Registration Dossier
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EC number: 942-293-6 | CAS number: -
- 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: oral
Administrative data
- Endpoint:
- short-term repeated dose toxicity: oral
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- Between 16 October 2009 and 08 March 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions. Scientific rationale for the read-across: the registration substance is a tertiary amine oxide and the read-across substance the corresponding tertiary amine so that an inter-convertibility of the registraiton substance and the proposed read-across substance can be presumed.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report Date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. certificate)
- Limit test:
- no
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Type:
- Constituent
- Details on test material:
- Sponsor's identification : Bis (2-hydroxyethyl) coco alkylamine (CAS Number 61791-31-9)
Description : pale brown viscous liquid
Batch number : S-001016
Date received : 08 July 2009
Storage conditions : approximately 4ºC in the dark, under nitrogen
Expiry date :26 June 2017
Test animals
- Species:
- rat
- Strain:
- other: Wistar Han™:HsdRccHan™:WIST strain rat
- Sex:
- male/female
- Details on test animals and environmental conditions:
- Test Animals
- Source:
Wistar Han™:HsdRccHan™:WIST strain rats from Harlan Laboratories U.K. Ltd., Blackthorn, Bicester, Oxon, UK.
- Age at study initiation:
Approximately 12 weeks old
- Weight at study initiation:
297 to 342g (male); 184 to 233g (female)
- Fasting period before study:
Not applicable
- Housing:
Initially, all animals were housed in groups of five in solid floor polypropylene cages with stainless steel mesh lids and softwood flake bedding (Datesand Ltd., Cheshire, UK). During the mating phase, animals were transferred to polypropylene grid floor cages suspended over trays lined with absorbent paper on a one male: one female basis within each dose group. Following evidence of successful mating, the males were returned to their original cages. Mated females were housed individually during gestation and lactation, in solid floor polypropylene cages with stainless steel mesh lids and softwood flakes.
- Diet:
The animals were allowed free access to food. A pelleted diet Rodent 2018C
Teklad Global Certified Diet Harlan UK Ltd, Oxon, UK was used throughout the study period. The diet was considered not to contain any contaminant at a level that might have affected the purpose or integrity of the study.
- Water:
Water intake was measured and recorded daily for each cage group (with the exception of non-recovery (satellite) animals during the mating phase). Individual daily water intakes were measures for females during the gestation and lactation phases of the study
- Acclimation period:
For 12 days
ENVIRONMENTAL CONDITIONS
- Temperature:
21 ± 2 °C
- Humidity:
55 ± 15 %
- Air changes (per hr):
At least fifteen air changes per hour
- Photoperiod (hr dark / hrs light):
12 hours continuous light and 12 hours darkness
IN-LIFE DATES:
20 October 2009 and 15 December 2009 (including recovery phase animals)
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- other: Arachis oil BP
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
For the purpose of this study the test material was prepared at the appropriate concentrations as a solution in Arachis oil BP. The stability and homogeneity of the test material formulations were previously determined by Harlan Laboratories Ltd., Shardlow, UK Analytical Services (Harlan Laboratories Ltd. Project Number: 0142-0416). Results from the previous study showed the formulations to be stable for at least twenty days. Formulations were therefore prepared twice monthly during the treatment period and stored at approximately +4ºC in the dark, under nitrogen.
Samples of each test material formulation were taken and analysed for concentration of test material at Harlan Laboratories Ltd., Shardlow, UK Analytical Services. The method used for analysis of formulations and the results obtained are given in Appendix 26. The results indicate that the prepared formulations were within plus or minus 9% of the nominal concentration.
DIET PREPARATION
- Not applicable
- Rate of preparation of diet (frequency):
Not applicable
- Mixing appropriate amounts with (Type of food):
Not applicable
- Storage temperature of food:
No data
VEHICLE
Arachis oil BP
- Justification for use and choice of vehicle (if other than water):
Not applicable
- Concentration in vehicle:
31.3, 7.5 and 2.5 mg/ml
- Amount of vehicle (if gavage):
4 ml/kg bodyweight
- Lot/batch no. (if required):
Not applicable
- Purity:
Not applicable - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The concentration of the test material in the formulations was determined by gas chromatography (GC) using an external standard technique. The test material formulations were extracted with methanol to give a final, theoretical test material concentration of approximately 0.1 mg/ml. Procedural recoveries were performed at each dose level on every analysis occasion.
