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EC number: 216-940-1 | CAS number: 1704-62-7
- 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
Oral (OECD Guideline 401), Dermal (OECD Guideline 402) and Inhalation (OECD Guideline 403) tests were conducted on DMEE. Toxicity in the oral gavage study was dose dependent for males and females with an LC50 of 2150 - 3830 mg/kg bw. Toxicity in the dermal study was also dose dependent and the observed LD50 was 1.74 mL/kg bw for males and 2.14 mL/kg bw for females. The potential LC50 for male and female rats exposed to the test substance for 4 hours via the inhalation route is > 72 ppm, which was the maximum concentration tested.
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:
- Experimental: 10 Apr 1987 - 25 June 1987
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to OECD guideline study. Acceptable, well documented report which meets basic scientific principles.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Version / remarks:
- (adopted 1981)
- Deviations:
- yes
- Remarks:
- A test group consisting of 5 animals was treated by single gavage application with an aqueous solution of the test substance.
- GLP compliance:
- no
- 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: Dr. K. Thomae GmbH, Germany
- Weight at study initiation: male: 187 g (mean); female: 177 g (mean)
- Fasting period before study: 16 h before administration but water was available ad libitum
- Housing: 5 animals per cage
- Diet: KLIBA-Labordiaet 343, Klingentalmuehle AG, CH, ad libitum
- Water: tap water ad libitum
- Acclimation period: at least 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24 °C
- Humidity (%): 30 - 70 %
- Photoperiod (hrs dark / hrs light): 12/12
- Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 0.5 % aqueous CMC
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 50, 38.3, 21.5, and 10.0 % (w/v), respectively, for 5000, 3830, 2150, and 1000 mg/kg bw doses
- Amount of vehicle (if gavage): 10 mL/kg bw
MAXIMUM DOSE VOLUME APPLIED: 10 mL/kg bw - Doses:
- 1000, 2150, 3830 and 5000 mg/kg bw
- No. of animals per sex per dose:
- 5 animals/sex/dose
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations: recording of signs and symptoms several times on the day of administration, at least once each workday. Check for moribund and dead animals twice each workday and once on holidays.
- Frequency of weighing: days 0, 5, 7, 13
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight - Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- >= 2 150 - <= 3 830 mg/kg bw
- Based on:
- test mat.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- >= 2 150 - <= 3 830 mg/kg bw
- Based on:
- test mat.
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- ca. 2 150 mg/kg bw
- Based on:
- test mat.
- Mortality:
- See details in "remarks on results".
- Clinical signs:
- other: See details in "remarks on results".
- Gross pathology:
- - Animals that died:
General congestion.
Stomach/small intestines: mucosa reddened, bloody contents.
- Sacrificed animals:
No pathologic findings noted.
Reference
Mortality:
Dose (mg/kg bw) | Conc. | Gender | 1 h | 24 h | 48 h | day 7 | day 14 | |
5000 | 50 | male | 0/5 | 5/5 | 5/5 | 5/5 | 5/5 | |
5000 | 50 | female | 0/5 | 5/5 | 5/5 | 5/5 | 5/5 | |
3830 | 38.3 | male | 0/5 | 5/5 | 5/5 | 5/5 | 5/5 | |
3830 | 38.3 | female | 0/5 | 5/5 | 5/5 | 5/5 | 5/5 | |
2150 | 21.5 | male | 0/5 | 0/5 | 0/5 | 0/5 | 0/5 | |
2150 | 21.5 | female | 0/5 | 2/5 | 2/5 | 2/5 | 2/5 | |
1000 | 10 |
male | 0/5 | 0/5 | 0/5 | 0/5 | 0/5 | |
1000 | 10 |
female | 0/5 | 0/5 | 0/5 | 0/5 | 0/5 |
Weight (g):
Dose (mg/kg bw) |
Gender | day 0 | day 5 | day 7 | day 13 | |||
5000 | male | 92 | - |
- | - | |||
5000 | female | 179 | - | - | - | |||
3830 | male | 186 | - | - | - | |||
3830 | female | 172 | - | - | - | |||
