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EC number: 249-655-6 | CAS number: 29463-06-7
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 015
- Report date:
- 2015
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- yes
- Remarks:
- In addition to the standard OECD 421 protocol, functional observational battery (FOB) as well as motor activity measurements (MA) were performed in all animals.
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Tris(2-hydroxyethyl)methylammonium methyl sulphate
- EC Number:
- 249-655-6
- EC Name:
- Tris(2-hydroxyethyl)methylammonium methyl sulphate
- Cas Number:
- 29463-06-7
- Molecular formula:
- C7H18NO3.CH3O4S
- IUPAC Name:
- 1,5-dihydroxy-3-(2-hydroxyethyl)pentan-3-aminium methyl sulfate
- Details on test material:
- - Name of test material (as cited in study report): Tris(2-hydroxyethyl)methylammonium methyl sulphate- Physical state: liquid- Analytical purity: 98.9% by weight- Lot/batch No.: Lot. 29734916K0- Stability under test conditions: The stability of the test substance under storage conditions over the test period was guaranteed by the sponsor andthe sponsor holds this responsibility.- Storage condition of test material: room temperature; avoid temperatures <5°C and >30°C
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS- Source: Charles River Laboratories, Research Models andServices, Germany GmbH- Age at study initiation: 10-11 weeks; males/females- Weight at study initiation: animals of comparable size and weight- Housing: During the study period, the rats were housed individually in Polycarbonate type M IIIcages supplied by TECHNIPLAST, Hohenpeißenberg, Germany and Becker & Co.,Castrop-Rauxel, Germany (floor area of about 800 cm²), with the following exceptions• During overnight matings, male and female mating partners were housed togetherin Polycarbonate type M III cages.• Pregnant animals and their litters were housed together until PND 4 (end oflactation).• For motor activity (MA) measurements the animals were housed individually inpolycarbonate cages supplied by TECNIPLAST, Hohenpeißenberg, Germany, withwire covers from Ehret, Emmendingen, Germany (floor area of about 800 cm2), andsmall amounts of bedding materialPregnant females were provided with nesting material (cellulose wadding) toward the endof gestation.Dust-free wooden bedding was used in this study (the present supplier is documented inthe raw data). Wooden gnawing blocks (Type NGM E-022) supplied by Abedd® Lab. andVet. Service GmbH, Vienna, Austria, was added for environmental enrichment.The cages with the test animals were arranged on the racks in such a way that uniformexperimental conditions (ventilation and light) were ensured.- Diet: ad libitum- Water: ad libitum- Acclimation period: at least 5 daysENVIRONMENTAL CONDITIONS- Temperature (°C): 20-24- Humidity (%): 30-70- Air changes (per hr): 15- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:Tris(2-hydroxyethyl)methylammonium methyl sulphate was applied as a solution. To prepare this solution, the appropriate amount of test substance was weighed out depending on the desired concentration. Then, drinking water was filled up to the desired weight, subsequently released with a magnetic stirrer. The test substance preparations were produced at least twice a week.
- Details on mating procedure:
- In general, each of the male and female animals was mated overnight in a 1:1 ratio for a maximum of 2 weeks. Throughout the mating period, each female animal was paired with a predetermined male animal from the same test group.The animals were paired by placing the female in the cage of the male mating partner from about 16.00 h until 06:30 - 09.00 h of the following morning. Deviations from the specified times were possible on weekends and public holidays and were reported in the raw data.A vaginal smear was prepared after each mating and examined for the presence of sperm.If sperm was detected, pairing of the animals was discontinued. The day on which sperm was detected was denoted gestation day (GD) 0 and the following day "GD 1".
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The analytical investigations of the test substance preparations were carried out as a separate study at the test facility Competence Center Analytics of BASF SE, 67056 Ludwigshafen, Germany under the responsibility of the Study Director of this test facility.The study was carried out in compliance with the Principles of Good Laboratory Practice.The stability of the test substance in drinking water at room temperature over a period of 4 days was demonstrated before the start of the study (study No. 14L00227; see PART III, Supplement).Concentration control analyses of the test substance preparations were performed in samples of all concentrations at the start and at the end of the administration period. Given that the test substance is completely miscible with drinking water, solutions were considered to be homogenous and no homogeneity analyses were carried out.