Standard solutions of test material were prepared in methanol at a nominal concentration of 0.1 mg/ml. The test material formulations were sampled and analysed within five days of preparation. The results indicate that the prepared formulations were within +9% of the nominal concentration. - Duration of treatment / exposure:
- The oral administration of the test substance to rats for a period of up to fifty-four consecutive days
- Frequency of treatment:
- Daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Dose levels of 10, 30 and 125 mg/kg/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 0 mg/kg/day – control: 10 animals per sex.
10 mg/kg/day : 10 animals per sex.
30 mg/kg/day : 10 animals per sex.
125 mg/kg/day : 10 animals per sex.
Recovery (Satellite ) 0 mg/kg/day – control: 5 males only.
Recovery (Satellite ) 125 mg/kg/day : 5 males only. - Control animals:
- yes, concurrent vehicle
- Details on study design:
- Dose selection rationale:
Based on Preliminary Fourteen Day Repeated Dose Oral (Gavage) Range-Finder in the Rat (Harlan 0142-0416; see the corresponding endpoint study record)
- Rationale for animal assignment (if not random):
Random
- Rationale for selecting satellite groups:
To determine potential regression of any detected systemic responses elicited by administration of the test material
- Post-exposure recovery period in satellite groups:
Fourteen days
- Section schedule rationale (if not random):
Random- Positive control:
- Not applicable
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS:
- Yes
- Time schedule:
- Immediately before dosing, up to thirty minutes after dosing, and one and five hours after dosing, during the working week. Animals were observed immediately before dosing, thirty minutes after dosing, and one hour after dosing at weekends and public holidays (except for females during
parturition where applicable). During the treatment-free period, recovery males were observed once daily. All observations were recorded.
DETAILED CLINICAL OBSERVATIONS: Yes (see above).
- Time schedule: As above.
NEUROBEHAVIOURAL EXAMINATION:
- Yes
- Functional Observations were performed prior to the start of treatment and at weekly intervals thereafter, all animals were observed for signs of
functional/behavioural toxicity.
- Functional performance tests (motor activity, forelimb/hindlimb grip strength and sensory reactivity) were also performed on five selected males
during the final week of treatment and five Day 4 post partum females from each dose level.
BODY WEIGHT:
- Yes
- Time schedule for examinations:
- Individual bodyweights were recorded on Day 1 (prior to dosing) and then weekly for males until termination and weekly for females until mating w as evident. Bodyweights were then recorded for females on Days 0, 7, 14 and 20 post coitum, and on Days 1 and 4 post partum. Bodyweights were
also recorded prior to termination
FOOD CONSUMPTION:
- Yes
- During the maturation period, weekly food consumption was recorded for each cage of adults. This was continued for males after the mating
phase. For females showing evidence of mating, food consumption was recorded for the periods covering Days 0-7, 7-14 and 14-20. For females with live litters, food consumption was recorded on Days 1 and 4 post partum. Weekly food consumptions were performed weekly for each cage of adults throughout the study period.
- FOOD EFFICIENCY:
- Yes
- Food efficiency (the ratio of bodyweight change/dietary intake) was calculated retrospectively for males throughout the study period, and for females prior to mating.
WATER CONSUMPTION:
- Yes
- Water intake was measured gravimetrically and recorded daily for each cage group (with the exception of non-recovery animals during the mating - phase). Individual daily water intakes were measured for females during the gestation and lactation phases of the study.
OPHTHALMOSCOPIC EXAMINATION:
Not applicable
HAEMATOLOGY AND CLINICAL CHEMISTRY:
- Yes
- Time schedule for collection of blood:
- Haematological and blood chemical investigations were performed on five males and five females selected from each non-recovery test and control group prior to termination (Day 42 for males and Day 4 post partum for females). These investigations were also performed on all recovery
(satellite) males at the end of the treatment-free period (Day 56).
- Blood samples were obtained from the lateral tail vein or by cardiac puncture at termination, if applicable.
