Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 229-764-5 | CAS number: 6712-98-7
- 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
In a GLP study, conducted according to OECD Guideline 407, a NOAEL of 100 mg/kg bw/day has been determined in the rat for DEIPA, following gavage administration for 28 days (Stebbins and Zablotny, 1999).
In a FDA guideline study to GLP, the repeated dose toxicity of TIPA was investigated in rats (F1 offspring) during a 90-day feeding study. The parental group had previously been exposed to TIPA for 5 wk prior to pairing, throughout mating, gestation and lactation. Since no significant treatment-related effects were seen at any dose level at the end of the 90-day exposure period, a NOAEL of 7500 ppm (about 609 mg/kg bw/day for males and 700 mg/kg bw/day for females) was determined (Mullin, 1988).
Although a higher NOAEL was seen in the reliable 90-day study with TIPA, as this was on a read-across material, it was considered health precautionary to base any subsequent assessment on the NOAEL of 100 mg/kg bw/day seen in the 28-day study with DEIPA.
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:
- 20 Jan to 4 March 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD guideline study to GLP, with minor deviations which are not expected to affect the outcome
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
- Deviations:
- yes
- Remarks:
- Animals stratified by body weights before being randomly assigned to treatment groups.
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.7 (Repeated Dose (28 Days) Toxicity (Oral))
- Deviations:
- yes
- Remarks:
- Animals stratified by body weights before being randomly assigned to treatment groups.
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Inc. (Raleigh, NC)
- Age at study initiation: 7 weeks
- Weight at study initiation: Not specified
- Fasting period before study: Not specified
- Housing: Individually caged in sainless steel cages with wire mesh floors suspended above catch pans.
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum): Ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25
- Humidity (%): 40-70
- Air changes (per hr): 12-15
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Aqueous solution mixed prior to start of study and weekly thereafter.
VEHICLE
- Concentration in vehicle: 0, 7.5, 25, 250 mg/ml
- Amount of vehicle (if gavage): 4 ml/kg
- Purity: Not specified - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Dose samples diluted, the DEIPA derivitised, extracted into solvent and extracts analysed by gas chromatography-flame ionisation detection. Concentrations of DEIPA averaged 107-112% of target concentrations.
- Duration of treatment / exposure:
- 4 weeks
- Frequency of treatment:
- Daily
- Remarks:
- Doses / Concentrations:
0 (control), 30, 100, 1000 mg/kg bw/day
Basis:
other: Nominal concentration - No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The high dose of 1000 mg/kg bw/day represented the limit test, the remaining dose levels expected to provide dose-response data for any treatment-related effects observed in the high dose groups and to determine a no-observed-effect level (NOEL).
- Rationale for animal assignment (if not random): Stratified by body weight and then randomly assigned to treatment groups by a computer programme [deviation from guideline]
- Rationale for selecting satellite groups: No data
- Post-exposure recovery period in satellite groups: Additional groups administered 0 or 1000 mg/kg bw/day were held for a two week recovery period
- Section schedule rationale (if not random): No data - Positive control:
- None specified
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
- Cage side observations included evaluation of skin, fur, mucous membranes, respiration, nervous system function, animal behaviour, moribundity, mortality and the availability of feed and water.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Pre study and weekly for 4 weeks
BODY WEIGHT: Yes
- Time schedule for examinations: Pre study and weekly thereafter
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Not applicable
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Not applicable
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations:Before start of study and prior to necropsy for all animals designated to 4-week toxicity study. For those satellite animals, eyes were examined after the 2-week recovery period.
- Dose groups that were examined: All
HAEMATOLOGY: Yes
- Time schedule for collection of blood: At the scheduled necropsy
- Anaesthetic used for blood collection: Yes (methoxyflurane)
- Animals fasted: Yes
- How many animals: All
- Parameters examined included prothrombin time, haematocrit, haemoglobin concentration, erythrocyte count, total leukocyte count, platelet count, differential leukocyte count and erythrocyte, leukocyte and platelet morphology.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: At the scheduled necropsy
- Animals fasted: Yes
- How many animals: All
- Parameters examined included enzyme activity and concentrations of urea nitrogen, protein, globulin, cholesterol, triglycerides and electrolytes and (4 week toxicity study only) glucose, creatine and total bilirubin.
