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EC number: 203-905-0 | CAS number: 111-76-2
- 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1993-1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Remarks:
- Fully documented study to a recognised protocol and performed by an organisation known to operate to high standards and that uses a peer review process for its work.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- carcinogenicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Fully documented NTP guideline study. NTP studies are subject to critical peer review process.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 451 (Carcinogenicity Studies)
- Deviations:
- no
- Remarks:
- , no significant deviations noted.
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Taconic Laboratory Animals and Services, Germantown, NY
- Age at study initiation: 7-8 weeks
- Housing: individual stainless steel, wire bottomed cages.
- Diet: NIH-07 open formulate, pelleted, ad libitum except during exposure period
- Water: tap, ad libitum, automated watering system
- Acclimation period: 18 days in quarantine.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24C approx
- Humidity (%): 57-58
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 23 Aug 1993 To: 18 Aug 1995 - Route of administration:
- inhalation: vapour
- Type of inhalation exposure (if applicable):
- whole body
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Stainless steel 1.7m3
- Method of conditioning air: charcoal filtration
- Temperature, humidity, pressure in air chamber: 24C approx, 55% approx.
- Air change rate: 15/hr
- Vapour generation: 2-butoxyethanol under nitrogen micrometer pumped onto a heated glass column filled with glass beads. Output of generator quantified by nitrogen flow and 2-butoxyethanol vapour pressure at exit temperature. Transfer lines heated to prevent condensation. Particle detector used to ensure vapour only entered chamber (particle counts never greater than LOD of 200/cm3).
TEST ATMOSPHERE
- Brief description of analytical method used: On line gas chromatography, sampling every 15 mins. Calibration with off-line gas chromatography, which were themselves calibrated with gravimetrically prepared samples of 2-butoxyethanol.
- Samples taken from breathing zone: no - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- On line gas chromatography, sampling every 15 mins. Calibration with off-line gas chromatography, which were themselves calibrated with gravimetrically prepared samples of 2-butoxyethanol.
- Duration of treatment / exposure:
- 2 years
- Frequency of treatment:
- 6 hours/day plus chamber equilibration time (12 mins), 5 days per week
- Post exposure period:
- none
- Remarks:
- Doses / Concentrations:
0, 31, 62.5, 125ppm
Basis:
nominal conc. - Remarks:
- Doses / Concentrations:
0, 29.0-32.6, 57.6-67.0, 117-133ppm
Basis:
analytical conc. - No. of animals per sex per dose:
- 50
- Control animals:
- yes, sham-exposed
- Details on study design:
- - Dose selection rationale: Based on 90 day range finder study described in chapter 7.5.3. Animal distribution among groups designed to equalise initial mean body weight.
- Rationale for selecting satellite groups: Satellite groups for haematology and bone marrow analysis (27 animals per sex in control, mid and high dose groups, 9 animals per sex for low dose group.) One group each for time point sacrifices of 3, 6 and 12 months. - Positive control:
- No
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: monthly (fortnightly during last 6 months) and at end of study
BODY WEIGHT: Yes
- Time schedule for examinations: start, monthly (fortnightly during last 6 months) and at end of study
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at end of study prior to sacrifice and from satellite groups at 3, 6 and 12 months (not 31.2ppm) - collected from retroorbital sinus
- Anaesthetic used for blood collection: Yes (identity) CO2/O2
- Animals fasted: No data
- How many animals: all survivors
- Parameters checked: erythrocyte, leucocyte, platelet counts; MCV, MCHg, MCHg concentration; hematocrit, reticulocyte, haemoglobin, leucocyte differential count and nucleated erythrocyte count. Morphological analysis of erythrocytes, leucocytes and platelets. Measurements made using an Ortho ELT-8/ds 9000 analyser. Bone marrow cellularity measurements using a Coulter model Zh counter while cytological evaluations of bone marrow cell morphology and myeloid/erythroid ratios were made microscopically.
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
ORGAN WEIGHTS: not measured. - Sacrifice and pathology:
- Complete histopathology on all core animals (not satellites). Apart from gross lesions, the following were examined for gross lesions and tissues fixed and processed for examination. : adrenal gland, bone with marrow, brain, clitoral gland, esophagus, heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, larynx, liver, lung, lymph nodes, (mandibular, mesenteric, brochial, mediastinal), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, spleen, stomach (fore and glandular), testes (with epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, uterus.
- Other examinations:
- Haematology at 3 and 6 months using satellite groups.
