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EC number: 203-978-9 | CAS number: 112-50-5
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- February to April 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- 2016 version
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- Species and strain accepted by many regulatory authorities and there are ample experience and background data on them.
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Italia S.p.A., Calco (Lecco), Italy.
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 7 to 8 weeks old
- Weight at study initiation: 210 - 224 g for males and 179 - 199 g for females
- Fasting period before study: no
- Housing: From arrival to pairing, 5 of one sex to a cage, in polysulfone
solid bottomed cages (59.5×38×20cm). Nesting material was provided inside suitable bedding bags and changed at least 2x/week. During mating, animals house 1 of each sex, then individually for remainder of study.
twice a week.
- Diet (ad libitum except during fasting period prior to sampling for clinical pathology): laboratory rodent diet (4 RF 21, ex Mucedola S.r.l., Italy)
- Water (ad libitum): drinking water (softened by reverse osmosis)
- Acclimation period: 27 days
DETAILS OF FOOD AND WATER QUALITY:
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C±2°C
- Humidity (%): 55%±15%
- Air changes (per hr): 15 to 20
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: February to April 2021 - Route of administration:
- oral: drinking water
- Details on route of administration:
- The oral drinking water route was selected as it is a more realistic route of exposure of the test item in man than oral gavage and would allow comparison with other studies on similar substances where this route of exposure has been used previously.
- Vehicle:
- water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Fresh solution prepared every 6 days. Stability tests previously confirmed solutions were stable for a 7 day period.
VEHICLE
- Concentration in vehicle: Concentrations were based on findings from the range finder study and were made up as follows: 1000, 3000 and 10000 ppm for males (low, mid, hiigh dose groups respectively) and 950, 2900 and 9500 ppm for females (low, mid, hiigh dose groups respectively.)
- Purity: information held by laboratory but not included in report. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis was performed in a separate study in order to validate both the analytical method and the preparation procedure and to verify the stability of the preparations. The analytical method was validated in the theoretical range from 0.8 to 100 mg/mL. Linearity, accuracy and precision were within the limits stated in the validation protocol (r >
0.99; accuracy 90-110%; precision CV <5%). Samples of the preparations made on two occasions during the study (Day 1 and again towards the end of the study) were analysed to check the concentration. The method used was gas chromatography with flame ionisation detection of the analyte. - Duration of treatment / exposure:
- Males: 35/36 days. Females 53-65 days.
- Frequency of treatment:
- Continous via drinking water
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
Based on a range finder study with non-pregnant animals
- Fasting period before blood sampling for clinical biochemistry: yes, overnight - Positive control:
- No
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily, twice daily for mortality
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly, incljuded as part of functional observation battery: Handling reactivity, Lachrymation, Palpebral closure, Salivation, Piloerection, Rearing, Spasms, Tonic spasms, Clonic spasms, Tonic-clonic spasms, Myoclonia, Mobility impairment, Arousal (animal activity), Vocalisation, Stereotypies, unusual respiratory pattern, Bizarre behaviour, Urination, Tremors, Gait
BODY WEIGHT: Yes
- Time schedule for examinations: at least weekly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Time schedule for examinations: weekly
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
- Time schedule for examinations: daily
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: females at sacrifice.
- Anaesthetic used for blood collection: Males: Yes (isoflurane) from retro-orbital sinus except for coagulation tests where vena cava used. Females: No, abdominal vena cava used.
- Animals fasted: Yes (overnight) except for coagulation test
- How many animals: not specified
- Parameters checked: Haematocrit, Haemoglobin, Red blood cell count, Reticulocyte, Mean red blood cell volume, Mean corpuscular haemoglobin, Mean corpuscular hemoglobin concentration, White blood cell count, Differential leucocyte count (Neutrophils, Lymphocites, Eosinophils, Basophils, Monocytes, Large unstained cells, Platelets, Prothrombin time.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood:
females at sacrifice.
- Anaesthetic used for blood collection: Males: Yes (isoflurane) from retro-orbital sinus except for coagulation tests where vena cava used. Females: No, abdominal vena cava used.