URINALYSIS: Yes
- Time schedule for collection of urine: Week prior to necropsy
- Metabolism cages used for collection of urine: No
- Animals fasted: No
- Parameters examined included specific gravity and (for 4 week toxicity study only) colour and appearance. Semiquantitative analysis of pH, bilirubin, glucose, proteins, ketones, blood and urobilinogen for the 4-week toxicity study.
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations: Prior to the start of the study and during last week of treatment.
- Dose groups that were examined: All
- Battery of functions tested: sensory activity / grip strength / motor activity - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, examination of external tissues and all orifices. Cranial cavity opened for the brain, pituitary and adjacent cervical tissues to be examined. The eyes were examined in situ by application of a moistened glass slide to each cornea. The nasal cavity was flushed via the the nasopharyngeal duct and lungs distended to an approximately normal insipratory volume with neutral , phosphate buffered 10% formalin using a syringe and blunt needle. The skin was relected from the carcass, the thoracic and abdominal cavities were opened and viscera examined. The brain, liver, kidneys, heart, adrenals, testes, epididymides, thymus and spleen were trimmed and weighed immediately for the 4-week toxicity study. The liver and kidney were trimmed and weighed immediately for the satellite groups.
HISTOPATHOLOGY: Yes , all of the following tissues examined by standard histologic procedures in the high and control groups, all tissues microscopically examined in the low and mid-dose group animals. Only the stomach was evaluated for the satellite group animals.
(Adrenals, kidneys, prostate, aorta, lacrimal/harderian glands, rectum, auditory sebaceous glands, larynx, salivary glands, bone (including joint), liver, seminal vesicles, bone marrow, lungs, skeletal muscle, brain (cerebrum, brainstem, cerebellum), mammary gland, skin and subcutis, cecum, mediastinal lymph node, spinal cord (cervical, thoracic, lumbar), cervix, mediastinal tissues, spleen, coagulating glands, mesenteric lymph node, stomach, colon, mesenteric tissues, testes, duodenum, nasal tissues, thymus, epididymides, oral tissues, thyroid gland, esophagus, ovaries, tongue, eyes, oviducts, trachea, gross lesions, pancreas, urinary bladder, heart, parathyroid glands, uterus, ileum, peripheral nerve, vagina, jejunum, pituitary). - Other examinations:
- Rectal temperature
- Statistics:
- Means and standard deviations were calculated for all continuous data.
In-life body weights evaluated using a analysis of variance (ANOVA).
Final body weight, organ weight, haematologic parameters, clinical chemistry parameters and urine specific gravity evaluated by using a two-way ANOVA. Comparisons of individual dose groups to the control group made with Dunnett's test.
Epididymides and testes weight analysed using a one-way ANOVA.
Rectal temperature and grip performance were analysed by a factorial analysis of covariance (ANCOVA).
Motor activity was analysed by a factorial repeated measures design.
All parameters were analysed for equality of variance using Bartlett's 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):
- not specified
- Description (incidence and severity):
- not applicable
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not specified
- Description (incidence and severity):
- not applicable
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- not specified
- Description (incidence and severity):
- none reported
- Details on results:
- CLINICAL SIGNS AND MORTALITY
No mortality and no treatment-related clinical observations at any dose level
BODY WEIGHT AND WEIGHT GAIN
No statistically significant differences in terminal body weights and body weight gains of any treated group compared to controls during the 4-week study period. Statistical signs of decreases in body weight seen at 1 and 2-week of recovery, period, however not considered to be of toxicological significance.
FOOD EFFICIENCY
Not examined
OPHTHALMOSCOPIC EXAMINATION
No treatment-related findings
HAEMATOLOGY
The only statistical alteration in haemotology parameters was a minimal decrease in mean haemoglobin concentration of both sexes combined in the high dose group. Statistically identified minimal decreases in the mean prothrombin time of both sexes combined , present in the low and high dose groups.
