.
- Water ( ad libitum):Tap water
- Acclimation period: 8 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 18 °C - 22 °C
- Humidity (%): 45 - 65 %
- Air changes (per hr): 15-20
- Photoperiod : (12hrs dark / 12hrs light)
- Route of administration:
- oral: gavage
- Vehicle:
- other: Distilled water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: Dosing solutions were prepared daily using distilled water as vehicle.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- See the attachment - 2
- Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- Daily
- Remarks:
- Doses / Concentrations:
100 mg/kg
Basis:
other: nominal concentration - Remarks:
- Doses / Concentrations:
250 mg/kg
Basis:
other: nominal concentration - Remarks:
- Doses / Concentrations:
1000 mg/kg
Basis:
other: nominal concentration - No. of animals per sex per dose:
- 5 animals per sex per dose
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Dose selection rationale: Dose levels were selected for this is on the basis of preliminary one week oral range finding study , conducted by Inveresk Research International.
- Positive control:
- no data
- Observations and examinations performed and frequency:
- -CAGE SIDE OBSERVATIONS: No
-DETAILED CLINICAL OBSERVATIONS: Yes, Weekly
-BODY WEIGHT: Yes
-Water Consumption : Yes, Weekly
-Time schedule for examinations: Weekly
-FOOD EFFICIENCY: Not Examined
-OPHTHALMOSCOPIC EXAMINATION: No
-HAEMATOLOGY: Yes
- Time schedule for collection of blood: During 4th week of dosing
- Anaesthetic used for blood collection: Yes ( Light Ether Anaesthesia )
- Animals fasted: Yes
- How many animals: 40
- Parameters checked : Hb, RBC, HCT, MCH, MCV, MCHC, WBC, DLC
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood:During 4th week of dosing
- Animals fasted: Yes
- How many animals: 40
- Parameters checked : BUN, Glu, AST, ALT, AP,Na, K, Cl, TP, Alb, AG-R, Crea, Ca, Phos, T. Bl.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Other examinations:
- none
- Statistics:
- Hematology, Clinical chemistry, organ weight and body weight data were statistically analysed for homogeneity of variance using the F-max test. If the group variances appeared homogenous a parametric ANOVA was used and pairwise comparisons made via student’s T test using Fischer’s F- protected LSD. If the variances were heterogeneous log or square root transformations were used in an attempt to stabilize the variances. If variances remained heterogeneous then a non parametric test such as Kruskal- Wallis ANOVA was used.
Organ weights were also analysed conditional on body weight. Histological data were analysed by Fisher’s Exact Probability test - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY : Increased breathing and subdued behavior were evident in the majority of animals of both sexes receiving T-4388. There were no deaths found during 4 weeks of dosing period.
BODY WEIGHT AND WEIGHT GAIN : There were no notable intergroup differences in either sex during 4 weeks of oral administration of T-4388.
FOOD CONSUMPTION :There were no notable intergroup differences in either sex during 4 weeks of oral administration of T-4388.
FOOD EFFICIENCY : Not examined
HAEMATOLOGY :There were no notable intergroup differences in either sex .
CLINICAL CHEMISTRY : There were no notable intergroup differences in either sex .
ORGAN WEIGHTS : There was a slight increase in liver in high dose females.
GROSS PATHOLOGY : There were no notable intergroup differences in either sex .
HISTOPATHOLOGY: NON-NEOPLASTIC : There were no findings considered to be due to administration of the test material.
- Dose descriptor:
- NOEL
- Effect level:
- 250 mg/kg bw/day (nominal)
- Sex:
- male/female
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Sex:
- male/female
- Basis for effect level:
- other: Slight increase in liver weight of females not accompanied by histopathological changes.
- Critical effects observed:
- not specified
- Conclusions:
- Based on the results of this study a dose of 1000 mg/kg/day was identified as no observed adverse effect level. Based on a slight increase in liver weight which was not accompanied by histopathologic changes and observed in females only. The no observed effect level is 250 mg/kg/day.
dosing Sprague-Dawley rats with dose levels of 100, 250, 1000 mg/kg/day T-4388 produced increased breathing and subdued behavior in the majority of animals of both sexes receiving T-4388 and a slight increase in liver weight at 1000 mg/kg/day in females
Only. - Executive summary:
Four groups of Sprague- Dawley rats each containing 5 males and 5 females received T- 4388 (colorless liquid) via oral route by steel cannula at dose levels of 0,100, 250, 1000 mg/kg/day daily for 28 days. Rats were received from Charles River (UK) and housed 2 or 3 of one sex per cage in suspended polypropylene cages with stainless steel wire grid tops and bottoms. Animals were kept for acclimatization for 8 days and provided adlibitum feed and water. Temperature maintained in animal rooms was 18 °C - 22 °C with relative humidity of 45 - 65 % and 15-20 air changes.12 hour dark and 12 hour light photoperiod was maintained.