- Anaesthetic used for blood collection:
- No
- Animals fasted:
- No
OTHER:
MATING
- Animals were paired on a 1 male: 1 female basis within each dose group, for a period of up to fourteen days. Cage tray-liners were checked each
morning for the presence of ejected copulation plugs and each female was examined for the presence of a copulation plug in the vagina. A vaginal
smear was prepared for each female and the stage of the oestrous cycle or the presence of sperm was recorded. The presence of sperm within the vaginal smear and/or vaginal plug in situ was taken as positive evidence of mating (Day 0 of gestation) and the males were subsequently returned to
their original holding cages (unless required for additional pairing). Mated females were housed individually during the period of gestation and
lactation.
PREGNANCY AND PARTURITION
- Each pregnant female was observed at approximately 0830, 1230 and 1630 hours and around the period of expected parturition. Observations
were carried out at approximately 0830 and 1230 hours at weekends and public holidays. The following was recorded for each female:
i) Date of mating
ii) Date and time of observed start of parturition
iii) Date and time of observed completion of parturition
iv) Duration of gestation
LITTER SIZE
On completion of parturition (Day 0 of post partum), the number of live and dead offspring was recorded. Offspring were individually identified within each litter by tattoo on Day 1.
For each litter the following was recorded:
i) Number of offspring born
ii) Number and sex of offspring alive recorded daily and reported on Day 1 and 4
post partum
iii) Clinical condition of offspring from birth to Day 5 post partum
iv) Individual offspring weights on Day 1 and 4 post partum (litter weights were calculated retrospecively from offsring weights).
PHYSICAL DEVELOPMENT
All live offspring were assessed for surface righting reflex on Day 1 post partum. - Sacrifice and pathology:
- GROSS PATHOLOGY:
- Yes
HISTOPATHOLOGY:
Yes - Other examinations:
- MORTALITY DATA
- Yes (no unscheduled deaths ocured during the study)
ORGAN WEIGHTS
- Yes
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- effects observed, treatment-related
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- 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:
- Mortality.
No unscheduled deaths were detected.
Clinical Observations.
A higher incidence of increased salivation was detected soon after dosing and up to one hour after dosing for animals of either sex treated with 125 and 30 mg/kg/day, and also for males treated with 10 mg/kg/day when compared to controls. Regression was evident following the cessation of treatment in recovery 125 mg/kg/day males.
Functional Observations.
No treatment-related effects were evident in the weekly behavioural assessments, sensory reactivity, grip strength or motor activity.
Bodyweight.
No adverse effect on bodyweight change was detected for males or for females during the pre-mating and gestation phases. Lower bodyweight gains were evident for females treated with 125 mg/kg/day when compared to controls during the lactation phase of the study. No adverse effects were evident at 30 or 10 mg/kg/day.
Food Consumption.
No adverse effects on dietary intake were evident for males or for females during the pre-mating or gestation phases of the study. A slight reduction in dietary intake was evident for females treated with 125 mg/kg/day when compared to controls during lactation.
Water Consumption.
No overt intergroup differences in water intake were detected for males or for females during the pre-mating or gestation phases of the study. A reduction in water intake was evident for females treated with 125 mg/kg/day when compared to controls during lactation.
Reproductive performance.
Mating.
No treatment-related effects were detected in mating performance.
Fertility.
No treatment-related effects were detected in fertility.
Gestation.
No treatment-related effects were detected on gestation length.
Litter responses.
Litter size and Viability.
Lower litter sizes, live birth indices and reduced numbers of viable litters were evident at 125 mg/kg/day when compared to controls. Slightly lower numbers in corpora lutea and implantation sites were evident for females treated with 125 mg/kg/day when compared to controls, and higher post-implantation losses were also evident.
Offspring Growth and Development.
Lower total litter weights were evident at 125 mg/kg/day in comparison to control values. Bodyweights and surface righting assessments were not
affected.
Laboratory Investigations.
Haematology.
Males treated with 125 mg/kg/day showed a reduction in haemoglobin, haematocrit, mean cell haemoglobin, mean cell volume and reticulocyte counts when compared to controls. These findings were considered to be of no toxicological significance.
No treatment-related effects were evident for females treated with 125 mg/kg/day, or for animals of either sex treated with 30 and 10 mg/kg/day.
Blood Chemistry.
No significant effects were detected in the blood chemical parameters investigated.
Pathology.
Organ Weights.