- Statistics:
- Probability of survival estimated by product limit procedure of Kaplan and Meier (1958). Dose related effects tested with Cox's method (1972) for group equality and Tarone's 1975 life table test to identify dose related trends. Reported p values 2 sided. The ply-k test was used to assess for lesion prevalence (modified version of Cochran-Armitage test). Organ and body weight assess using Dunett's parametric multicomparison procedure. Haematology data analysed using method of Shirley and Dunn for nonparametric data along with Jonckheere's method to test for trend. Dixon and Masssey (1951) method used to eliminate outlier values.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- effects observed, treatment-related
- Details on results:
- BODY WEIGHT AND WEIGHT GAIN: Body weights of male and female rats in the 31.2 and 62.5 ppm groups and male rats of the 125 ppm group were generally similar to the controls throughout the experiment. Body weights of female rats of the 125 ppm group were generally lower than those of the chamber control from week 17 until the end of the experiment.
All non-neoplastic findings are reported in the entry for this study in chapter 7.5.3. Neoplastic findings are reported in the 'remarks on results' field. - Relevance of carcinogenic effects / potential:
- No clear evidence of carcinogenic effect
- Dose descriptor:
- NOAEC
- Sex:
- male/female
- Basis for effect level:
- other: The NOAEC for other effects is reported in chapter 7.5.3
- Remarks on result:
- not determinable
- Remarks:
- no NOAEC identified. Effect type:carcinogenicity (migrated information)
- Conclusions:
- There was no clear evidence of a carcinogenic effect. The marginal effects that were statistically significantly different to historic but not concurrent controls could not be atttributed with confidence to exposure.
- Executive summary:
In a 2 year NTP cancer bioassay in rats exposed to 2 -butoxyethanol by the whole body inhalation route to concentrations up to 125ppm, there was no evidence for carcinogenicity in males. The incidence of benign or malignant phaeochromocytoma (combined) of the adrenal medulla in females exposed to the top dose of 125 ppm was not significantly increased compared to the chamber controls, but it did exceed the historical control range. Within this dose group, there was only a single incidence of malignant phaeochromocytoma. The study report recorded that this finding provided equivocal evidence of carcinogenicity in females, this is a very conservative interpretation and the findings cannot be attributed with confidence to exposure
Synopsis
NOAEL (2yr cancer study, rats)>125ppm
The incidence of benign or malignant phaeochromocytoma (combined) of the adrenal medulla in females exposed to 125 ppm EGBE was not significantly increased compared to the chamber controls, but it did exceed the historical control range. There was only one malignant phaeochromocytoma, which occurred in the 125 ppm group. The data are summarised in the table below:
Neoplastic and non-neoplastic lesions of the adrenal medulla in female F344/N rats
Chamber control |
31.2 ppm |
62.5 ppm |
125 ppm |
|
No. examined |
50 |
50 |
49 |
49 |
Hyperplasia (severity) |
11 (1.9) |
11 (2.3) |
8 (2.1) |
17 (2.5) |
Benign phaeochromocytoma |
3/50 (6 %) |
4/50 (8 %) |
1/49 (2 %) |
7/49 (14 %) |
Benign or malignant phaeochromocytoma |
3/50 (6 %) |
4/50 (8 %) |
1/49 (2 %) |
8/49 (16 %) |
Two nasal tumours were discovered: a chondroma in a 31.2 ppm male and an adenoma in a 62.5 ppm male. In the absence of any preneoplastic changes, these are considered incidental findings. Although the incidence of hyaline degeneration was significantly increased in all exposed groups of male rats, the severity of the lesion was minimal and was not affected by exposure.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 453 (Combined Chronic Toxicity / Carcinogenicity Studies)
- Deviations:
- no
- Remarks:
- , no significant deviations noted
- Principles of method if other than guideline:
- NTP carcinogenicity study
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 2-butoxyethanol
- EC Number:
- 203-905-0
- EC Name:
- 2-butoxyethanol
- Cas Number:
- 111-76-2
- Molecular formula:
- C6H14O2
- IUPAC Name:
- 2-butoxyethanol
- Details on test material:
- - Name of test material (as cited in study report): 2-butoxyethanol
- Physical state: liquid
- Analytical purity: >99%
- Impurities (identity and concentrations): Water 0.0254%, 0.003% acetic acid, <1000ppm peroxide.
- Lot/batch No.: QP-921215-26D2
- Source: Dow Chemical, Plaquemine, LA
- Stability under test conditions: No degradation detected (monitored for acid, peroxide and by GC)
- Storage condition of test material: Room temperature in the dark.