All animals were monitored for toxic effects which included clinical observations, body weights, organ weights, hematology, clinical chemistry, macroscopic and microscopic evaluations. Increased breathing and subdued behavior were evident in the majority of animals of both sexes receiving T-4388. There were no deaths found during 4 weeks of dosing period.
In body weights and feed consumption, there were no notable intergroup differences in either sex during 4 weeks of oral administration of T-4388. In hematology and clinical chemistry, there were no notable intergroup differences in either sex. In organ weights there was a slight increase in liver in high dose females.
There were no notable intergroup differences in either sex in gross pathology. There were no microscopic findings considered to be due to administration of the test material T-4388.
Based on the results of this study a dose of 1000 mg/kg/day was identified as no observed adverse effect level. Based on a slight increase in liver weight which was not accompanied by histopathologic changes and observed in females only. The no observed effect level is 250 mg/kg/day.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- good
Repeated dose toxicity: inhalation - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1983
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-study according to OECD guideline 413.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EPA OPPTS 870.3465 (90-Day Inhalation Toxicity)
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- other: Rat and Rabbit
- Strain:
- other: Fischer - 344 and New zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Rats :Charles River Breeding Laboratories (Portage, MI and Rabbits : Langshaw Rabbitry (Augusta, MI)
- Age at study initiation: 9 weeks for rats
- Weight at study initiation: Rats (140-195 gms) for male and female and for rabbits approx. 3 kg and above
- Housing: Rats (2/cage) and rabbits (1/cage) were housed in stainless steel cages with wire bottoms
- Diet (ad libitum): A standard laboratory diet (Purina Certified laboratory Chow, Ralson Purina Co., St. Louis. MO)
- Water (ad libitum): ad libitum except during exposure
- Acclimation period: 2 weeks for rats and 4 weeks for rabbits
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 -24°C
- Humidity (%): 40- 60 % (Relative humidity) - Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: unchanged (no vehicle)
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus:Stainless steel and glass inhalation chambers
- Method of conditioning air:DPGME was vaporized and metered into the chambers with a compressed air flames heat torch/j-tube assembly as described by Miller.The concentration of DPGME in each chamber was measured approximately once per hour with a Varian 2400 GC with 1/8" by 6 nickel column (8%Triton X-305 on 100/120 chromosorb) and flame ionization detector. Standard bags were made by adding DPGME to a "U-tube" 100 l of dry filtered air was metered through the tube into gas tight bag. Heat was applied to the test material to facilitate vaporirization.A series of standards which included15, 50,200 ppm were made and analyzed at least biweekly to produce standard curve.
- Temperature, humidity, in air chamber: Temperature- Mean maximum in the 4 chambers were 24-26°C
- Air flow rate: 800 l/min
TEST ATMOSPHERE :Measured mean chamber DPGME concentrations were within 1% of target concentrations (15, 50,200 ppm). Mean nominal DPGME concentrations (based on chamber air flow) were good in agreement (within 8%) with mean analytical concentrations, indicating that the test material losses were minimized in the vapor generator and exposure systems. Chamber distribution studies indicated that the test atmosphere concentrations were uniform within 10% inside each chamber. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- See the attachment-5
- Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- 6 hr/day, 5 days/week for 13 weeks
- Remarks:
- Doses / Concentrations:
0, 15, 50, or 200 ppm (0, 91, 303, or 1,212 mg/m3) for rats and rabbits
Basis:
nominal conc. - No. of animals per sex per dose:
- Rats : 10/sex/exposure
Rabbits : 7/sex/exposure - Control animals:
- other: Yes, room air.
- Details on study design:
- Post-exposure period: none
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Weekly once prior and after exposure.
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD EFFICIENCY: Not examined
-WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: After 12 weeks of exposure
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: Rats :40 male and 40 female Rabbit : 27 male and 28 female
- Parameters checked : PCV, Hgb, RBC, WBC (total and differential), Plat, RBC indices
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Blood samples from rats for clinical chemistries were taken at necropsy.