- Animals fasted: Yes (overnight) except for coagulation test
- How many animals:
not specified
- Parameters checked: Alkaline phosphatase, Alanine aminotransferase, Aspartate aminotransferase, Gamma-glutamyltransferase, Urea, Creatinine, Glucose, Triglycerides, Bile acids, Total bilirubin,Total cholesterol, total protein, Albumin, Globulin, A/G Ratio, Sodium, Potassium, Calcium, Chloride, Inorganic phosphorus.
PLASMA/SERUM HORMONES-IMMUNOLOGY: Yes - T4 and TSH hormones
- Sampling time 14 days postpartum
- Time of blood sample collection: Termination
- Animals fasted: Not specified
- How many animals: Not specified
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: Yes / No / Not specified
- Time schedule for examinations: once, towards end of treatment
- Dose groups that were examined: 5 animals from each sex and dose group, randomly selected.
- Battery of functions tested: sensory activity to stimuli, grip strength and motor activity
IMMUNOLOGY: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes. Following weighed: Adrenal glands, brain, epididymides, heart, kidney, liver, ovaries, prostate, seminal vesicles, spleen, testes, thymus, thyroid, uterus-cervix
HISTOPATHOLOGY: Yes, (5M/5F from high dose and control group randomly selected plus all abnormalities); as above plus: bone marrow, caecum, clitoral gland, colon, duodenum, eyes, femur with knee joint, ileum, jejenum incl Peyer's patches, lngs,lymph nodes (cervical & mesenteric), mammary glands (both), nasal cavity, oesophagus, parathyroid gland, penis, rectum, sciatic nerve, spinal cord, skeletal muscle, stomach, trachea, urinary bladder, vagina. - Statistics:
- Standard deviations were calculated as appropriate. For variables, e.g. body weight, food consumption, clinical pathology parameters and organ weights, the significance of the differences amongst group means was assessed by Dunnett’s test or a modified t test, depending on the homogeneity of data. The non-parametric Kruskal-Wallis analysis of variance was used for the other parameters. Intergroup differences between the control and treated groups were assessed by the nonparametric version of the Williams test. Statistical significance set at p<0.05.
- Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One high dose female was sacrificed for humane reasons on the day of start of parturition (Day 23 post coitum) due to the difficulties with delivery. Pale appearance and red staining of the vagina were observed prior to sacrifice. Macroscopically, pale color of liver and red staining of the urogenital area were observed. At microscopic observation, inflammation and congestion of uterus and atrophy of thymus were noted. The factors contributory to the illness status of this animal were ascribed to difficulty in delivery and unrelated to treatment.
- 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
- Description (incidence and severity):
- A statistically significant increase of monocytes recorded in mid dose males (300mg/kg/day) was not seen in the top dose group and, since ithre was no dose response relationship, was considered to be incidental.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Cholesterol was higher than controls in females dosed at 1000 mg/kg/day (44%). Since data within groups were homogeneous and a minimal increase of cholesterol was also recorded in females dosed at 300 mg/kg/day (26% above controls, but not reaching statistical significance), a correlation with treatment cannot be excluded. However, due to the slight severity and in the absence of other related changes (histopathological findings and/or other clinical chemistry parameters), the cholesterol increase was not considered to be adverse. An increase of bile acids recorded in females dosed at 1000 mg/kg/day was due to the high value of one animal ). Due to the minimal incidence, this finding was considered to be unrelated to treatment. The only other statistically significant differences between control and treated animals (decrease of alkaline phosphatase and bilirubin and increase of cholesterol in males, increase of globulin in females) were not dose related and/or of minimal severity, therefore they were considered to be incidental.
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- effects observed, non-treatment-related
- Description (incidence and severity):
- There was a statistically significant increase in motor activity in the high dose males. However, despite there being a dose response, this outcome was driven by two animals with high activity whilst the comparatively low values seen in the concurrent control were driven by 3 animals. (Counter units: concurrent control 671 (SD 174), historic control 745 (5 year data), group 4: 927 (SD=141). The effects was not seen in females. No treatment-related changes were seen in the sensory reaction to stimuli (including grip strength and landing footsplay) measured at the end of the study in all treated groups of both sexes. The findings were not considered as a result of treatment and not adverse. See table below in 'other information' for individual animal scores.