CLINICAL CHEMISTRY
Statistically-identified increase in mean urea nitrogen, aspartate aminotransferase, and (including after the 2-week recovery period) total protein, albumin, triglycerides and calcium for both sexes in the high-dose group. A statistically-identified decrease in mean cholesterol was noted for females in the high-dose group in 4-week toxicity study animals.
URINALYSIS
Statistically-significant decrease in mean urine specific gravity for both sexes combined in the mid and high dose groups. This decrease was not apparent in females following the 2-week recovery period, and it had significantly improved for males.
NEUROBEHAVIOUR
No treatment-related findings
ORGAN WEIGHTS
Statistically significant increase in mean absolute and relative kidney and liver weights of both sexes combined in the high-dose group, possibly treatment-related.
GROSS PATHOLOGY
No treatment-related gross pathologic observations
HISTOPATHOLOGY: NON-NEOPLASTIC
All males and females in the high-dose group had stomach alterations consisting of slight to moderate inflammation, hyperplasia and/or hyperkeratosis of the non-glandular mucosa at the limiting ridge. One female at this dose also had a focal erosion of the hyperplastic non-glandular mucosa. All treatment-related stomach alterations were completely resolved following the 2-week recovery period. No treatment-related findings seen in the lower mid-dose groups.
OTHER FINDINGS: RECTAL TEMPERATURE
No treatment-related findings - Dose descriptor:
- NOAEL
- Effect level:
- 100 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Critical effects observed:
- not specified
- Conclusions:
- In a GLP study, conducted according to OECD guideline 407, a NOAEL of 100 mg/kg bw/day has been determined in the rat for DEIPA, following gavage administration for 28 days.
- Executive summary:
In a GLP study, conducted according to OECD guideline 407, groups of 5 female and 5 male Fischer rats were administered 0 (control), 30, 100 and 1000 mg/kg bw/day of DEIPA (in water) by oral gavage for 28 days. Recovery was assessed in a two-week recovery period following a 4-week dosing regime, in additional groups administered 0 (control) or 1000 mg/kg bw/day. Parameters evaluated included mortality, detailed clinical observations, functional tests, ophthalmologic examination, body weight, feed consumption, clinical chemistry, haematology, urinalysis, selected organ weights, gross and histopathologic examination.
There were no mortalities or treatment-related clinical observations at any dose level. The most significant effects noted were inflammation, hyperplasia and hyperkeratosis of the non-glandular mucosa of the stomach in rats receiving 1000 mg/kg bw/day. All treatment-related stomach alterations were completely resolved following the 2 -week recovery period. Both sexes administered 1000 mg/kg bw/day showed statistically significant increases in liver and kidney weights (but no associated tissue effects), a minimal decrease in haemoglobin concentration and increases in urea nitrogen, aspartate aminotransferase, total protein, albumin, triglycerides and calcium. The high dose rats had reduced urine specific gravity. This was also seen in females at 100 mg/kg bw/day, however this was not considered significant as there were no associated toxicological alterations. There was partial or complete recovery of all treatment-related effects in the high dose group following the 2-week recovery period.
From the results of this study, an oral no-observed-adverse-effect level (NOAEL) of 100 mg/kg bw/day has been determined in the rat for DEIPA.
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 100 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Good-quality, reliable, GLP-compliant, guideline 28-day gavage study on DEIPA (Stebbins and Zablotny, 1999e) and 90-day dietary study on closely-related substance TIPA (Mullins, 1988), which together meet the REACH tonnage-driven data requirements. Adverse affects were seen at the highest tested dose (1000 mg/kg bw/day) in the 28-day gavage study with DEIPA, but not at the next dose level of 100 mg/kg bw/day (Stebbins and Zablotny, 1999e). No adverse effects seen at any dose (NOAEL > 600 mg/kg bw/day) in the 90-day dietary study (Mullins, 1988).