- Animals fasted: Yes
- How many animals: Rats 40 male and 40 female and Rabbits :27 male and 28 female
- Parameters checked : Alb, AP, BUN, TP, Globulin,glucose, SGPT
URINALYSIS: Yes ( For rats only)
- Time schedule for collection of urine: After 12 weeks of exposure
- Metabolism cages used for collection of urine: No data
- Animals fasted: No data
- Parameters checked : Bilirubin, Glucose,Ketone, Occult blood, pH,Protein, Specific gravity and Urobilinogen
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see table) : See attachment 1
HISTOPATHOLOGY: Yes (see table) : See attachment 1
All surviving animals underwent a gross necropsy on the day following last exposure. Rats (but not rabbits) were deprived of food overnight prior to necropsy. Rats were anesthetized with methoxyflurane, and then decapitated. Rabbits were anesthetized with CO2, and then decapitated. The trachea of all animals was clamped after anesthesia to prevent aspiration of blood during decapitation. Each animal was examined internally and externally for gross pathological changes. The heart, liver, kidneys, brain, thymus (rats), and testes (males) were removed from each animal and weighed. Eyes of all animals were examined grossly using a microscope slide technique with fluorescent illumination. Representative portions of the tissues and organs were preserved in buffered 10% formalin.
One male rabbit from the 200 ppm exposure group was sacrificed prior to scheduled termination of the study because of a head tilt and disequlibirium.This animal was examined in a manner similar to the other rabbits, except that organs were not weighed and serum was not collected. A full set of tissues was prepared and examined microscopically.
Liver samples from male rats and rabbits (3.exposure group) were fixed in a phosphate buffered 2% gluteraldehyde and 2% formaldehyde solution, then routinely processed and embedded in EPON 812 resin for possible electron microscopy. - Other examinations:
- Organ weights : The heart, liver, kidneys, brain, thymus (rats), and testes (males) were removed from each animal and weighed.
- Statistics:
- Clinical chemistry, hematology (PCV, Hgb, RBC, WBC and Plat only), urinary specific gravity, organ weight, body weight and organ to body weight ratio data were evaluated by Bartlett’s test for the equality of variances. If group variances were homogeneous; a parametric analysis of variance was conducted to determine if any statistically significant differences exist between groups. If overall parametric ANOVA was significant at <0.10 Dunnett’s test was used to identify statistically significant differences (<0.05) between experimental groups and their corresponding controls.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY: There were no apparent clinical effects and mortality due to DPGME exposure. Several minor observations were noted, including a case of ear mites in a male rabbit (treated topically with mineral oil), facial alopecia in 2 female rabbits, and a possible ruptured abscess in a female rabbit. One male rabbit which had been exposed to 200 ppm developed an ear infection and was sacrificed prior to the scheduled necropsy.
BODY WEIGHT AND WEIGHT GAIN: There were no exposure related adverse effects on body weights in either species during the 13 week study. There were no statistically significant differences from control body weight means in male and female rats or in male rabbits. The mean body weights of female rabbits in the 50 ppm group were slightly higher than the controls at the beginning of the study and at various intervals thereafter. This was not considered to be exposure related, due to absence of any effect on body weights of female rabbits in the high exposure group
HAEMATOLOGY: There were no exposure related effects on any measured hematology parameters in either sex of rat and rabbit. There were also no statistically significant differences from control means.
CLINICAL CHEMISTRY: There were no exposure related effects on any measured clinical chemistry parameters in either sex of rat and rabbit The only statistically significant difference was a slight decrease in BUN in female rats exposed to 50 ppm but this has no toxicologic significance.
URINALYSIS: There were no apparent effects on any of urinalysis parameters of male and female rats.
ORGAN WEIGHTS: There were no statistically significant differences in absolute or relative organ weights of rats exposed to DPGME, except for a slight decrease in mean relative liver weight of 50 ppm exposed males. There were several statistical differences in mean organ weights of rabbits but these also did not occur at the highest concentration tested, and were therefore not considered to be exposure related. There was an increase in mean relative kidney weight of female rabbits exposed to 200 ppm. The absolute mean kidney weights of 50 ppm and 200 ppm exposed female rabbits were also increased. However, both the absolute and relative mean kidney weights of DPGME exposed rabbits were within the range of historical control values. Because there was no evidence of nephrotoxicity, the increased kidney weights in the female rabbits were thought to be unrelated to the treatment.