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- There were no treatment-related changes in terminal body weight and organ weights when compared to the controls that were considered adverse. An increase in absolute and relative mean kidney weights in high dose treated males (13% for relative kidneys weight) was not correlated to any histopathological changes, and was in the range of expected spontaneous changes in rats of the same age and therefore considered unrelated to treatment.
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- No treatment-related changes were recorded in parental males and in pups on Day 14 post partum on the levels of T4 and TSH. Thyroid stimulating hormone (TSH) was increased in two parental males dosed at 300 mg/kg/day. Compared with mean control, changes were 2.4 and 2.5 fold, respectively. Due to the absence of dose-relation and the minimal incidence, this change was considered to be unrelated to treatment
- Dose descriptor:
- NOAEL
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Critical effects observed:
- no
- Executive summary:
In a guideline and GLP OECD422 combined repeat dose and reproductive toxicity study, SD rats were exposed to 2 -(2 -(2 -ethoxyethoxy)ethoxy)ethanol (TEGEE) by drinking water for 35/36 days for males and 53 -65 days for females. The average actual doses received by males were 83, 262 and 901 mg/kgbw/day and by females 122, 376 and 1296 mg/kgbw/day. During the post partum/lactation phase, females were receiving 1714 mg/kgbw/day. No effects were seen in any dose group and for either sex that were deemed to be adverse and attributable to treatment.
A treatment-related increase in cholesterol was observed in females dosed at nominal 300 and 1000 mg/kg/day, which only reached statistical significance in the high dose group. This increase was not considered to be adverse due to the slight severity and the absence of other related changes (histopathological findings and/or other clinical chemistry parameters. The NOAEL in the study was determined to be 1000 mg/kgbw/day (actual 906 in males, 1296 in females) , the maximum dose used.
Motor activity values recorded for males:
Animal # | Concurrent control | Group 4 |
1 | 855 | 1085 |
2 | 456 | 746 |
3 | 840 | 819 |
4 | 638 | 1024 |
5 | 565 | 959 |
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- 2016 version
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- 2-(2-(2-ethoxyethoxy)ethoxy)ethanol
- EC Number:
- 203-978-9
- EC Name:
- 2-(2-(2-ethoxyethoxy)ethoxy)ethanol
- Cas Number:
- 112-50-5
- Molecular formula:
- C8H18O4
- IUPAC Name:
- 2-[2-(2-ethoxyethoxy)ethoxy]ethan-1-ol
- Reference substance name:
- 2,2'-oxydiethanol
- EC Number:
- 203-872-2
- EC Name:
- 2,2'-oxydiethanol
- Cas Number:
- 111-46-6
- Molecular formula:
- C4H10O3
- IUPAC Name:
- 2,2'-oxydiethanol
- Test material form:
- liquid
- Details on test material:
- Other identified impurities, all less than 0.1% include water, triethylene glycol methyl ether and diethylene glycol ethyl ether. Balance of 0.08% not identified.
Constituent 1
impurity 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- Species and strain accepted by many regulatory authorities and there are ample experience and
background data on them. - Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Italia S.p.A., Calco (Lecco), Italy.
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 7 to 8 weeks old
- Weight at study initiation: 210 - 224 g for males and 179 - 199 g for females
- Fasting period before study: no
- Housing: From arrival to pairing, 5 of one sex to a cage, in polysulfone
solid bottomed cages (59.5×38×20cm). Nesting material was provided inside suitable bedding bags
and changed at least 2x/week. During mating, animals house 1 of each sex, then individually for r
emainder of study.
twice a week.
- Diet (ad libitum except during fasting period prior to sampling for clinical pathology): laboratory
rodent diet (4 RF 21, ex Mucedola S.r.l., Italy)
- Water (ad libitum): drinking water (softened by reverse osmosis)
- Acclimation period: 27 days
DETAILS OF FOOD AND WATER QUALITY:
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22°C±2°C
- Humidity (%): 55%±15%
- Air changes (per hr): 15 to 20
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: February to April 2021
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
DIET PREPARATION
- Rate of preparation of diet (frequency):
- Mixing appropriate amounts with (Type of food):
- Storage temperature of food:
VEHICLE
- Justification for use and choice of vehicle (if other than water):
- Concentration in vehicle:
- Amount of vehicle (if gavage):
- Lot/batch no. (if required):
- Purity:PREPARATION OF DOSING SOLUTIONS: Fresh solution prepared every 6 days. Stability tests pr
eviously confirmed solutions were stable for a 7 day period.