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Taconic Laboratory Animals and Services, Germantown, NY
- Age at study initiation: 7-8 weeks
- Housing: individual stainless steel, wire bottomed cages.
- Diet: NIH-07 open formulate, pelleted, ad libitum except during exposure period
- Water: tap, ad libitum, automated watering system
- Acclimation period: 18 days in quarantine.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24C approx
- Humidity (%): 57-58
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 23 Aug 1993 To: 18 Aug 1995
Administration / exposure
- 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 1.7m3
- Method of conditioning air: charcoal filtration
- Temperature, humidity, pressure in air chamber: 24C approx, 55% approx.
- Air change rate: 15/hr
- Vapour generation: 2-butoxyethanol under nitrogen micrometer pumped onto a heated glass column filled with glass beads. Output of generator quantified by nitrogen flow and 2-butoxyethanol vapour pressure at exit temperature. Transfer lines heated to prevent condensation. Particle detector used to ensure vapour only entered chamber (particle counts never greater than LOD of 200/cm3).
TEST ATMOSPHERE
- Brief description of analytical method used: On line gas chromatography, sampling every 15 mins. Calibration with off-line gas chromatography, which were themselves calibrated with gravimetrically prepared samples of 2-butoxyethanol.
- Samples taken from breathing zone: no - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- On line gas chromatography, sampling every 15 mins. Calibration with off-line gas chromatography, which were themselves calibrated with gravimetrically prepared samples of 2-butoxyethanol.
- Duration of treatment / exposure:
- 2 years
- Frequency of treatment:
- 6 hours/day plus chamber equilibration time (12 mins), 5 days per week
Doses / concentrationsopen allclose all
- Dose / conc.:
- 31 ppm (nominal)
- Remarks:
- Actual dose 29.0 to 32.6ppm over course of study
- Dose / conc.:
- 62.5 ppm (nominal)
- Remarks:
- Actual dose 57.6 to 67.0ppm over course of study
- Dose / conc.:
- 125 ppm (nominal)
- Remarks:
- Actual dose 117 to 133ppm over course of study
- No. of animals per sex per dose:
- 50
- Control animals:
- yes, sham-exposed
- Details on study design:
- - Dose selection rationale: Based on range finder study described in this chapter. Animal distribution among groups designed to equalise initial mean body weight.
- Rationale for selecting satellite groups: Satellite groups for haematology and bone marrow analysis (27 animals per sex in control, mid and high dose groups, 9 animals per sex for low dose group.) One group each for time point sacrifices of 3, 6 and 12 months. - Positive control:
- No
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: monthly (fortnightly during last 6 months) and at end of study
BODY WEIGHT: Yes
- Time schedule for examinations: start, monthly (fortnightly during last 6 months) and at end of study
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No
WATER CONSUMPTION: No
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at end of study prior to sacrifice and from satellite groups at 3, 6 and 12 months (not 31.2ppm) - collected from retroorbital sinus
- Anaesthetic used for blood collection: Yes (identity) CO2/O2
- Animals fasted: No data
- How many animals: all survivors
- Parameters checked: erythrocyte, leucocyte, platelet counts; MCV, MCHg, MCHg concentration; hematocrit, reticulocyte, haemoglobin, leucocyte differential count and nucleated erythrocyte count. Morphological analysis of erythrocytes, leucocytes and platelets.
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- HISTOPATHOLOGY: Yes. Complete histopathology on all core animals (not satellites). Apart from gross lesions, the following were examined: adrenal gland, bone with marrow, brain, clitoral gland, esophagus, heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, larynx, liver, lung, lymph nodes, (mandibular, mesenteric, brochial, mediastinal), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, spleen, stomach (fore and glandular), testes (with epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, uterus.
- Other examinations:
- none
- Statistics:
- Probability of survival estimated by product limit procedure of Kaplan and Meier (1958). Dose related effects tested with Cox's method (1972) for group equality and Tarone's 1975 life table test to identify dose related trends. Reported p values 2 sided. The ply-k test was used to assess for lesion prevalence (modified version of Cochran-Armitage test). Organ and body weight assess using Dunett's parametric multicomparison procedure. Haematology data analysed using method of Shirley and Dunn for nonparametric data along with Jonckheere's method to test for trend. Dixon and Masssey (1951) method used to eliminate outlier values.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No clinical signs were attributed to 2-butoxyethanol exposure.