Males treated with 125 mg/kg/day showed slightly higher absolute and bodyweight-relative spleen and liver weights. These findings were considered to be of no toxicological importance.
No treatment-related effects were detected for females treated at 125 mg/kg/day, or for animals of either sex treated with 30 or 10 mg/kg/day.
Necropsy.
Offspring: No treatment-related macroscopic abnormalities were detected for offspring from treated animals when compared to control litters.
Adults: Treatment-related findings were confined to the presence of a thickened non-glandular region of the stomach for one male treated with
125 mg/kg/day.
Histopathology. The following treatment-related changes were observed:
STOMACH: Acanthosis, frequently with associated hyperkeratosis, was seen in the forestomach of all animals of either sex treated with 125 mg/kg/day, and in males treated with 30 mg/kg/day. There was evidence of regression of the condition in recovery 125 mg/kg/day males following an additional fourteen days without treatment.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Remarks:
- systemic toxicity
- Effect level:
- 30 other: mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: see 'Remark'
- Dose descriptor:
- NOEL
- Remarks:
- Reproductive toxicity.
- Effect level:
- 30 mg/kg bw/day (actual dose received)
- Based on:
- other: Reproductive toxicity
- Sex:
- female
- Basis for effect level:
- other: Lower litter sizes due to lower numbers of corpora lutea and implantation sites, and higher post implantation losses were evident at 125 mg/kg/day. A NOEL was therefore considered to be 30 mg/kg/day for reproductive toxicity
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Tab 1a: Body weight development for males [g] | ||||||||||
Dose group | Day numbers relative to start date | |||||||||
| 1 | 8 | 15 | 22 | 29 | 36 | 43 | 50 | 57 | |
Control | Mean | 318.3 | 329.7 | 341.2 | 353.7 | 363.5 | 375.7 | 385.1 | 403.8 | 411.0 |
S.D. | 12.8 | 16.7 | 20.3 | 19.8 | 21.6 | 26.3 | 28.2 | 21.1 | 22.3 | |
N | 15 | 15 | 15 | 15 | 15 | 15 | 15 | 5 | 5 | |
10 mg/kg bw/day | Mean | 320.9 | 336.9 | 348.0 | 360.7 | 371.6 | 379.7 | 389.6 | - | - |
S.D. | 10.2 | 13.3 | 17.9 | 20.3 | 21.3 | 23.2 | 24.4 | - | - | |
N | 10 | 10 | 10 | 10 | 9 | 10 | 10 | 0 | 0 | |
30 mg/kg bw | Mean | 325.5 | 340.1 | 353.9 | 365.0 | 376.5 | 387.3 | 398.7 | - | - |
S.D. | 9.8 | 14.7 | 18.2 | 19.7 | 21.1 | 21.5 | 22.4 | - | - | |
N | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 0 | 0 | |
125 mg/kg bw/day | Mean | 320.9 | 330.4 | 340.7 | 353.3 | 361.5 | 372.3 | 382.9 | 395.2 | 404.8 |
S.D. | 11.7 | 15.4 | 17.8 | 21.0 | 20.9 | 22.8 | 23.8 | 20.3 | 23.0 | |
N | 15 | 15 | 15 | 15 | 15 | 15 | 15 | 5 | 5 |
Tab 1b: Body weight development for females [g] | ||||||||||
Dose group |
| Pre-mating | Gestation | Lactation | ||||||
| 1 | 8 | 15 | 0 | 7 | 14 | 20 | 1 | 4 | |
Control | Mean | 207.8 | 211.6 | 217.9 | 218.0 | 243.2 | 268.6 | 333.8 | 235.1 | 248.6 |
S.D. | 7.3 | 3.6 | 7.3 | 7.9 | 10.1 | 14.7 | 18.9 | 11.9 | 11.4 | |
N | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | |
10 mg/kg bw/day | Mean | 205.6 | 207.4 | 213.7 | 214.9 | 240.4 | 267.7 | 327.0 | 247.0 | 257.1 |
S.D. | 12.7 | 9.7 | 14.4 | 11.2 | 15.7 | 19.2 | 24.8 | 23.0 | 21.1 | |
N | 10 | 10 | 10 | 9 | 9 | 9 | 9 | 9 | 9 | |
30 mg/kg bw | Mean | 210.6 | 212.8 | 217.7 | 224.1 | 246.0 | 272.9 | 339.8 | 243.8 | 256.6 |
S.D. | 10.2 | 8.9 | 12.6 | 12.7 | 11.9 | 10.9 | 16.7 | 14.6 | 13.5 | |
N | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | 10 | |
125 mg/kg bw/day | Mean | 212.3 | 211.4 | 218.6 | 222.0 | 243.6 | 269.3 | 321.9 | 259.3 | 260.1 |
S.D. | 9.6 | 11.7 | 11.3 | 14.2 | 15.2 | 17.7 | 24.2 | 18.1 | 18.5 | |
N | 10 | 10 | 10 | 9 | 9 | 9 | 9 | 9 | 9 |
Tab 2: Hematology for males (N=5) at termination and after recovery: - data for females not shown as no difference was found for control and treated animals | ||||||||||||||
Dose group |
| Hb | RBC | Hct | MCH | MCV | MCHC | WBC | Neut | Lymph | CT | PLT | APTT | Retics |
| g/dl | 10^12/l | % | pg | g/dl | g/dl | 10^9/l | 10^9/l | 10^9/l | sec | 10^9/l | sec | % | |
At termination | ||||||||||||||
Control | Mean | 16.60 | 8.974 | 48.68 | 18.48 | 54.28 | 34.06 | 7.56 | 0.902 | 6.562 | 11.06 | 530.4 | 16.84 | 4.80 |
S.D. | 0.41 | 0.386 | 1.17 | 0.42 | 1.34 | 0.38 | 1.29 | 0.280 | 1.026 | 0.89 | 77.3 | 0.81 | 0.71 | |
10 mg/kg bw/day | Mean | 16.28 | 9.158 | 46.60 | 17.80 | 50.88** | 34.96 | 6.66 | 0.744 | 5.858 | 11.72 | 581.4 | 16.68 | 4.56 |
S.D. | 0.27 | 0.367 | 1.15 | 0.82 | 1.26 | 1.23 | 1.61 | 0.190 | 1.635 | 1.41 | 73.2 | 1.32 | 0.47 | |
30 mg/kg bw/day | Mean | 16.62 | 9.176 | 48.32 | 18.10 | 52.60** | 34.44 | 7.98 | 0.966 | 6.942 | 12.36 | 577.8 | 16.84 | 4.68 |
S.D. | 0.77 | 0.362 | 2.71 | 0.19 | 1.13 | 0.58 | 1.73 | 0.523 | 1.528 | 1.99 | 33.5 | 1.27 | 0.40 | |
125 mg/kg bw/day | Mean | 15.60** | 8.854 | 45.62* | 17.62* | 51.52** | 34.20 | 8.06 | 0.756 | 7.206 | 12.86 | 632.2* | 16.62 | 5.78* |
S.D. | 0.34 | 0.240 | 0.80 | 0.11 | 1.26 | 0.64 | 1.70 | 0.336 | 1.833 | 2.29 | 58.4 | 1.11 | 1.02 | |
After recovery | ||||||||||||||
Control | Mean | 15.66 | 8.962 | 47.64 | 17.48 | 53.20 | 32.88 | 7.22 | 0.778 | 6.356 | 9.12 | 638.0 | 13.30 | 4.58 |
S.D. | 0.39 | 0.312 | 1.43 | 0.51 | 1.67 | 0.18 | 0.75 | 0.160 | 0.717 | 0.41 | 46.9 | 1.22 | 0.40 | |
50 mg/kg bw/day | Mean | 15.40 | 9.168 | 46.76 | 16.80* | 51.00* | 32.94 | 7.64 | 1.042 | 6.512 | 9.12 | 690.8 | 14.66 | 5.54 |
S.D. | 0.66 | 0.376 | 2.35 | 0.14 | 0.80 | 0.34 | 0.36 | 0.283 | 0.432 | 0.16 | 90.8 | 0.72 | 0.91 |
Tab 3: Organ weight for males and females [g]: -data shown only for organs with statistical differences for control and treated animals | |||||||||||
| males | females | |||||||||
| At treatment termination | After recovery of 14 days | At treatment termination | ||||||||
Dose group[g] | Dose group[g] | Dose group[g] | |||||||||
Control | 10 | 30 | 125 | 0 | 125 | Control | 10 | 30 | 125 | ||
Terminal body weight | Mean | 380.8 | 389.6 | 398.7 | 382.5 | 411.0 | 404.8 | 250.0 | 257.0 | 255.4 | 259.2 |