VEHICLE
- Concentration in vehicle: Concentrations were based on findings from the range finder study and
were made up as follows: 1000, 3000 and 10000 ppm for males (low, mid, hiigh dose groups respec
tively) and 950, 2900 and 9500 ppm for females (low, mid, hiigh dose groups respectively.)
- Purity: information held by laboratory but not included in report. - Details on mating procedure:
- - M/F ratio per cage: 1:1
- Length of cohabitation: up to 14 days
- Proof of pregnancy: vaginal plug in situ or in tray or sperm in vaginal smear (referred to as [day 0 / day 1] of pregnancy
- After14 days of unsuccessful pairing replacement the study was continued with the non-pregnant female for the repeat dose element of the study, with the female sacrified 28 days later.
- Further matings not performed (only affected one pair in high dose group.)
- After successful mating each pregnant female was caged individually.
- Any other deviations from standard protocol: no - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analysis was performed in a separate study in order to validate both the analytical method and the preparation procedure and to verify the stability of the preparations. The analytical method was validated in the theoretical range from 0.8 to 100 mg/mL. Linearity, accuracy and precision were within the limits stated in the validation protocol (r > 0.99; accuracy 90-110%; precision CV <5%). Samples of the preparations made on two occasions during the study (Day 1 and again towards the end of the study) were analysed to check the concentration. The method used was gas chromatography with flame ionisation detection of the analyte.
- Duration of treatment / exposure:
- Duration of treatment / exposure
Males: 35/36 days. Females 53-65 days. - Frequency of treatment:
- Continous via drinking water
- Details on study schedule:
- Further information not required for a screening study
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- Dose / conc.:
- 300 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- Remarks:
- For actual doses received, see table in section 'any other information on methods')
- No. of animals per sex per dose:
- Males: 35/36 days. Females 53-65 days.
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Based on a range finder study with non-pregnant animals
- Positive control:
- No
Examinations
- Parental animals: Observations and examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily, twice daily for mortality
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly, incljuded as part of functional observation battery: Handling reactivity,
Lachrymation, Palpebral closure, Salivation, Piloerection, Rearing, Spasms, Tonic spasms, Clonic sp
asms, Tonic-clonic spasms, Myoclonia, Mobility impairment, Arousal (animal activity), Vocalisation,
Stereotypies, unusual respiratory pattern, Bizarre behaviour, Urination, Tremors, Gait
BODY WEIGHT: Yes
- Time schedule for examinations: at least weekly
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Time schedule for examinations: weekly
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
- Time schedule for examinations: daily
OTHER: A parturition check was performed from Day 20 to Day 25 post coitum. Gestation length was calculated as the time between the day of successful mating (Day 0 post coitum) and the day of birth when the parturition was defined complete (Day 0 post partum). - Oestrous cyclicity (parental animals):
- Oestrous cycle was monitored by vaginal smears in all stock females for 2 weeks before allocation in order to exclude from the study females with irregular cycle. For females allocated to groups, vaginal smears were taken in the morning from Day 1 of treatment, up to positive identification of mating including not less than 2 weeks before the pairing. The vaginal smear data were examined to determine the following:
– anomalies of the oestrous cycle;
– pre-coital interval (i.e., the number of nights paired prior to the detection of mating).
Vaginal smears were also taken from all females, before despatch to necropsy. - Sperm parameters (parental animals):
- The identification of the stages of the spermatogenic cycle was also performed in five randomly selected males of the control and high dose groups as part of the histopathology. The testes and epididymides were cut at 2-3 micrometer thickness and stained with Periodic Acid Schiff (PAS). The morphological evaluation of the seminiferous epithelium (staging of spermatogenic cycle) was performed. The evaluation took into account the tubular stages of the spermatogenic cycle, in order to identify treatment-related effects, such as: missing germcell layers or types, retained spermatids, multinucleated or apoptotic germcells and sloughing of spermatogenic cells into the lumen. The PAS- H stained sections were used to identify the spermatogenic stages. Otherwise no other sperm parameters were assessed.
