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EC number: 268-625-3 | CAS number: 68131-72-6
- 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:
- Between 10 August 2011 and November 2011
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: -
- 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 studywas conducted under GLP conditions.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: EPA OPPTS 870.3650 (Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test) as at July 2000
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: EC 440/2008 (laying down test methods pursuant to Regulation EC 1907/2006) as at 30 May 2008
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Polyphosphoric acids, esters with triethanolamine, sodium salts
- EC Number:
- 268-625-3
- EC Name:
- Polyphosphoric acids, esters with triethanolamine, sodium salts
- Cas Number:
- 68131-72-6
- Molecular formula:
- Not applicable (a generic molecular formula cannot be provided for this specific UVCB substance)
- IUPAC Name:
- Polyphosphoric acids, esters with triethanolamine, sodium salts
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS- Animals: Rat, RccHanTM: WIST(SPF)- Rationale: Recognized by international guidelines as a recommended test system.- Breeder: Harlan Laboratories, B.V., Kreuzelweg 53, 5961 NM Horst, Netherlands- Number of Animals: 40 males (10 per group), 40 females (10 per group)- Age (at Start of Treatment): 11 weeks- Body Weight Range (at Start of Treatment): Male (289 to 333 g), Females (186 to 216 g)- Identification: Cage card and individual animal number (ear tattoo). Pups: On day 1 post partum, pups were individually tattooed with Indian ink.- Randomization: Computer-generated random algorithm. In addition body weights (recorded on the day of allocation) were taken into consideration in order to ensure similar mean body weights in all groups.- Acclimatization: Under test conditions after health examination. Only animals without any visible signs of illness were used for the study.ENVIRONMENTAL CONDITIONS- Conditions: Standard laboratory conditions. Air-conditioned with 10 - 15 air changes per hour, continuously monitored environmental conditions (temp. range: 22 ± 3 °C; relative humidity range: 30 - 70%). There was 12 hour fluorescent light / 12-hour dark cycle with music during the light period.- Accommodation: Individually in Makrolon type-3 cages with wire mesh tops and sterilized standard softwood bedding (‘Lignocel’ J.Rettenmaier & Söhne GmbH & CoKG, 73494 Rosenberg / Germany, imported by Provimi Kliba SA, 4303 Kaiseraugst / Switzerland) with paper enrichment (Enviro-dri from Lillico, Biotechnology, Surrey, UK and ISO-BLOX from Harlan Laboratories B.V., Netherlands), batch/lot nos. 02105110601, 72 and 100099. During the pre-pairing period, cages with males were interspersed amongst those holding females to promote the development of regular estrus cycles.- Diet: Pelleted standard Harlan Teklad 2018C (batch no. 28/11) rodent maintenance diet (Provimi Kliba SA, 4303 Kaiseraugst / Switzerland) was available ad libitum.- Water: Community tap-water from Füllinsdorf was available ad libitum in water bottles.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- DOSE FORMULATIONSThe dose formulations were prepared weekly using the test item as supplied by the Sponsor.Polyphosphoric acids, esters with triethanolamine, sodium salts was weighed into a glass beaker on a tared precision balance and approximately 80% of the vehicle was added (w/v). Using a magnetic stirrer, a homogeneous suspension was prepared. Having obtained a homogeneous mixture, the remaining vehicle was added. Separate formulations were prepared for each concentration. Each formulation was divided in daily aliquots.Homogeneity of the test item in the vehicle was maintained during the daily administration period using a magnetic stirrer.STORAGE OF DOSE FORMULATIONSDose formulations were stored at room temperature (20 ± 5 °C) in glass beakers.TREATMENT- Method: Oral, by gavage- Rationale for Method: Administration by gavage is a common and accepted route of exposure for this type studies.- Frequency of Administration: Once daily- Target Dose Levels: Group 1: 0 mg/kg/day (control group), Group 2: 100 mg/kg/day, Group 3: 500 mg/kg/day, Group 4: 1000 mg/kg/day- Rationale for Dose Level Selection: The dose levels were selected based on a previous dose range-finding toxicity study in Han Wistar rats, using dose levels of 0, 100, 300 and 1000 mg/kg/day.- Dose Volume: 10 mL/kg body weight (daily adjusted to the actual body weight of individual animal)- Duration of Acclimatization Period: 6 days- Duration of Treatment Period: Males (28 days), females (approximately 6 weeks)