2150 | male | 179 | - | 238 | 272 | |||
2150 | female | 179 | - | 197 | 215 | |||
1000 | male | 189 | 244 | - | 291 | |||
1000 | female | 180 | 205 | - | 217 |
Clinical signs:
Dose (mg/kg bw) | 5000 | 3830 | 2150 | 1000 | ||||
male | female | male | female | male | female | male | female | |
Dyspnea |
1 h - 4 h |
1 h - 4 h |
30 m - 5 h |
30 m - 5 h |
1 d - 2 d |
4 h - 2 d |
- |
- |
Apathy |
1 h - 4 h |
1 h - 4 h |
30 m - 5 h |
30 m - 5 h |
1 d - 2 d |
4 h - 2 d |
- |
- |
Abnormal position |
4 h |
4 h |
- |
4 h - 5 h |
- |
- |
- |
- |
Staggering |
4 h |
4 h |
30 m - 5 h |
30 m - 1 h |
- |
1 d - 2 d |
- |
- |
Atonia |
4 h |
4 h |
- |
4 h - 5 h |
- |
- |
- |
- |
Paresis |
4 h |
4 h |
- |
4 h - 5 h |
- |
- |
- |
- |
Piloerection |
1 h - 4 h |
1 h - 4 h |
30 m - 5 h |
30 m - 5 h |
1 d - 2 d |
4 h - 2 d |
- |
- |
Cyanosis | 4 h | 4 h | 4 h - 5 h | 4 h - 5 h | - | - | - | - |
Exsiccosis | 4 h | 4 h | - | 4 h- 5 h | - | - | - | - |
Salivation | 4 h | 4 h | - | - | - | - | - | - |
Poor general state | 1 h - 4 h | 1 h - 4 h |
30 m - 5 h | 30 m - 5 h | 1 d - 2 d | 4 h - 2 d | - | - |
min: minutes
h: hour
d: day
The test substance caused systemic toxicity (including mortality) in a dose dependent manner.
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 150 mg/kg bw
- Quality of whole database:
- One reliable acute oral toxicity study is available for DMEE (CAS# 1704-62-7).
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:
- 1987-04-13 to 1989-08-10
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study following internal Laboratory standards and protocols that are equivalent to OECD Guideline 403.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Principles of method if other than guideline:
- The study followed a specific protocol (87-15-04-AI-A) and standard protocol amendment.
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Sprague-Dawley, Inc., Indianapolis, IN)
- Age at study initiation: 45 d (Static), 46 d (Dynamic bubbler), 51 d (Dynamic evaporator)
- Weight at study initiation: 174 g (Static mean weight- Male), 150 g (Static mean weight- Female), 186 g (Dynamic bubbler mean weight- Male), 152 g (Dynamic bubbler mean weight- Female), 210 g (Dynamic evaporator Mean weight- Male), 165 g (Dynamic evaporator Mean weight- Female)
- Fasting period before study: None
- Housing: Housed five per sex in 23.5 X 40 X 18 cm stainless steel wire-mesh cages on carriers
- Diet (e.g. ad libitum): Pelletted feed (Pro Lab RMH#3000, Agway, Inc.); ad libitum except during exposure
- Water (e.g. ad libitum): Tap water (Municipal Authority of Westmoreland County, Greenburg, PA); ad libitum except during exposure
- Acclimation period: yes, 2 days for static, 3 days for dyanmic bubbler, and 8 days for dynamic evaporator; the Study Director opinion was that the lower than 5-day acclimation period for the first two tests did not alter the interpretation of results.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 deg C
- Humidity (%): N/A
- Air changes (per hr): N/A
- Photoperiod (hrs dark / hrs light): 12-hr photoperiod throughout the entire study
IN-LIFE DATES: From: April 10 To: April 27 (Static), April 28 (Dynamic bubbler), May 3 (Dynamic evaporator). - Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Static and dynamic bubbler exposures were in plexiglass and stainless steel chambers and the dynamic evaporator exposures were in glass and stainless steel chamber
- Exposure chamber volume: approximately 120 liters (static and dynamic bubbler exposures); 900 liters (dynamic evaporator exposures)
- Method of holding animals in test chamber: 5 per sex free to move in 26x18.5x18 cm wire-mesh cages for the static and dynamic bubbler exposure chambers; individually housed in 21x12.5x18 cm wire-mesh cages, free to move in the dynamic evaporator exposure chambers.