GROSS PATHOLOGY: There were no exposure related changes observed at the necropsy in rats and rabbits. The changes observed during necropsy that were considered to be spontaneous changes of minimal severity which were not treatment related.
HISTOPATHOLOGY: NON-NEOPLASTIC: There were no DPGME exposure related microscopically changes observed in rats and rabbit. All histopathological observations were considered to be spontaneous changes of minimal severity which were not treatment related
- Dose descriptor:
- NOAEL
- Remarks:
- (Rat and Rabbit)
- Effect level:
- 200 ppm
- Sex:
- male/female
- Dose descriptor:
- NOAEC
- Effect level:
- 1 212.27 mg/m³ air (nominal)
- Sex:
- male/female
- Critical effects observed:
- not specified
- Conclusions:
- Based on the results of this study NOAEL in rat and rabbit was 200 ppm which is the highest attainable concentration due to the low vapor pressure of dipropylene glycol methyl ether.
- Executive summary:
Fischer – 344 (10/sex/exposure concentration ) and New Zealand white rabbits ( 7/sex/exposure concentration ) were exposed to 0, 15,50,200 ppm (0,91,303,1212 mg/m3) of dipropylene glycol monomethyl ether (colorless liquid DPGME) for 6 hrs/day, 5 days/week for 13 weeks.
Rats were received from Charles River Breeding Laboratories (, ) and Rabbits were received from Langshaw Rabbitry (, ).Rats and rabbits were kept for an acclimatization period of 2 weeks and 4 weeks respectively. Rats were housed (2/cage) and rabbits (1/cage) in stainless steel cages with wire bottoms. A standard laboratory diet (Purina Certified laboratory Chow, Ralson Purina Co., . MO) was supplied to rats and rabbits. Water also provided ad libitum to rats and rabbits except during exposure. Housing conditions were maintained at temperature of 20 -24 °C with relative humidity of 40-60 %.
Monitored for effects included general observations, body weights, clinical chemistry, hematology, urinalysis (Rats only), necropsy, organ weights and histopathology.
There were no exposure related adverse effects on body weights in either species during the 13 week study. There were no statistically significant differences from control body weight means in male and female rats or in male rabbits. The mean body weights of female rabbits in the 50 ppm group were slightly higher than the controls at the beginning of the study and at various intervals thereafter. This was not considered to be exposure related, due to absence of any effect on body weights of female rabbits in the high exposure group.
There were no apparent clinical effects and mortality due to DPGME exposure. There were no exposure related effects on any measured hematology parameters in either sex of rat and rabbit. There were also no statistically significant differences from control means. There were no apparent effects on any of urinalysis parameters of male and female rats.
Clinical chemistry, hematology (PCV, Hgb, RBC, WBC and Plat only), urinary specific gravity, organ weight, body weight and organ to body weight ratio data were evaluated by ’s test for the equality of variances.
All surviving animals underwent a gross necropsy on the day following last exposure. Rats (but not rabbits) were deprived of food overnight prior to necropsy. Rats were anesthetized with methoxyflurane, and then decapitated. Rabbits were anesthetized with CO2, and then decapitated. The trachea of all animals was clamped after anesthesia to prevent aspiration of blood during decapitation. Each animal was examined internally and externally for gross pathological changes. The heart, liver, kidneys, brain, thymus (rats), and testes (males) were removed from each animal and weighed. Eyes of all animals were examined grossly using a microscope slide technique with fluorescent illumination. Representative portions of the tissues and organs were preserved in buffered 10% formalin.
One male rabbit from the 200 ppm exposure group was sacrificed prior to scheduled termination of the study because of a head tilt and disequlibirium.This animals was examined in a manner similar to the other rabbits, except that organs were not weighed and serum was not collected. A full set of tissues was prepared and examined microscopically.
Liver samples from male rats and rabbits (3 exposure group) were fixed in a phosphate buffered 2%gluteraldehyde and 2% formaldehyde solution, then routinely processed and embedded in EPON 812 resin for possible electron microscopy.
There were no exposure related changes observed at the necropsy in rats and rabbits. There were no DPGME exposure related microscopically changes observed in rats and rabbits. All histopathological observations were considered to be spontaneous changes of minimal severity which were not treatment related.