- Duration of treatment / exposure:
- The duration of treatment covered a 2-week premating period and mating in both sexes (mating pairs were from the same test group) as well as entire gestation and 4 days of lactation period in females up to one day prior to the day of scheduled sacrifice of the animals.
- Frequency of treatment:
- Continuous via drinking water
- Details on study schedule:
- N/A
Doses / concentrations
- Remarks:
- Doses / Concentrations:0 ppm, 1200 ppm, 4000 ppm and 12000 ppmBasis:nominal in water
- No. of animals per sex per dose:
- 10
- Control animals:
- yes
- Details on study design:
- The dose levels were selected based on the results of a range-finding study.
- Positive control:
- N/A
Examinations
- Parental animals: Observations and examinations:
- MortalityA check for moribund and dead animals was made twice daily on working days and oncedaily on Saturdays, Sundays and public holidays. If animals were in a moribund state, theywere sacrificed and necropsied.Clinical observationsA cageside examination was conducted at least once daily for any signs of morbidity,pertinent behavioral changes and signs of overt toxicity. Abnormalities and changes weredocumented daily for each affected animal.The littering and lactation behavior of the dams was generally evaluated in the mornings incombination with the daily clinical inspection of the dams. Only particular findings (e.g.inability to deliver) were documented on an individual dam basis.On weekdays (except public holidays) the parturition behavior of the dams was inspectedin the afternoons in addition to the evaluations in the mornings.The day of littering was considered the 24-hour period from about 15.00 h of one day untilabout 15.00 h of the following day.Detailed clinical observationsDetailed clinical observations (DCO) were performed in all animals prior to theadministration period and thereafter at weekly intervals. The findings were rankedaccording to the degree of severity, if applicable. The animals were transferred to astandard arena (50 × 37.5 cm with sides of 25 cm high). The following parameters wereexamined:1. abnormal behavior in handling2. fur3. skin4. posture5. salivation6. respiration7. activity/arousal level8. tremors9. convulsions10. abnormal movements11. gait abnormalities12. lacrimation13. palpebral closure14. exophthalmos15. assessment of the feces discharged during the examination (appearance/consistency)16. assessment of the urine discharged during the examination17. pupil sizeWater consumptionGenerally, water consumption was determined once a week for male and female parentalanimals, with the following exceptions:• Water consumption was not determined during the mating period (male and female F0animals).• Water consumption of the F0 females with evidence of sperm was determined on GD6-7, 13-14 and 19-20.• Water consumption of F0 females, which gave birth to a litter was determined forPND 3-4.Water consumption was not determined in females without positive evidence of spermduring mating and gestation periods and in females without litter during the lactation periodand in males after the premating period.Food consumptionGenerally, food consumption was determined once a week for male and female parentalanimals, with the following exceptions:• Food consumption was not determined during the mating period (male and female F0animals).• Food consumption of the F0 females with evidence of sperm was determined on GD0-7, 7-14 and 14-20.• Food consumption of F0 females, which gave birth to a litter was determined forPND 1-4.Food consumption was not determined in females without positive evidence of sperm(during the mating period of dams used in parallel) and females without litter (during thelactation period of dams used in parallel) and in males after the premating period.Body weight dataBody weight was determined before the start of the administration period in order torandomize the animals. During the administration period body weight was determined onstudy day 0 (start of the administration period) and thereafter once a week at the sametime of the day (in the morning).The body weight change of the animals was calculated from these results.The following exceptions are notable for the female animals:• During the mating period the parental females were weighed on the day of positiveevidence of sperm (GD 0) and on GD 7, 14 and 20.• Females with litter were weighed on the day of parturition (PND 0) and on PND 4.