- Source and rate of air:
(A) For the static exposure, the test substance (120 grams untreated) was placed in an open tray at the top of the sealed 120-liter chamber and the vapor was allowed to achieve equilibration (17 hours). The animals were then placed into the chamber for a 4 hour exposure period.
(B) For the dynamic bubbler exposure, compressed air was passed through a 250 mL gas washing bottle containing approximately 59 grams of test substance. The air containing the test substance vapor entered directly into the exposure chamber at a rate of 30 L/min.
(C) For the dynamic evaporator exposure, the test substance was metered with a piston pump (Fluid Metering Inc., Oyster Bay, NY) into a heated evaporator. The resulting vapor mixture was carried to the chamber by a countercurrent air stream that entered the bottom of the evaporator at a rate of 200 L/min.
- Method of conditioning air: N/A
- System of generating particulates/aerosols: N/A
- Method of particle size determination: N/A
- Treatment of exhaust air: N/A
- Temperature, humidity, pressure in air chamber:
Static: 25 +/- 1 deg C, 77 +/- 23% % relative humidity
Dynamic bubble: 24 +/- 0 deg C, 37 +/- 2% relative humidity
Dynamic evaporator: 24 +/- 0 deg C, 43 +/- 2% relative humidity
TEST ATMOSPHERE
- Brief description of analytical method used: The concentration of test substance in the exposure chamber atmosphere was determined for the dynamic and static exposures by sampling with XAD-2 sorbent tubes. The samples were desorbed and then analyzed by flame ionization gas chromatograpy.
- Samples taken from breathing zone: no
VEHICLE
- Composition of vehicle (if applicable): N/A
- Concentration of test material in vehicle (if applicable): N/A
- Justification of choice of vehicle: N/A
- Lot/batch no. (if required): N/A
- Purity: N/A
TEST ATMOSPHERE (if not tabulated)
- Particle size distribution: N/A
CLASS METHOD (if applicable)
Rationale for the selection of the starting concentration: The target concentration for both the static and dynamic exposures was the highest attainable vapor concentrations of the test substance without visual observation of an aerosol (saturated vapor). - Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- The concentration of test substance in the exposure chamber atmosphere was determined for the dynamic and static exposures by sampling with XAD-2 sorbent tubes. The samples were desorbed and then analyzed by flame ionization gas chromatograpy.
- Duration of exposure:
- 4 h
- Concentrations:
- Static: Mean 15 ppm, standard deviation +/- 8.11 ppm
Dynamic bubbler: Mean 72 ppm, standard deviation +/- 11.6 ppm
Dynamic evaporator: Mean 63 ppm, standard deviation +/- 3.4 ppm - No. of animals per sex per dose:
- 5 per sex per type of exposure (static, dynamic bubbler, or dynamic evaporator)
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Animals were observed for signs of toxic effects on the day of exposure and daily following exposure for 14 days. The animals were weighed prior to exposure and on postexposure Days 7 and 14. The change in body weight was calculated by subtracting the pre-exposure value from each successive weight.
- Necropsy of survivors performed: Yes, a complete necropsy was performed for all animals. The survivors were anesthetized with methoxyflurane and killed by exsanguination via the branchial blood vessels. The lungs and liver for the female rat which died (static exposure) were extracted and fixed in 10% neutral buffered formalin.
- Other examinations performed: clinical signs, body weight, organ weights, histopathology, other: N/A - Statistics:
- The mean and standard deviation of the body weights and body weight changes of the animals and the exposure concentrations, temperature, relative humidity and oxygen were calculated. No statistical comparisons were made.
- Preliminary study:
- N/A
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 72 ppm
- Based on:
- test mat.
- Remarks:
- generated by dynamic bubbler
- Exp. duration:
- 4 h
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 68 ppm
- Based on:
- test mat.
- Remarks:
- generated by dynamic evaporator
- Mortality:
- One delayed mortality was observed for female rats on postexposure Day 1. No other mortalities occurred during the study.
- Clinical signs:
- other: Static and dynamic bubbler: No clinical signs of toxicity were observed on the day of exposure or during the 14-day postexposure observation period. Dynamic evaporator: Blepharospasm and periocular wetness were the only clinical signs of toxicity observed
- Body weight:
- Mean body weight gain was observed for both sexes on postexposure Days 7 and 14.