- Mortality:
- no mortality observed
- Description (incidence):
- Survival of exposed male and female rats was similar to the chamber control groups, the mean numbers of survivors at the end of the experiment in each of the 0, 31.2, 62.5 and 125 ppm groups were 19, 11, 21 and 24 males and 29, 27, 23 and 21 females, respectively.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Body weights of male and female rats in the 31.2 and 62.5 ppm groups and male rats of the 125 ppm group were generally similar to the controls throughout the experiment.
- Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Haematological examination showed that inhalation of 2-butoxyethanol resulted in the development of a persistent and exposure-related macrocytic, normochromic, responsive anaemia, as indicated by decreased haematocrit values, haemoglobin concentrations and erythrocyte counts. These changes occurred at 3, 6 and 12 months in 62.5 ppm group females and 125 ppm group males. Some anaemia also occurred at 3 and 6 months in the 31.2 ppm group females and at 12 months in the 62.5 ppm group males. In females this was characterised by t adose related and significant fall in hematocrit, haemoglobin and erythrocyte count and an increase in MCV. The changes at 31ppm were however small (<5%). Increases in circulating reticulocyte and nucleated erythrocyte counts are consistent with an erythropoietic response to the anaemia. In bone marrow there were approximately 15 % - 35 % decreases in the myeloid/erythroid ratio in the 125 ppm rats of both sexes, but particularly in females. Increases in bone marrow cellularity occured at all time points in females at 125ppm along with a 15-35% decrease in myeloid/erythroid ratio. Significant changes were also seen in males at 125ppm and females at 62.5ppm but only at one time point. The severity of the response was dose related.
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- In the nose there were significant increases in the incidences of hyaline degeneration of the olfactory epithelium in all groups of males (chamber control, 13/48; 31.2 ppm, 21/49; 62.5 ppm, 23/49; 125 ppm, 40/50) and in females exposed to the two higher concentrations of EGBE (chamber control, 13/50; 31.2 ppm, 18/48; 62.5 ppm, 28/50; 125 ppm, 40/49). The severity of the lesion was minimal and did not change with increasing exposure concentration. It is the most common age-related change of the nasal passages of rats (St. Clair & Morgan, 1992) and it has been proposed to have an adaptive or protective role (Buckley et al., 1985).
Incidences of Kupffer cell pigmentation of the liver increased significantly in all exposed groups of male rats (chamber control, 23/50; 31.2 ppm, 30/50; 62.5 ppm, 34/50; 125 ppm, 42/50) and in the two higher exposure groups of female rats (chamber control, 15/50; 31.2 ppm, 19/50; 62.5 ppm, 36/50; 125 ppm, 47/50). The severity of the lesion increased in the 125 ppm group of both sexes.
In the spleen, incidences of fibrosis were significantly increased in the two higher exposure groups of male rats (chamber control, 11/50; 31.2 ppm, 14/50; 62.5 ppm, 19/50; 125 ppm, 20/50), but not in females. - Histopathological findings: neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- See results in chapter 7.7 of IUCLID dossier
Effect levels
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- < 31 ppm
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- haematology
- histopathology: non-neoplastic
- Remarks on result:
- other: adverse effects seen at lowest tested dose
- Dose descriptor:
- NOAEC
- Effect level:
- < 31 ppm
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: Kupffer cell pigmentation.
Target system / organ toxicity
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 31 ppm
- System:
- hepatobiliary
- Organ:
- liver
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- no
Any other information on results incl. tables
Neoplastic effects are reported in chapter 7.7.
Applicant's summary and conclusion
- Conclusions:
- No NOAEC was found. The LOAEL of 31 ppm based on haematological effects seen at all doses tested. in females and Kupffer cell pigmentation in both sexes. Females appear to be more senstive to the haematological effects of 2-butoxyethanol than males.
- Executive summary:
In a two year carcinogenicity study, rats were exposed by inhalation to butoxyethanol at doses up to 125ppm for a period of 104 weeks. The study approximated to guideline but parameters known to be insensitive to this substance were not examined. The predominant non-neoplastic effects of note were adverse changes to the haematology, particularly haematocrit, hemoglobin, erythrocytes reductions. Females were particularly sensitive showing dose related and statistically significant reductions in these parameters at 31ppm, although it should be noted that the reduction in these parameters was only around 5%. These effects were only consistently seen at all interim sacrifice points at 125ppm in males. However no NOAEL could be established due to the presence in both sexes of increased Kupffer cell pigmentation at 31ppm.
Synopsis:
NOAEL (rats, 104 weeks, inhalation): <31ppm
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