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EC number: 205-355-7 | CAS number: 139-13-9
- 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
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- The aim of the study was to determine if this effect is reproducible and thus the test substance may have a "protective" effect on the kidney at low concentrations.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- testing lab.
Test material
- Reference substance name:
- Trilon A 92
- IUPAC Name:
- Trilon A 92
- Reference substance name:
- Trisodium nitrilotriacetate
- EC Number:
- 225-768-6
- EC Name:
- Trisodium nitrilotriacetate
- Cas Number:
- 5064-31-3
- IUPAC Name:
- trisodium 2,2',2''-nitrilotriacetate
- Details on test material:
- Trilon A 92 R; purity : 95 g / 100g
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Male Wistar rats at an age about 12 weeks. Only animals free from clinical signs of disease were used for the study. The rats were identified clearly by ear tattoo. The rats were housed singly in type DK I I I stainless steel wire mesh cages (floor area about 800 cm2) . Underneath the cages, waste trays were fixed containing absorbent material. The animals were housed in a fully air-conditioned room. Central air-conditioning guaranteed a range of 20 - 24°C for temperature and of 30 - 70% for relative humidity . The day/night rhythm was 12 hours. Deviations from these ranges did not occur. The animal room was completely disinfected using a disinfector. The floor and the walls were cleaned once a week. The cleansing liquid used was water containing about 0.1% Incidin. The food used was ground Kliba maintenance diet mouse/rat, meal. Food and drinking water (from water bo ttles) were
available ad libitum.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- The test substance was weighed out and thoroughly mixed with a small amount of food. Then corresponding amounts of food were added to this premix in order to obtain the desired concentration , and mixing was carried out for 10 minutes in a laborato ry mixer.
The mixtures were prepared weekly. No analyses of the test substance in the diet were carried out. The food used in the study was assayed for chemical and microbiological contaminants. The drinking water is regularly assayed for chemical contaminants. - Duration of treatment / exposure:
- 4 weeks
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 150 ppm
Basis:
- No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- According to previous studies with the test substance, a concentration of 150 ppm in the diet was used.
Examinations
- Observations and examinations performed and frequency:
- The animals were examined for evident signs of toxicity or mortality twice a day (in the morning and in the late afternoon) from Mondays to Fridays and once a day (in the morning) on Saturdays , Sundays and public holidays. Additionally, further general clinical examinations were carried out daily.
Food consumption was determined weekly and calculated as mean food consumption in grams per animal and day. Water consumption was determined weekly over a period of 4 days and calculated as mean food consumption in grams per animal and day.
Body weight was determined before the start of the administration period in order to randomize the animals. During the administration period the body weight was determined on day 0 (start of administration period) and thereafter at weekly intervals. The difference between the body weight on the respective day of weighing and the body weight on day 0 was calculated as body weight change. Food efficiency (group means) was calculated based upon individual values for body weight and food consumption. The mean daily intake of test substance (group means) was calculated based upon individual values for body weight and food consumption.
On the day given in the time table , the animals were transferred to metabolism cages (withdrawal of food and water) and urine was collected overnight. The urine specimens were stored at about -80°C for a possible analysis of zinc . However, on request of the sponsor, no analyses were performed.
The determination of 8-HO-deoxyguanosine was performed in the right kidney of the animals, and determination of lipid peroxidation was performed in the left kidney of the animals. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Statistics:
- Means and standard deviations of each test group were calculated for several parameters.
Results and discussion
Results of examinations
- Details on results:
- No animal died during the study.
No abnormal clinical signs were observed.
Food and water consumption, body weight data, food efficiency: No substance-related effects were obtained.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Induction of oxidative stress by Na 3NTA in kidneys was determined by measuring lipid peroxidation and 8-HO-dG. Lipid peroxidation was not affected by Na 3NTA treatment. There was, however, a statistically significant decrease in 8-HO-dG levels in kidney DNA from treated rats (35% lower than control). Although absolute levels of 8-HO-dG were rather high in this study, the effect is nevertheless considered to be biologically relevant because the data are rather consistent and were confirmed by the analysis of a second set of digested DNA-samples. These results confirm the results of a previous study (BASF Project No. 99S0061/95057) in which levels of 8-HO-dG in kidney DNA were decreased after treatment with 150 ppm Na 3NTA, too.
Applicant's summary and conclusion
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.
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