• Females without a litter and without positive evidence of sperm in the vaginal smear orwaiting for necropsy were weighed weekly and these values are only documented inthe Individual Tables (PART II).Intake of test substanceThe mean daily intake of test substance (group means) was calculated based uponindividual values for body weight and mean water consumption per cage.To calculate the mean values of entire administration period for each test group, thevalues of each study period, i.e. premating (14 days), gestation (20 days) and lactation (4days), were assessed according to days of treatment.Functional observational batteryA functional observational battery was performed in the first five surviving male animalsper test group and the first five surviving females with litter (in order of delivery) of all testgroups at the end of the administration period starting at about 10.00 h. The FOB startedwith passive observations without disturbing the animals, followed by removal from thehome cage, open field observations in a standard arena and sensorimotor tests as well asreflex tests. The findings were ranked according to the degree of severity, if applicable.The observations were performed at random. A detailed description of the methods, theranking and documentation system can be found in PART III (Supplement).Home cage observations:The animals were observed in their closed home cages; during this period any disturbingactivities (touching the cage or rack, noise) were avoided during these examinations inorder not to influence the behavior of the animals. Attention was paid to:1. Posture2. Tremors3. Convulsions4. Abnormal movements5. Impairment of gait6. Other findingsOpen field observations:The animals were transferred to a standard arena (50 × 50 cm with sides of 25 cm height)and observed for at least 2 minutes. The following parameters were examined:1. behavior on removal from the cage2. fur3. skin4. salivation5. nose discharge6. lacrimation7. eyes/pupilsize8. posture9. palpebral closure10. respiration11. tremors12. convulsions13. abnormal movements/stereotypes14. gait abnormalities15. activity/arousal level16. feces excreted within 2 minutes (appearance/consistency)17. urine excreted within 2 minutes (amount/color)18. rearing within 2 minutes19. other findingsSensory motor tests/ reflexes:The animals were then removed from the open field and subjected to following sensorymotor or reflex tests:1. Reaction to an object being moved towards the face (approach response)2. touch sensitivity (touch response)3. vision (visual placing response)4. pupillary reflex5. pinna reflex6. audition (auditory startle response)7. coordination of movements (righting response)8. behavior during handling9. vocalization10. pain perception (tail pinch)11. other findings12. grip strength of forelimbs13. grip strength of hindlimbs14. landing foot-splay testMotor activity assessmentMotor activity (MA) was also measured from 14:00 h onwards on the same day as theFOB was performed in the first five parental males and the first five surviving females withlitter (in order of delivery) per group. The examinations were performed using the TSELabmaster System supplied by TSE Systems GmbH, Bad Homburg, Germany. For thispurpose, the animals were placed in new clean polycarbonate cages with a small amountof bedding for the duration of the measurement. Eighteen beams were allocated per cage.The numbers of beam interrupts was counted over 12 intervals of 5 minutes per interval.The sequence in which the animals were placed in the cages was selected at random. Onaccount of the time needed to place the rats in the cages, the starting time was"staggered" for each animal. The measurement period began when the 1st beam wasinterrupted and finished exactly 1 hour later. No food or water was offered to the animalsduring these measurements and the measurement room was darkened after the transferof the last animal. The program required a file name for the measured data to be stored.This name consisted of the reference number and a serial number.Male reproduction dataThe pairing partners, the number of mating days until vaginal sperm was detected in thefemale animals, and the gestational status of the females were recorded for F0 breedingpairs.For the males, mating and fertility indices were calculated for F1 litters.Female reproduction and delivery dataThe pairing partners, the number of mating days until vaginal sperm were detected andgestational status were recorded for F0 females.For the females, mating, fertility and gestation indices were calculated for F1 litters.The total number of pups delivered and the number of liveborn and stillborn pups werenoted, and the live birth index was calculated for F1 litters.The implantations were counted and the postimplantation loss (in %) was calculated.To determine the number of implantation sites, the apparently non-pregnant uteri werestained for about 5 minutes in 1% ammonium sulfide solution according to the method ofSALEWSKI (Salewski, E.; 1964). Then the uteri were rinsed carefully in physiologic saltsolution (0.9% NaCl). Thereafter the implantation sites were recorded for calculation of thepostimplantation loss.