- Gross pathology:
- Macroscopic lesions were not observed in animals sacrificed at the end of the 2-week postexposure period. The only macroscopic lesions observed was a dark red (mottled) discoloration of the lungs and liver, noted only in the rat which died.
- Other findings:
- N/A
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: not specified
- Conclusions:
- LC50 for male and female rats during the 4 hour exposure was > 72 ppm.
Reference
The potential LC50 for male and female rats exposed to the test substance for 4 hours is > 72 ppm, which was the highest exposure concentration, obtained in the dynamic bubbler chamber.
For the static exposure, a decrease in concentration was observed with exposure time as the relative humidity rose during the exposure period. The decrease in concentration may be attributed to interaction of the test material with water (relative humidity), as the test substance is highly soluble in water. Similar interaction with water may have occurred during the dynamic exposures, as indicated by the low actual/nominal ratios of 0.42 and 0.66 for the test substance for the dynamic bubbler and dynamic evaporator exposures, respectively.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 392.2 mg/m³ air
- Quality of whole database:
- One reliable acute oral toxicity study is available for DMEE (CAS# 1704-62-7).
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:
- Unspecified to 1986-08-25
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study report without statement of guideline used for study or certification of following GLP; however, the methodology provided was equivalent to OECD 402.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Deviations:
- yes
- Remarks:
- Clinical observations were made before dose (0 days) and at 7 and 14 days instead of daily.
- Principles of method if other than guideline:
- N/A
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation: between 2.0 and 3.0 kg - Type of coverage:
- occlusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- TEST SITE
- Area of exposure: Trunk
- % coverage: N/A
- Type of wrap if used: Vetrap Bandaging Tape wrapped over the impervious sheeting of the intact, clipped skin
REMOVAL OF TEST SUBSTANCE
- Washing (if done): Excess fluid removed to diminish ingestion
- Time after start of exposure: 24 hrs - Duration of exposure:
- 24 hrs
- Doses:
- Males: 0.50, 1.00, 1.41, and 2.00 mL/kg (the last dose was inferred by reviewer from lower doses and LD50; first number is erased in study's table).
Females: 0.50, 1.00, 2.00 (this dose inferred by reviewer from other doses and LD50; first number is erased in study's table), and 4.00 mL/kg. - No. of animals per sex per dose:
- 5 males and 5 females were included on each level for the LD50 calculation.
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: weighing at 0 days (before dose), 7 days and 14 days (just prior to sacrifice).
- Necropsy of survivors performed: yes - Statistics:
- Moving average method (Thompson, 1947 (reference in OECD 402); Weil, 1983).
- Preliminary study:
- N/A
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 1.74 mL/kg bw
- Based on:
- test mat.
- 95% CL:
- 1.5 - 2.01
- Remarks on result:
- other: Using the density for DMEE of 0.95 g/mL to convert to mg/kg bw resulted in a LD50 value of 1663 mg/kg bw.
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 2.14 mL/kg bw
- Based on:
- test mat.
- 95% CL:
- 1.45 - 3.17
- Remarks on result:
- other: Using the density for DMEE of 0.95 g/mL to convert to mg/kg bw resulted in a LD50 value of 2033 mg/kg bw.
- Mortality:
- Time of death ranged from 1 to 4 days.
- Males: 4/5 of the 2.00 mL/kg group died, 0/5 of the 1.41 mL/kg group, 0/5 of the 1.00 mL/kg group, 0/5 of the 0.50 group.
- Females: 5/5 of the 4.00 mL/kg group, 2/5 of the 2.00 mL/kg group. - Clinical signs:
- other: Local dermal effects included: erythema, edema, necrosis, ecchymosis, fissuring, ulceration, desquamation and scabs. Dermal reactions persisted through 14 days. Salvation, sluggishness, unsteady gait, red discharge (from nose and mouth), tremors (in 2) an
- Gross pathology:
- Gross pathology findings included red and mottled lungs, red tracheas, a few discolored livers and kidneys, and subcutaneous edema.
- Other findings:
- N/A
- Conclusions:
- The LD50 for percutaneous exposure to male rabbits was 1.74 mL/kg (1663 mg/kg bw) and to female rabbits was 2.14 mL/kg (2033 mg/kg bw). Severe skin irritation was apparent on each rabbit through death or sacrifice at 14 days.