- Litter observations:
- STANDARDISATION OF LITTERS
- Performed on day 4 postpartum: yes, all pups were weighed and litters in excess of 8 offspring were culled to 8 (4 males and 4 females, where possible) by a random selection.
PARAMETERS EXAMINED
The following parameters were examined in offspring: number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, physical or behavioural abnormalities, anogenital distance (AGD - post partum day 1 normalised to cube root of bodyweight measured on same day), presence of nipples/areolae in male pups.
GROSS EXAMINATION OF DEAD PUPS: Pups dying during the lactation period were weighed before the despatch to necropsy. All pups found dead in the cage were examined for external and internal abnormalities. - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: All surviving animals[after the completion of the mating period on Days 35 and 36 of the study.
- Maternal animals: All surviving animals day 14 post partum
GROSS PATHOLOGY: Yes. Following weighed: Adrenal glands, brain, epididymides, heart, kidney, liver, ovaries, prostate, seminal vesicles, spleen, testes, thymus, thyroid, uterus-cervix. Parental females were examined also for the number of visible implantation sites (pregnant animals) and the number of corpora lutea (pregnant animals). Uteri of apparently non-pregnant females were immersed in a 20% solution of ammonium sulphide to reveal evidence of implantation.
HISTOPATHOLOGY: Yes, as above plus (5M/5F from high dose and control group randomly selected plus all abnormalities): bone marrow, caecum, clitoral gland, colon, duodenum, eyes, femur with knee joint, ileum, jejenum incl Peyer's patches, lngs,lymph nodes (cervical & mesenteric), mammary glands (both), nasal cavity, oesophagus, parathyroid gland, penis, rectum, sciatic nerve, spinal cord, skeletal muscle, stomach, trachea, urinary bladder, vagina. - Postmortem examinations (offspring):
- SACRIFICE
- day 4 and 14 post partum
- These animals were subjected to postmortem examinations (macroscopic and/or microscopic examination) as follows:
GROSS NECROPSY
- All culled pups sacrificed on Day 4 post partum were subjected to an external examination. Sex was determined by internal gonads inspection. All live pups sacrificed on Day 14 post partum were killed and examined for external abnormalities and sex confirmation by gonadal inspection. Thyroids were weighed from one male and one female pup selected for blood collection for hormones determination and preserved in 10% neutral buffered formalin. The thyroid weights were determined after fixation.
HISTOPATHOLOGY / ORGAN WEIGHTS
- not examined - Statistics:
- Standard deviations were calculated as appropriate. The non-parametric Kruskal-Wallis analysis of variance was used for the non-continuous parameters. Intergroup differences between the control and treated groups were assessed by the nonparametric version of the Williams test. Statistical significance set at p<0.05.
- Reproductive indices:
- Males: Copulatory index (# with confirmed mating/number cohabited), Fertility index (# which produced pregnancy/number cohabited).
Females: Copulatory index (# with confirmed mating/number cohabited), Fertility index (# pregnant/number cohabited).
Both sexes: Pre coital Interval = number of nights paired prior to detection of mating.
Pre-implantation loss, pre-natal loss, sex ratios (days 0, 4, 13) - Offspring viability indices:
- Post-natal loss (days 0, 4, 13)
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One high dose female was sacrificed for humane reasons on the day of start of parturition (Day 23 post coitum) due to the difficulties with delivery. Pale appearance and red staining of the vagina were observed prior to sacrifice. Macroscopically, pale color of liver and red staining of the urogenital area were observed. At microscopic observation, inflammation and congestion of uterus and atrophy of thymus were noted. The factors contributory to the illness status of this animal were ascribed to difficulty in delivery and unrelated to treatment.