- Details on mating procedure:
- MATING, GESTATION AND LACTATIONDuring the pairing period, females were housed with sexually mature males (1:1) until evidence of copulation was observed. The females were removed and housed individually if:- the daily vaginal smear was sperm positive, or- a copulation plug was observed.The day on which a positive mating was determined (copulation plug or sperm) was designated day 0 post coitum.All dams were allowed to give birth and rear their litters (F1 pups) up to day 4 post partum. Day 0 was designated as the day on which a female had delivered all her pups.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- ANALYSIS OF DOSE FORMULATIONSOn the first treatment day samples from the control group as well as three samples (top, middle and bottom) of about 2 g of each concentration were taken prior to dosing for analysis of concentration and homogeneity. To confirm the stability (7 days) samples of about 2 g of each concentration were taken from the middle only of each aliquot used on the first treatment day. During the last week of the treatment, samples were taken from the middle to confirm concentration. The aliquots for analysis of dose formulations were frozen (-20 ± 5 °C) and delivered on dry ice to Analytical Department (Harlan Laboratories Ltd., Itingen / Switzerland) and stored there at -20 ± 5 °C until analysis.The samples were analyzed by their free content of phosphate using ion chromatography coupled to a conductivity detector following an analytical procedure developed by Harlan Laboratories. The test item was used as the analytical standard. The phosphate peak in polyphosphoric acids, esters with triethanolamine, sodium salts was assigned in sample chromatograms by comparison to that of working standards. In blank sample chromatograms no peak appeared at the retention time of phosphate in polyphosphoric acids, esters with triethanolamine, sodium salts and, therefore, the absence of the test item in the vehicle control samples (purified water) was confirmed.The application formulations investigated during the study were found to comprise polyphosphoric acids, esters with triethanolamine, sodium salts in the range of 90.1% to 100.3% and, thus, the required content limit of ±20% with reference to the nominal content was met. The homogeneous distribution of polyphosphoric acids, esters with triethanolamine, sodium salts in the preparations was approved because single results found did not deviate more than 1.7% (<15%) from the corresponding mean.In addition, the test item was found to be stable in application formulations when kept seven days at room temperature due to recoveries which met the variation limit of 10% from the time-zero (homogeneity) mean.In conclusion, the results indicate the accurate use of the test item polyphosphoric acids, esters with triethanolamine, sodium salts and purified water as vehicle during this study. Application formulations were found to be homogeneously prepared and sufficient formulation stability under storage conditions was approved.
- Duration of treatment / exposure:
- - Males: 28 days- Females: Approximately 6 weeks
- Frequency of treatment:
- - Once daily
- Details on study schedule:
- MALES- Acclimatization: 5 days minimum- First Test Item Administration: Day 1 of pre-pairing- Pre-Pairing: 14 days- Pairing: 14 days maximum- Treatment Ends: On day before sacrifice- Necropsy: After treatment for 28 days, when no longer needed for assessment of reproductive effectsFEMALES- Acclimatization: 5 days minimum- First Test Item Administration: Day 1 of pre-pairing- Pre-Pairing: 14 days- Pairing: 14 days maximum- Gestation: Approximately 21 days- Treatment Ends: On day 4 post partum- Necropsy: On day 5 post partum (pups on day 4 post partum)
Doses / concentrationsopen allclose all
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Remarks:
- active ingredient
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Remarks:
- active ingredient
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Remarks:
- active ingredient
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Positive control:
- not required
Examinations
- Parental animals: Observations and examinations:
- VIABILITY/MORTALITY- Twice dailyCLINICAL SIGNS AND OBSERVATIONSDaily cage-side clinical observation was performed once daily during acclimatization period. Thereafter, up to the necropsy, daily clinical observation was performed immediately before dosing, up to 30 minutes post-dosing and one hour after dosing. An additional observation was made five hours after dosing during the normal working week. Additionally females were observed for signs of difficult or prolonged parturition, and behavioral abnormalities in nesting and nursing.FOOD CONSUMPTION- Males (weekly during pre-pairing period and days 1 - 5 and 5 - 9 during after pairing period).- Females (pre-pairing period days 1 - 8 and 8 - 14; gestation days 0 - 7, 7 - 14 and 14 - 21 post coitum, and days 1 - 4 post partum). No food consumption was recorded during the pairing period.WATER CONSUMPTION- Monitored daily by visual inspection of water bottles. BODY WEIGHTS- Recorded daily from treatment start to day of necropsy.DETAILED CLINICAL OBSERVATIONSDetailed clinical observations were performed outside the home cage in all P generation animals. In all males of P generation it was performed once prior to the first administration of the test item and weekly thereafter. In females of P generation, it was prepared once prior to the first administration of the test item, weekly during the pre-pairing and pairing periods and on days 0, 6, 13 and 20 of the gestation period.Animals were observed for the following: changes in skin, fur, eyes, mucous membranes, occurrence of secretions and excretions, and autonomic activity (e.g. lacrimation, piloerection, pupil size, unusual respiratory pattern), changes in gait, posture and response to handling as well as the presence of clonic or tonic movements, stereotypies or bizarre behavior. FUNCTIONAL OBSERVATION BATTERYAt one time during the study (males shortly before the scheduled sacrifice and females on day 3 or 4 post partum) relevant parameters were performed with five P generation males and five P generation females from each group. This FOB assessment was conducted following the daily dose administration. Animals were observed for the following:- Cage-side observations: Faeces-balls, urine and posture as well as resistance to removal.- Hand-held observations: Muscle tone, constituation, skin, pupile size, palpebral closure, lacrimation, salivation, reaction to handling and general abnormalities.- Open field observations: Level of ambulatory activity including rearing (one minute evaluation), unusual body movements (e.g. spasms, convulsions), gait evaluation, behavior, hair coat, respiration, quantity of faeces-balls and urine.- Reflexes: Blinking, palpebral closure, pinna reflex, extensor thrust response, paw pinch, responsiveness to sharp noise, righting reflex and hearing ability (Preyer’s reflex).- Measurements / Counts: Hind limb / fore limb grip strength, landing foot splay, rectal temperature.Any abnormal findings were recorded and, where appropriate, graded in severity. Additionally, locomotor activity was measured quantitatively for the same animals. Activity was measured with an Activity Monitor AMS-0151 (FMI, Germany). Activity of the animals (based on beam count) was recorded for 6-minute intervals over a period of 30 minutes. These data and the total activity over 30 minutes were reported.CLINICAL LABORATORY INVESTIGATIONSBlood samples were obtained on the day before or on the day of the scheduled necropsy from 5 males from each group. Blood samples from 5 lactating females from each group were obtained on day 5 post partum. Blood samples were drawn sublingually from all animals under light isoflurane anesthesia. The animals were fasted for approximately 17.5 hours before blood sampling but allowed access to water ad libitum. The samples were collected early in the working day to reduce biological variation caused by circadian rhythms.HEMATOLOGYThe following hematology parameters were setermined:Complete Blood Cell Count:- Erythrocyte count- Hemoglobin- Hematocrit- Mean corpuscular volume- Red cell volume distribution width- Mean corpuscular hemoglobin- Mean corpuscular hemoglobin concentration- Hemoglobin concentration distribution width- Leukocyte count, total- Differential leukocyte count:- Platelet countCoagulation:- Prothrombin time (= Thromboplastin time)- Activated partial Thromboplastin timeCLINICAL BIOCHEMISTRYThe following clinical biochemistry parameters were determined:- Glucose - Urea - Creatinine - Bilirubin, total - Cholesterol, total- Triglycerides - Aspartate aminotransferase - Alanine aminotransferase - Alkaline phosphatase- Gamma-glutamyl-transferase - Bile acids- Sodium - Potassium - Chloride - Calcium - Phosphorus - Protein, total- Albumin- Globulin- Albumin/Globulin ratio
- Oestrous cyclicity (parental animals):
- No data
- Sperm parameters (parental animals):
- During histopathology examination, special emphasis was made on the stages of spermatogenesis and histopathology of interstitial cell structure.