S.D. | 31.5 | 24.4 | 22.4 | 25.2 | 22.3 | 23.0 | 8.1 | 24.5 | 12.8 | 18.5 | |
N | 10 | 10 | 10 | 10 | 5 | 5 | 10 | 9 | 10 | 9 | |
Kidneys | Mean | 1.99 | 2.18* | 2.17* | 2.15* | 2.24 | 2.24 | 1.43 | 1.42 | 1.52 | 1.53 |
S.D. | 0.20 | 0.19 | 0.13 | 0.16 | 0.13 | 0.18 | 0.10 | 0.08 | 0.08 | 0.11 | |
N | 10 | 10 | 10 | 10 | 5 | 5 | 10 | 9 | 10 | 9 | |
Liver | Mean | 11.97 | 12.34 | 12.38 | 13.40** | 12.45 | 12.34 | 10.59 | 10.19 | 10.40 | 11.43 |
S.D. | 1.20 | 0.87 | 0.90 | 1.13 | 1.79 | 0.56 | 1.26 | 1.02 | 0.86 | 1.13 | |
N | 10 | 10 | 10 | 10 | 5 | 5 | 10 | 9 | 10 | 9 | |
Spleen | Mean | 0.64 | 0.63 | 0.68 | 0.73* | 0.66 | 0.71* | 0.62 | 0.63 | 0.63 | 0.63 |
S.D. | 0.06 | 0.09 | 0.09 | 0.11 | 0.07 | 0.03 | 0.06 | 0.09 | 0.09 | 0.09 | |
N | 10 | 10 | 10 | 10 | 5 | 5 | 10 | 9 | 10 | 9 | |
Thyroid | Mean | 0.012 | 0.014 | 0.017* | 0.016* | 0.023 | 0.020 | 0.014 | 0.015 | 0.015 | 0.017 |
S.D. | 0.004 | 0.003 | 0.005 | 0.004 | 0.014 | 0.005 | 0.003 | 0.006 | 0.004 | 0.007 | |
N | 10 | 10 | 10 | 10 | 5 | 5 | 10 | 9 | 10 | 9 |
The
Applicant's summary and conclusion
- Conclusions:
- The read-across supporting substance N,N-Bis(2-hydroxyethyl)-C12-18(even numbered)alkyl-amine was investigated for its oral repeated dose toxicity according to the OECD Guideline 422. Stomach, hematopoietic system, and liver were identified as target organs at 125 mg/kg bw. The NOAEL of 30 mg/kg bw was derived for systemic toxicity and for reproductive toxicity.
- Executive summary:
The repeated dose toxicity of the registration substance is derived by use of data on the read-across supporting substance N,N-Bis(2-hydroxyethyl)-C12-18(even numbered)alkyl-amine.
N,N-Bis(2-hydroxyethyl)-C12-18(even numbered)alkyl-amine was investigated for its oral repeated dose toxicity according to the OECD Guideline 422. The rats were treated at doses of 0, 10, 30 and 125 mg/kg bw for up to forty five days. The irritant effect such as salivation and histopathologcal alteration in the gastric tract was evident at 125 mg/kg bw. Further, a possible effect on the hematopoietic system could be derived based on the minimal changes in hematology parameters and the slightly increased spleen weights in males. Also the liver weight was minimally increased for males that was considered as adaptive responce. Based on the histopathological changes observed in the stomach the NOAEL of 30 mg/kg bw was derived for the systemic toxicity.
At dose of 125 mg/kg bw lower litter size was evident. The NOAEL of 30 mg/kg bw was derived for the reproductive toxicity.
Similar toxicity pattern is expected for the registration substance. Gastric tract, hematopoietic system and liver are likely to serve as target organs at doses of 125 mg/kg bw and higher. Taking account that the chemical structure and the molecular size of the registration substance is closely similar to those of the read-across supporting substance, the NOAEL of 30 mg/kg bw is considered to be also valid for the registration substance.
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