- 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
- Description (incidence and severity):
- There were no treatment-related changes in terminal body weight and organ weights hat were considered adverse when compared to the controls.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Cholesterol was higher than controls in females dosed at 1000 mg/kg/day (44%). Since data within groups were homogeneous and a minimal increase of cholesterol was also recorded in females dosed at 300 mg/kg/day (26% above controls, but not reaching statistical significance), a correlation with treatment cannot be excluded. However, due to the slight severity and in the absence of other related changes (histopathological findings and/or other clinical chemistry parameters), the cholesterol increase was not considered to be adverse. An increase of bile acids recorded in females dosed at 1000 mg/kg/day was due to the high value of one animal ). Due to the minimal incidence,
this finding was considered to be unrelated to treatment. The only other statistically significant differences between control and treated animals (decrease of alkaline phosphatase and bilirubin and increase of cholesterol in males, increase of globulin in females) were not dose related and/or of minimal severity, therefore they were considered to be incidental. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Description (incidence and severity):
- There were no treatment-related changes in terminal body weight and organ weights hat were considered adverse when compared to concurrent and historic controls.
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- T4 and TSH hormones
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- no effects observed
- Reproductive function: sperm measures:
- no effects observed
- Description (incidence and severity):
- Based on a lack of effects seen following histopathology of the testes and epididymides.
- Reproductive performance:
- no effects observed
- Description (incidence and severity):
- Gestation length was similar between treated and control groups. No treatment related effectswere seen in the number of implantations or in pre-implantation and pre-natal loss in all groups.
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Remarks:
- No adverse effects seen up to and including the limit dose of 1000 mg/kgbw/day
Target system / organ toxicity (P0)
- Critical effects observed:
- no
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- Any pre-weaning clinical signs observed were comparable between low, mid-, high dose and control groups or considered incidental.
- Mortality / viability:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- 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:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Sexual maturation:
- no effects observed
- Description (incidence and severity):
- Sex ratios at birth, on Days 4 and 14 post partum did not show treatment-related effects, when calculated as percentage of males.
- Anogenital distance (AGD):
- no effects observed
- Nipple retention in male pups:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- No treatment-related differences were noted in thyroid weight between control and pups of treated groups. No other organs weighed.
- Gross pathological findings:
- no effects observed
- Description (incidence and severity):
- Deceased pups: No macroscopic examination could be performed, since autolysed abdominal organs were observed in the majority of the deceased pups of control and treated groups. No abnormalities were noted in the other deceased pups at necropsy examination.
Pups sacrificed on Days 4 and 14 post partum: No findings were recorded in pups sacrificed for humane reason due to the sacrifice occurred
in the relative dam. No findings were recorded in pups sacrificed on Day 4 post partum (culled pups) or Day 14 post partum. - Histopathological findings:
- not examined
- Other effects:
- no effects observed
- Description (incidence and severity):
- Litter data of treated females (e.g. total litter size, live litter size, pup loss, litter weight and mean pup weight) did not show dose-related or treatment-related differences.
Developmental neurotoxicity (F1)
- Behaviour (functional findings):
- not examined
Developmental immunotoxicity (F1)
- Developmental immunotoxicity:
- not examined
Effect levels (F1)
- Dose descriptor:
- NOAEC
- Generation:
- F1
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Remarks:
- No adverse effects seen up to and including the limit dose of 1000 mg/kgbw/day
Target system / organ toxicity (F1)
- Critical effects observed:
- no
Overall reproductive toxicity
- Reproductive effects observed:
- no
Applicant's summary and conclusion
- Executive summary:
In a guideline and GLP OECD422 combined repeat dose and reproductive toxicity study, SD rats were exposed to 2 -(2 -(2 -ethoxyethoxy)ethoxy)ethanol (TEGEE) by drinking water for 35/36 days for males and 53 -65 days for females. The average actual doses received by males were 83, 262 and 901 mg/kgbw/day and by females 122, 376 and 1296 mg/kgbw/day. During the post partum/lactation phase, females were receiving 1714 mg/kgbw/day. No reproductive effects were seen in any dose group and for either sex that were deemed to be adverse and attributable to treatment. The NOAEL in the study was determined to be 1000 mg/kgbw/day (actual 906 in males, 1296 in females) , the maximum dose used.
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