- Litter observations:
- The litters were examined for litter size, live births, still births and any gross anomalies. The sex ratio of the pups was recorded. Pups were weighed individually (without identification) on days 0 (if possible) and (with identification) on days 1 and 4 post partum. In addition a surface righting assessment was performed on day 1 post partum.
- Postmortem examinations (parental animals):
- TERMINATION AND NECROPSYMales were sacrificed after treatment for 28 days, when no longer needed for the assessment of reproductive effects. Dams were sacrificed on day 5 post partum. If birth did not occur on the expected date (day 21 post coitum), the dam was sacrificed on day 25 post coitum. All parent animals sacrificed were subjected to a detailed macroscopic examination. Specimens of abnormal tissue were fixed in neutral phosphate buffered 4% formaldehyde solution. At the scheduled sacrifice, all parent animals were sacrificed by an injection of sodium pentobarbital. All P generation animals were exsanguinated. All parent animals were examined macroscopically for any structural changes.For the parent animals, special attention was directed at the organs of the reproductive system.The number of implantation sites and corpora lutea was recorded for all dams with litters. The uteri of non-pregnant females were placed in a solution of ammonium sulfide to visualize possible hemorrhagic areas of implantation sites.ORGAN WEIGHTSAt the scheduled sacrifice following organs were trimmed from any adherent tissue, as appropriate, and their wet weight taken of all parental males:- Testes (as pairs)- Epididymides (as pairs)- Seminal vesicles (as pairs)- ProstateOf all parental females:- Ovaries (as pairs)- Uterus and CervixOf all parental males and females: - Adrenal glands (weighed as pairs)- Brain - Heart- Kidneys (weighed as pairs)- Liver- Pituitary - Thymus- Spleen- ThyroidTISSUE PRESERVATIONTissues from the following reproductive organs from all parental males were preserved in neutral phosphate buffered 4% formaldehyde solution (or in Bouin’s fixative, if indicated):- Prostate- Seminal vesicles with coagulating gland - Testes (in Bouin’s fixative)- Epididymides (in Bouin’s fixative) Tissues from the following reproductive organs from all parental females were preserved in neutral phosphate buffered 4% formaldehyde solution:- Ovaries - Uterus- Vagina- CervixIn addition, from all males and females at scheduled necropsy and from all animals found dead or killed in extremis, the following tissues were preserved in neutral phosphate buffered 4% formaldehyde solution:- Gross lesions- Brain (including cerebrum, cerebellum and pons)- Spinal cord (cervical, mid-thoracic and lumbar)- Small and large intestines (incl. Peyer’s patches)- Stomach- Liver - Kidneys- Adrenals- Spleen- Heart- Thymus- Thyroids, and parathyroids if possible- Trachea and lungs (preserved by inflation with fixative and then immersion)- Urinary bladder- Lymph nodes (mesenterial, mandibular)- Peripheral nerve (sciatic)- Aorta (thoratic)- Bone and bone marrow (femur including stifle joint)- Bone and bone marrow (sternum)- Muscle (skeletal)- Oesophagus - Pancreas- Pituitary- Salivary glands (submaxillary / mandibular)- Skin (abdominal region)- Eyes ( fixed in Davidson's fluid)- Mammary tissueHISTOTECHNIQUEAll organ and tissue samples to be examined by the principal investigator for histopathology phase were processed, embedded and cut at an approximate thickness of 2 - 4 micrometers and stained with hematoxylin and eosin. Additionally, the testis were stained by PAS-hematoxylin. Special stains were used at the discretion of the principal investigator.HISTOPATHOLOGYSlides of all organs and tissues collected at terminal sacrifice from the first five males and first five females which gave birth and slides of all reproductive organs from all males and females of the control and high-dose groups were examined by the study pathologist. The same applied to all occurring gross lesions, to all animals, which died spontaneously or had to be terminated in extremis and to all unfertile animals. Special emphasis was made on the stages of spermatogenesis and histopathology of interstitial cell structure.Histological examination of ovaries was carried out on any females that did not give birth. In addition, microscopic examination of the reproductive organs of all infertile males was made. A histopathology peer review was performed a principal investigator (AnaPath GmbH).