Based on the results of this study NOAEL in rat and rabbit was 200 ppm. Under conditions of this study the low vapor pressure of DPGME, and results in this 13 week study DPGME appears to have a low subchronic vapor inhalation toxicity hazard.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEC
- 1 212.27 mg/m³
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- good
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: This study was conducted similar to OECD guideline 410.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 410 (Repeated Dose Dermal Toxicity: 21/28-Day Study)
- Principles of method if other than guideline:
- Method: other
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source:
- Age at study initiation:
- Weight at study initiation: 170-240 gms
- Fasting period before study:
- Housing:
- Diet (e.g. ad libitum):
- Water (e.g. ad libitum):
- Acclimation period:
ENVIRONMENTAL CONDITIONS
- Temperature (°C):
- Humidity (%):
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light):
IN-LIFE DATES: From: To: - Type of coverage:
- other: occlusive and open
- Vehicle:
- water
- Details on exposure:
- Route of Administration: dermal
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- Not specified in the publication
- Duration of treatment / exposure:
- 4 weeks
- Frequency of treatment:
- 4 hours/day; 5 days/week
- Remarks:
- Doses / Concentrations:
0, 100, 1000 mg/kg/d(occlusive and open)
Basis:
nominal per unit body weight - No. of animals per sex per dose:
- 8/sex/dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Post-exposure period: None
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
DETAILED CLINICAL OBSERVATIONS: No
DERMAL IRRITATION (if dermal study): No
BODY WEIGHT: Yes
FOOD CONSUMPTION: Yes
FOOD EFFICIENCY: No data
WATER CONSUMPTION: No data
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
CLINICAL CHEMISTRY: Yes
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
At the postmortem examination, fragments of bone marrow were removed from the left femur of each rat and placed in tubes containing one drop of 20 % bovine serum albumin in saline. The tubes were placed on a vortex mixer for a few seconds to disperse the marrow fragments. Marrow films were then prepared, air dried and fixed in solvent methanol before staining for 10 min each in May-Grunwald and Giemsa stains. The films were then differentiated for 10 min in dilute phosphate buffer and blotted dry. Additionally one femur from each animal was decalcified with a 10 % solution of formic acid in formalin for 1 week and processed and stained with hematoxylin and eosin.
HISTOPATHOLOGY: Yes
At 28 days, all the rats were killed by intraperitoneal injection of pentobarbitone sodium. The animals were examined post-mortem and testes weighed. Samples of liver, kidney, skin, stomach, small and large intestine and testes were taken for histological processing. Additionally lungs were processed where there was evidence gross abnormality. After fixation in neutral buffered formalin, 5µm sections were cut and stained with hematoxylin and eosin - Other examinations:
- Organ weights
- Statistics:
- The differences between body weight gain, food intake, clinical chemistry, hematology and bone marrow film data between test and control groups were analyzed using the unpaired student t-test to compare values in a test group with those in the corresponding control group at the same stage of the study. Thus combined weight of both testes was used in the analysis in which the weight of both testes animals from test animals was compared with that from the corresponding control animals, with the unpaired student t-test. Histological data were analyzed Fischer's test.
- Clinical signs:
- not specified
- Dermal irritation:
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not specified
- Details on results:
- CLINICAL SIGNS AND MORTALITY: All animals were survived during 28 day exposure period.
BODY WEIGHT AND WEIGHT GAIN: There were no significant differences in body weights between control and exposed animals
FOOD CONSUMPTION: There were no significant differences in food consumption between control and exposed animals
HAEMATOLOGY: There were no statistically significant differences from control values with respect to hematology.
CLINICAL CHEMISTRY: There were no statistically significant differences from control values with respect to clinical chemistry.
ORGAN WEIGHTS: There were no statistically significant differences organ weights of rats exposed to DPGME
GROSS PATHOLOGY: Macroscopic examination of the tissues revealed no significance findings attributable to DPGME exposure in rats
HISTOPATHOLOGY: NON-NEOPLASTIC: Macroscopic examination of the tissues revealed no significance findings attributable to DPGME exposure in rats - Dose descriptor:
- NOEL
- Effect level:
- > 1 000 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- other: overall effects
- Critical effects observed:
- not specified
- Conclusions:
- Based on results of the study NOEL for rats via dermal route was >1000 mg/kg/day.
- Executive summary:
Wistar rats (8 animals/sex/dose) were exposed to 0,100 and 1000 mg/kg/day (occluded and open) of DOWANOL DPM (colorless liquid) 5 days/week for 28 days.