- Oestrous cyclicity (parental animals):
- N/A
- Sperm parameters (parental animals):
- N/A
- Litter observations:
- Litter/PupsLitter dataPup number and status at deliveryAll pups delivered from the F0 parents (F1 litter) were examined as soon as possible onthe day of birth to determine the total number of pups, the sex and the number of livebornand stillborn pups in each litter. At the same time, the pups were also being examined formacroscopically evident changes. Pups, which died before this initial examination, weredefined as stillborn pups.Pup viability/mortalityIn general, a check was made for any dead or moribund pups twice daily on workdays(once in the morning and once in the afternoon) or as a rule, only in the morning onSaturdays, Sundays or public holidays.The number and percentage of dead pups on the day of birth (PND 0) and of pups dyingbetween PND 1-4 (lactation period) were determined. Pups which died accidentally orwere sacrificed due to maternal death were not included in these calculations. The numberof live pups/litter was calculated on the day after birth, and on lactation day 4. The viabilityindex was calculated.Sex ratioOn the day of birth (PND 0) the sex of the pups was determined by observing the distancebetween the anus and the base of the genital tubercle; normally, the anogenital distance isconsiderably greater in male than in female pups. The sex of the pups was finallyconfirmed at necropsy.The sex ratio was calculated at day 0 and day 4 after birth.Pup clinical observationsThe live pups were examined daily for clinical symptoms (including gross-morphologicalfindings) during the clinical inspection of the dams.Pup body weight dataThe pups were weighed on the day after birth (PND 1) and on PND 4. Pups' body weightchange was calculated from these results. The individual weights were always determinedat about the same time of the day (in the morning). In the summary tables pup bodyweights and pup body weight change are listed for males, females and males + females.“Runts” were defined on the basis of the body weights on PND 1. "Runts" are pups thatweigh less than 75% of the mean weight of the respective control pups.
- Postmortem examinations (parental animals):
- PATHOLOGYNecropsyAll parental animals were sacrificed by decapitation under isoflurane anesthesia. Theexsanguinated animals were necropsied and assessed by gross pathology, specialattention being given to the reproductive organs.Organ weightsThe following weights were determined in all animals sacrificed on schedule:1. Anesthetized animals2. Epididymides3. Testes4. KidneysOrgan/tissue fixationThe following organs or tissues were fixed in 4% neutral-buffered formaldehyde solution orin modified Davidson’s solution:1. All gross lesions2. Cervix3. Coagulating glands4. Epididymides (modified Davidson’s solution)5. Ovaries (modified Davidson’s solution)6. Oviducts7. Prostate gland8. Seminal vesicles9. Testes (modified Davidson’s solution)10.Vagina11.Uterus (uteri of all cohabited female F0 parental animals were stained according toSalewski’s method: see chapter 3.8.1.1112.KidneysHistopathologyFixation was followed by histotechnical processing, examination by light microscopy andassessment of findings in the following organs in all the control and high dose group animals:TestesEpididymidesOvariesThe organs were trimmed according to the “Revised guides for organ sampling and trimming in rats and mice” (Ruehl-Fehlert et al., 2003; Kittel et al., 2004; Morawietz et al., 2004).A correlation between gross lesions and histopathological findings was attempted.
- Postmortem examinations (offspring):
- Pup necropsy observationsAll pups with scheduled sacrifice on PND 4 were sacrificed under isoflurane anesthesiawith CO2. All pups were examined externally and eviscerated; their organs were assessedmacroscopically.All stillborn pups and all pups that died before PND 4 were examined externally,eviscerated and their organs were assessed macroscopically.All pups without notable findings or abnormalities were discarded after their macroscopicevaluation. Animals with notable findings or abnormalities were evaluated on a case-bycasebasis, depending on the type of finding noted.
- Statistics:
- Detailed statisitical analyses were conducted as indicated in the study report.
- Reproductive indices:
- see parental animals: Observations and examinations
- Offspring viability indices:
- see litter observations
Results and discussion
Results: P0 (first parental generation)
Details on results (P0)
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Remarks:
- general systemic toxicity, neurotoxicity and reproductive performance and fertility
- Effect level:
- 12 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical signs
- gross pathology
- reproductive performance
Results: F1 generation
Details on results (F1)
Effect levels (F1)
- Dose descriptor:
- NOAEL
- Remarks:
- developmental toxicity
- Generation:
- F1
- Effect level:
- 12 000 ppm
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical signs
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
ANALYSES
Stability analysis
The stability of the test substance in drinking water was demonstrated over a period of 4
days at room temperature. As the mixtures were stored no longer than this time period, the
stability was guaranteed (project No. 14L00227).