- Postmortem examinations (offspring):
- TERMINATION AND NECROPSYPups were sacrificed on day 4 post partum.All pups sacrificed were subjected to a detailed macroscopic examination. Specimens of abnormal tissue were fixed in neutral phosphate buffered 4% formaldehyde solution. At the scheduled sacrifice, all pups were sacrificed by an injection of sodium pentobarbital.Dead pups, except those excessively cannibalized, were examined macroscopically. All pups were examined macroscopically for any structural changes, either at the scheduled necropsy or during the study if death occurred.
- Statistics:
- The following statistical methods were used to analyze functional observational battery, locomotor activity, food consumption, body weights, reproduction data, clinical laboratory investigations, organ weight and ratios and incidence and severity of histopathological findings:- Means and standard deviations of various data were calculated and included in the report.- The Dunnett-test (many to one t-test) based on a pooled variance estimate was applied if the variables could be assumed to follow a normal distribution for the comparison of the treated groups and the control groups for each sex.- The Steel-test (many-one rank test) was applied instead of the Dunnett-test when the data could not be assumed to follow a normal distribution.- Fisher's exact-test was applied if the variables could be dichotomized without loss of information.
- Reproductive indices:
- From the on-line recorded reproduction data, the following parameters were calculated: fertility indices, mean precoital time, pre- and post-implantation losses, mean litter size.
- Offspring viability indices:
- From the on-line recorded reproduction data, the following parameters were calculated: dead/live pups at first litter check, pup sex rations and postnatal losses (up to day 4 post partum).
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- 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):
- no effects observed
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Incidentally, statistically significantly lower value of hemoglobin concentration distribution width (HDW) was noted in males at the dose level of 1000 mg/kg bw/day; mean value at the high dose level was 1.56 compared to 1.72 in the control group. The value at the high dose level was within the 95% of a tolerance limit for the historical controls (a range from 1.55 to 2.14) and therefore the difference was considered not to be test item-related.
- Clinical biochemistry findings:
- no effects observed
- Behaviour (functional findings):
- effects observed, non-treatment-related
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Histopathological findings: non-neoplastic:
- no effects observed
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- no effects observed
- Reproductive performance:
- no effects observed
Details on results (P0)
Effect levels (P0)
open allclose all
- Key result
- Dose descriptor:
- NOEL
- Remarks:
- for reproduction and development
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- act. ingr.
- Sex:
- male/female
- Basis for effect level:
- other: No effect of treatment was detected on reproduction or offspring development, at a treatment level up to 1000 mg/kg/day, the highest dose level used.
- Key result
- Dose descriptor:
- NOEL
- Remarks:
- for general toxicity
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- act. ingr.
- Sex:
- male/female
- Basis for effect level:
- other: No signs of general toxicity in males or females and was observed up to 1000 mg/kg bw day, the highest dose level used.
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- no effects observed
- Mortality / viability:
- mortality observed, non-treatment-related
- Body weight and weight changes:
- no effects observed
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- not examined
Details on results (F1)
Effect levels (F1)
- Key result
- Dose descriptor:
- NOEL
- Remarks:
- for development to day 4 post partum
- Generation:
- F1
- Effect level:
- ca. 1 000 other: mg/kg bw/day received by parental animals. Offspring were not treated.
- Based on:
- other: act. ingr received by parent animals
- Sex:
- male/female
- Basis for effect level:
- viability
- clinical signs
- mortality
- body weight and weight gain
- gross pathology
- Remarks on result:
- other: No test item-related findings were noted in pups to day 4 post partum
Overall reproductive toxicity
- Key result
- Reproductive effects observed:
- no
Any other information on results incl. tables
SUMMARY OF PERFORMANCE
P Animals Breeding for F1 Litters
Group (mg/kg/day) | 1 (0) | 2 (100) | 3 (500) | 4 (1000) |
Female numbers | 41-50 | 51-60 | 61-70 | 71-80 |
Number of females paired | 10 | 10 | 10 | 10 |
Number of females mated | 10 | 10 | 10 | 10 |
Numbers of females, which were not pregnant (A) | 1 | 3 | 0 | 2 |
Number of females which reared their pups until day 4 post partum | 9 | 7 | 10 | 8 |
(A)Female nos. 43, 51, 57, 60, 77 and 72.