Monitored for effects included clinical observations, body weights, food consumption, hematology, blood chemistry and, necropsy, organ weights, gross pathology and histopathology.
All animals were survived during 28 day exposure period.There were no significant differences in body weights, food consumption between control and exposed animals.There were no statistically significant differences from control values with respect to hematology and clinical chemistry DPGME exposed rats.
Macroscopic and microscopic examination of the tissues revealed no significance findings attributable to DPGME exposure in rats.
Based on results of the study NOEL for rats via dermal route was > 1000 mg/kg/day.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- good
Additional information
Based on toxicokinetics data summarized in IUCLID section 7.1.1, dipropylene glycol methyl ether acetate (DPMA) rapidly hydrolyzes to yield dipropylene glycol methyl ether in vivo. Thus, it is appropriate to conclude that the acetate behaves in a similar way to the parent ether due to the rapid conversion. Therefore, data on dipropylene glycol methyl ether are used to characterise the hazards of DPMA. Supporting data on PM and PMA are also provided.
Short-term repeated dose toxicity studies in rats (28-day), via oral gavage, are available for propylene glycol methyl ether (PM), propylene glycol methyl ether acetate (PMA), dipropylene glycol methyl ether (DPM) and DPMA. The NOAELs (oral) are > 919 mg/kg bw/day for all 4 substances. No adverse effects have been observed at the highest dose level tested. For the inhalation route, range-finding studies (up to 14-days) are available for PM and DPM. Repeated dose toxicity studies (28- and 90-day) via the dermal route are available for PM and DPM.
Sub-chronic (90-day) inhalation studies in rats and in rabbits are available for PM and DPM. The NOAEL for PM is 1000 ppm (3686 mg/m3), in rats and rabbits. The NOAEL for DPM is 200 ppm (1212 mg/m3, the highest attainable concentration), in rats and rabbits.
The only effects observed during the repeated dose toxicity study with DPMA were increased liver weights, subdued behaviour and increased breathing. The liver weight increase was very slight and only observed in females of the highest dose group. There were no histopathological changes accompanying this effect. There were no changes in clinical chemistry (ALP, ASP) indicating any liver damage.
The same liver effects were observed with other structurally related molecules, e.g. PM has been shown to cause liver weight increases via a phenobarbital-like enzyme induction mode of action and it is highly likely that DPMA liver weight increases occur via the same mode of action. As this is an adaptive effect typical for many glycol ethers, it is not considered as adverse. The toxicological significance of the observed increased breathing and subdue behaviour is unclear. As these observations were not accompanied by any significant effect, they are considered as not relevant.
PM, PMA and DPM have been subjected to repeated dose toxicity studies by at least one route of exposure. All studies indicate low repeated dose toxicity for these glycol ethers. The NOAELs obtained in the 90-day inhalation studies with PGME and DPGME were 1000 ppm (3686 mg/m3) and 200 ppm (1212 mg/m3, the highest attainable concentration), respectively. For DPMA, this would (theoretically) be equivalent to inhalation NOAELs of 7779 mg/m3 and 1556 mg/m3, respectively. Extrapolation to the oral route would result in NOAELs of 2256 and 451 mg/kg bw/day, respectively. Conducting repeated dose toxicity studies with DPMA via the oral route up to the limit dose of 1000 mg/kg bw/day will unlikely results in any adverse effects. Therefore, the data from DPM should be used to read-across, based on the rapid hydrolysis of acetate moiety from DPMA to yield DPM.
Further support for read across is attached at section 13 of the IUCLID.
For the purposes of risk assessment, the inhalation 90 -day study peformed using DPM with a NOEC of 200ppm will be taken as the starting point for DNEL derivation. Converting this to mg/m3 of DPMA, this is equivalent to 1556 mg/m3.
Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
A well conducted 28-day oral toxicity study (reliability 1, GLP)
Justification for selection of repeated dose toxicity inhalation - systemic effects endpoint:
A well conducted guideline 90-day inhalation study on a structural analogue.
Justification for selection of repeated dose toxicity dermal - systemic effects endpoint:
most recent, reliable study performed on a strucrutal analogue
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: liver
Justification for classification or non-classification
The no observed adverse effect levels for dipropylene glycol methyl ether acetate exceed the values triggering classification via all routes of exposure. Therefore no classification for prolonged exposure is required.
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