Reference
The author of the study concluded that DMEE was moderately toxic following its administration by single dermal application. The criteria used for interpretation of results is listed above under "Any other information on materials and methods incl. tables".
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 1 663 mg/kg bw
- Quality of whole database:
- One reliable acute oral toxicity study is available for DMEE (CAS# 1704-62-7).
Additional information
Justification for selection of acute toxicity – oral endpoint
An oral LD50 study in Wistar rats was conducted equivalent to OECD
401 without deviations and thus was chosen as the key study. Five male
and five female rats per dose group (1000, 2150, 3830 and 5000 mg/kg bw)
were dosed via oral gavage. The rats were observed over a 14-day period.
LD50 results were reported to be 2150 - 3830 mg/kg bw in males; ca. 2150
mg/kg bw in females; and 2150 - 3830 mg/kg bw in males/females. Clinical
findings were noted in all dose groups except the low dose (1000 mg/kg
bw). Dyspnea, apathy, staggering and piloerection were reported in the
5000, 3830 and 2150 mg/kg bw dose groups. Abnormal position, atonia,
paresis, cyanosis, exsiccosis and salivation were reported in the two
high-dose groups (5000 and 3830 mg/kg bw). In the animals that died,
gross pathology revealed general congestion and maddened mucosa and
bloody contents in the stomach/small intestine. No pathologic findings
were noted in the animals sacrificed following the 14-day observation
period.
Justification for selection of acute toxicity – inhalation endpoint
The key study was chosen due to it being a recent, Klimisch 1-rated
study conducted equivalent to OECD 403 and following GLP. In this study,
Sprague Dawley rats (5/sex/dose) were exposed whole body to either a 72
ppm (Dynamic bubbler) or a 63 ppm (Dynamic evaporator) vapour
concentration of DMEE for four hours. The rats were observed for 14 days
post-exposure. No clinical signs of toxicity were observed on the day of
exposure or during the 14-day post-exposure observation period for the
dynamic bubbler group. Blepharospasm and periocular wetness were the
only clinical signs of toxicity observed during the 4-hour exposure
period in the dynamic evaporator group. No clinical signs of toxicity
were observed for both sexes following exposure or during the 14-day
post-exposure observation period. Macroscopic lesions were not observed
in animals sacrificed at the end of the 14-day post-exposure period. The
only macroscopic lesions observed was a dark red (mottled) discoloration
of the lungs and liver, noted only in the one rat which died during the
study. The four hour vapour inhalation LC50 for DMEE in male and female
rats was >72 ppm (0.39 mg/L) under the conditions of this study.
Justification for selection of acute toxicity – dermal endpoint
The key study is a well-documented study following methods
equivalent to OECD Guideline 402 (Acute Dermal Toxicity). New Zealand
White rabbits (5/sex/dose) were exposed dermally under occluded
conditions for 24-hours to varying doses of undiluted DMEE (0.50, 1.00,
1.41, and 200 mL/kg in males and 0.500, 1.00, 2.00, and 4.00 ml/kg in
females). Local dermal effects included: erythema, edema, necrosis,
ecchymosis, fissuring, ulceration, desquamation and scabs. Dermal
reactions persisted through 14 days. Salvation, sluggishness, unsteady
gait, red discharge (from nose and mouth), tremors (in 2) and
prostration were among the signs of toxicity observed. No signs of
toxicity were observed in the groups exposed to 1.00 mL/kg (males) and
0.50 mL/kg (males and females). Gross pathology findings included red
and mottled lungs, red tracheas, a few discolored livers and kidneys,
and subcutaneous edema. The LD50 in males was reported to be 1.74 mL/kg
bw and in females was 2.14 mL/kg bw. Using the density for DMEE of 0.95
g/mL (OECD guideline 109) to convert to mg/kg bw resulted in LD50 values
of 1663 mg/kg bw and 2033 mg/kg bw in males and females, respectively.
Justification for classification or non-classification
Based on acute toxicity results, the suggested classification for 2-[2-(dimethylamino)ethoxy]ethanol according to EU Regulation 1272/2008 is acute dermal category 4.
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