Applicant's summary and conclusion
- Conclusions:
- This study is a valid investigation of the toxicological effects resulting from repeated oral-gavage administration of the test item polyphosphoric acids, esters with triethanolamine, sodium salts to rats over approximately 28 days. Polyphosphoric acids, esters with triethanolamine, sodium salts was administered in highly purified water as vehicle at dosages of 100, 500, and 1000 mg/kg body weight/day, and controls received the vehicle only. Polyphosphoric acids, esters with triethanolamine, sodium salts was administered to male rats for 28 days and to female rats for 14 days prior to pairing, through the pairing and gestation periods until the F1 generation reached day 4 post partum. Reproduction and development were not affected by the treatment. Mating performance, fertility, duration of gestation, corpora lutea count, implantation rate, post implantation and postnatal loss or litter size were similar in the control and all dose groups. There were no test item-related findings in pups noted during the first litter check, the first 4 days post partum or during the necropsy, pups body weights and body weight gain were not affected at any dose level.Based on the results of this study, the NOEL (No Observed Effect Level) for general toxicity in males and females and for reproduction/developmental toxicity was considered to be 1000 mg/kg bw/day, the highest dose level used.
- Executive summary:
The purpose of this study was to generate information concerning the effects of polyphosphoric acids, esters with triethanolamine, sodium salts on the possible health hazards likely to arise from repeated exposure over a relatively limited period of time. In addition it provides information on possible effects on male and female reproductive performance such as gonadal function, mating behavior, conception, development of the conceptus and parturition.
Polyphosphoric acids, esters with triethanolamine, sodium salts was administered to male rats for 28 days and to female rats for 14 days prior to pairing, through the pairing and gestation periods until the F1 generation reached day 4 post partum, for a period of approximately of 6 weeks.
The following dose levels were applied:
Group 1: 0 mg/kg body weight/day (control group)
Group 2: 100 mg/kg body weight/day
Group 3: 500 mg/kg body weight/day
Group 4: 1000 mg/kg body weight/day
A standard dose volume of 10 mL/kg body weight with a daily adjustment to the actual body weight was used. Control animals were dosed with the vehicle alone (highly purified water).
The following results were obtained:
PARENTAL ANIMALS
Mortality and General Tolerability
All animals survived the scheduled study period.
No test item-related effects were noted during daily clinical or detailed weekly clinical observations in males or females at any dose level.
Functional Observational Battery
No test item-related effects were noted during functional observational battery in males or females at any dose level.
Food Consumption
No effects on food consumption of males or females were observed at any dose level.
Body Weights
No effects on body weights or body weight gain of males or females were observed at any dose level.
Clinical Laboratory Investigations
No test item-related effects on hematology or clinical biochemistry parameters were noted in males or females at any dose level.
Reproduction and Breeding Data
No test item-related effect on mating performance, fertility, duration of gestation, corpora lutea count, implantation rate, post implantation and postnatal loss or litter size were observed at any dose level.
Organ Weights
No test item-related effects on absolute organ weights or organ weights relative to body or brain weights were noted in males or females at any dose level.
Macroscopical Findings and Histopathological Examinations
No test item-related findings were noted during necropsy of males or females at any dose level.
During histological examination, no evidence of toxicological properties in the organs and tissues examined was found. No test item-related histological findings were recorded in ovaries of females that did not give birth or in the reproductive organs of infertile males. During the sperm staging no differences on the completeness of stages or cell populations of the testes were recorded between controls and high dose animals were found.
LITTERDATA- F1 PUPS
Findings at First Litter Check and during Lactation
No test item-related findings were noted at first litter check or during the first 4 days post partum in pups at any dose level.
No effects on righting reflex were observed in pups at any dose level.
Pups sex ratio was not affected by exposure to the test item at any dose level.
Pup Weights to Day 4 Post Partum
No effects on pups body weights or body weight gain were noted at any dose level.
Macroscopical Findings
No findings were noted during the necropsy of pups at any dose level.
Conclusion
Based on the results of this study, the NOEL (No Observed Effect Level) for general toxicity in males and females and for reproduction/developmental toxicity was considered to be 1000 mg/kg bw day, the highest dose level used.
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