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
In a GLP study, conducted according to OECD Guideline 407, groups of 5 female and 5 male Fischer rats were administered 0 (control), 30, 100 or 1000 mg/kg bw/day of DEIPA (in water) by oral gavage for 28 days. Reversibility of effects was assessed in a 2-wk recovery period following a 4-wk dosing regime in additional groups administered 0 (control) or 1000 mg/kg bw/day. Parameters evaluated included mortality, detailed clinical observations, functional tests, ophthalmologic examination, body weight, feed consumption, clinical chemistry, haematology, urinalysis, selected organ weights, gross and histopathologic examination. There were no mortalities or treatment-related clinical observations at any dose level. The most significant effects noted were inflammation, hyperplasia and hyperkeratosis of the non-glandular mucosa of the stomach in rats receiving 1000 mg/kg bw/day (indicative of local effects). All treatment-related stomach alterations were completely resolved following the 2-wk recovery period. Both sexes administered 1000 mg/kg bw/day showed statistically significant increases in liver and kidney weights (but no associated tissue effects), a minimal decrease in haemoglobin concentration and increases in urea nitrogen, aspartate aminotransferase, total protein, albumin, triglycerides and calcium. The high dose rats had reduced urine specific gravity. This was also seen in females at 100 mg/kg bw/day, however this was not considered significant as there were no associated toxicological alterations. There was partial or complete recovery of all treatment-related effects in the high dose group following the 2-wk recovery period. From the results of this study, an oral no-observed-adverse-effect level (NOAEL) of 100 mg/kg bw/day has been determined in the rat for DEIPA (Stebbins and Zablotny, 1999).
No longer-term study with DEIPA is available. However, in a FDA guideline study conducted to GLP, the repeated dose toxicity of TIPA was investigated in rats (F1 offspring) during a 90-day feeding study. The parental rats had previously been exposed to TIPA for 5 wk prior to pairing, throughout mating, gestation and lactation. During the 90-day testing period, 20 F1 offspring per sex per group were fed a diet that contained 0, 500, 2000 or 7500 ppm TIPA. Clinical signs, mortality, body weights and food consumption of the offspring were recorded during the 90-day feeding period. Clinical chemistry and urine analyses were conducted after approximately 45 and 90 days of feeding. At the end of the feeding period, pathological examinations were carried out on all surviving rats. There were no significant TIPA related changes in clinical signs, body weights or food consumption. Any changes in the clinical chemistry evaluations, urine analyses, organ weights, ophthalmological examinations, gross observations or histopathological evaluations were not considered to be significant or related to TIPA administration. From these results, the NOAEL for repeated dose toxicity was determined to be 7500 ppm (about 609 mg/kg bw/day for males and 700 mg/kg bw/day for females), the highest dose tested (Mullin, 1988).
No repeated toxicity data involving the dermal or inhalation routes of exposure were available for DEIPA. However, in a guideline study to GLP, no systemic effects were evidently seen in rats (5/sex/dose) dermally exposed to the closely related TIPA at up to 3000 mg/kg bw/day (considered the systemic NOAEL) for 28 days (21 applications). Effects at the application site (namely scab formation, erythema and oedema) in rats exposed at 1000 and 3000 mg/kg bw/day, resulted in a local toxicity NOAEL of 300 mg/kg bw/day (Redmond and Johnson, 1994).
References
OECD (2009). Organisation for Economic Co-operation and Development.SIDS Initial Assessment Report for SIAM 29. The Hague, Netherlands, 20-23 October 2009. Propanolamines category. July 2009.
Redmond, J.M. and Johnson, K.A. (1994). Triisopropanolamine: Dermal Probe and 28-Day Repeated Dermal Study of Systemic Toxicity in Fischer 344 Rats. Unpublished Report of the Dow Chemical Company, Midland, MI (cited in OECD, 2009).
Justification for selection of repeated dose toxicity via oral
route - systemic effects endpoint:
Good-quality, GLP-compliant (reliability 1), guideline 28-day study
available on DEIPA which has a lower NOAEL than the 90-day study on TIPA
(reliability 2).
Justification for classification or non-classification
Based on the reliable 28-day repeated dose oral toxicity study with DEIPA (NOAEL 100 mg/kg bw/day), 90-day oral study with TIPA (NOAEL >600 mg/kg bw/day), and 28-day dermal study with TIPA (NOAEL 3000 mg/kg bw/day), classification as a repeated dose toxicant (or STOT RE) is not warranted under the EU CLP regulations.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.