Homogeneity control analyses
Given that the test substance was completely miscible with drinking water, solutions were
considered to be homogenous without further analysis.
Concentration control analysis of the test substance preparations
At the beginning of the administration period (study day 0: 23 Feb 2015) samples 3 - 5
were taken and send to the analytical laboratory (project No. 15L00112). The values of
sample numbers 3 and 4 were found to be in the range of 90-110% of the nominal
concentrations (see Part III, Supplement). The concentrations of sample No. 5 (64%) and
5R (retain sample, 56%) were not in good accordance with the expected concentration.
Towards the end of the administration period (study day 52: 16 Apr 2015) another
analytical examination was carried out. Samples 8 - 10 were taken and sent to the
analytical laboratory (project No. 15L00204). The values for each test group were found to
be in the range of 90-110% of the nominal concentrations.
Therefore, the deviations found in samples 5 and 5R were assessed to be incidental.
Food analyses
On the basis of duration of use and the analytical findings with respect to chemical and
microbiological contaminants the diet was found to be suitable. Fed. Reg. Vol. 44, No. 91
of 09 May 1979, p. 27354 (EPA), served as a guideline for maximum tolerable chemical
contaminants. The number of microorganisms did not exceed 1*105/g food. Individual
results can be found in the archives of the Experimental Toxicology and Ecology of
BASF SE.
Drinking water analyses
On the basis of the analytical findings the drinking water was found to be suitable. German
“Trinkwasserverordnung” (Drinking Water Regulation) served as a guideline for maximum
tolerable contaminants. Individual results can be found in the archives of the Experimental
Toxicology and Ecology of BASF SE.
Bedding and enrichment analyses
On the basis of the analytical findings the bedding and the enrichment are found to be
suitable. Levels given in Lab. Animal, Nov-Dec 1979, pp. 24-34, served as a guideline for
maximum tolerable contaminants. Individual results are to be found in the archives of the
Experimental Toxicology and Ecology of BASF SE.
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of the present Reproduction/Developmental Toxicity Screening Testthe oral administration of Tris(2-hydroxyethyl)methylammonium methyl sulphate to maleand female Wistar rats did not result in signs of systemic toxicity up to a concentration of12000 ppm. Thus, the no observed adverse effect level (NOAEL) for general systemictoxicity was 12000 ppm for male (774 mg/kg bw/d) and female Wistar rats (1564 mg/kgbw/d).In addition, signs of neurotoxicity were not observed. The NOAEL for neurotoxicity was setto 12000 ppm for male and female animals.The NOAEL for reproductive performance and fertility was also set to 12000 ppm for maleand female Wistar rats.The NOAEL for developmental toxicity was 12000 ppm.
- Executive summary:
Tris(2-hydroxyethyl)methylammonium methyl sulphate was administered orally via drinking
water to groups of 10 male and 10 female Wistar rats (F0 animals) at dose levels of 0 ppm
(test group 0), 1200 ppm (test group 1), 4000 ppm (test group 2) and 12000 ppm (test
group 3).
The duration of treatment covered a 2-week premating and a mating period in both sexes,
approximately 1 week post-mating in males, and the entire gestation period as well as 4
days of lactation and 2 weeks thereafter in females.
Regarding clinical examinations, signs of general systemic toxicity were not observed in
male or female parental animals of test groups 1-3 (1200, 4000 and 12000 ppm) during
the entire study period. In addition, functional observational battery (FOB) as well as motor
activity measurements (MA) did not reveal any signs of a neurotoxic potential.
Fertility indices for male and female animals were not impaired by test-substance
administration even at a concentration of 12000 ppm. In addition, live birth indices of pups
in all test groups were not influenced.
The viability index as indicator for pup mortality was not altered.
Regarding pathology, no treatment-related findings were observed with regard to organ
weights, macroscopic and histologic findings. All findings occurred either individually or
were biologically equally distributed over control and treatment groups. They were
considered to be incidental or spontaneous in origin and without any relation to treatment.
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