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EC number: 225-768-6 | CAS number: 5064-31-3
- 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:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 2002-06-11 to 2003-05-16
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: no guideline exists for this type of study - site participates in GLP compliance program; however, no analyses of the test substance in the food were carried out
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- 4 week feeding study in male Wistar rats at 0 and 150 ppm, focussing on kidney toxicity.
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Trisodium nitrilotriacetate
- EC Number:
- 225-768-6
- EC Name:
- Trisodium nitrilotriacetate
- Cas Number:
- 5064-31-3
- Molecular formula:
- C6H9NO6.3Na
- IUPAC Name:
- trisodium 2-[bis(carboxylatomethyl)amino]acetate
- Details on test material:
- - Name of test material (as cited in study report): Trilon A92 R; Monohydrat des Trinatriumsalzes der Nitrilotriessigsäure
- Physical state: solid white powder
- Stability under test conditions: the stability of the test substance under storage conditions over the test period was guaranteed by the sponsor and the sponsor holds this responsibility.
- Storage condition of test material: room temperature; test substance is hydroscopic
- manufacturing date: 2002-05-02
- Other: Homogeneity verified
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany
- Age at study initiation: 13 weeks
- Weight at study initiation:
- Fasting period before study: none
- Housing: individually in DKIII stainless steel wire mesh cages (floor area about 800 cm²). Underneath waste trays containing adsorbent material.
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-24 °C
- Humidity (%): 30-70%
- Air changes (per hr): fully air conditioned rooms
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 2002-06-18 To: 2002-07-17
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
DIET PREPARATION
- Rate of preparation of diet (frequency): mixtures were prepared weekly
- Mixing appropriate amounts with (Type of food): ground Kliba maintenance diet rat/mouse meal, supplied by Provimi Kliba AG, Kaiseraugst, Switzerland - Analytical verification of doses or concentrations:
- no
- Details on analytical verification of doses or concentrations:
- No analyses of the test substance in the diet were carried out
- Duration of treatment / exposure:
- 28 d
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 150 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- 10 males
- Control animals:
- yes, plain diet
- Details on study design:
- - Dose selection rationale: Previous study administered 150 ppm Na3NTA over 28-day period and determined the 8-OH-2-deoxyguanosine content in kidney to be significantly lower than in controls (BASF 99S0061/95057). The study was set up to reproduce this effect and test if the substance may have a protective effect on the kidney at low concentrations.
- Rationale for animal assignment (if not random): random
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice a day (morning and late afternoon), once a day on Saturdays, Sundays and public holidays
- Cage side observations checked in table [No.IA-001] were included.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: at start of administration period and weekly thereafter
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: No
CLINICAL CHEMISTRY: Yes
- 8-HO-deoxyguanosine was determined in the right kidney and lipid peroxidation was determined in the left kidney.
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
OTHER: BIOCHEMICAL INVESTIGATION: determination of 8-OH-2-deoxyguanosine content in the right kidney (according to Dahlhaus et al. 1993 and Fialy et al. 1989) and lipid peroxidation in the left kidney (according to Reece et al. 1998). (see table IB-001 - IIA-003) - Sacrifice and pathology:
- GROSS PATHOLOGY: No
HISTOPATHOLOGY: No - Other examinations:
- At necropsy, kidneys were weighted and 8-HO-deoxyguanosine was determined in the right kidney and lipid peroxidation was determined in the left kidney.
- Statistics:
- Mean and standard deviation of each test group were calculated for several parameters including body weight, body weight change, food consumption, water consumption, and food efficiency. A comparison of each group with the control group was performed using DUNNETT’s test (two-sided) for the hypothesis of equal means.
* for p ≤ 0.05
** for p ≤ 0.01
Dunnett C.W. (1955): A multiple comparison procedure for comparing several treatments with a control. JASA, Vol.50, 1096 - 1121
Dunnett C.W. (1964): New tables for multiple comparisons with a control. Biometrics, Vol.20, 482 - 491
Results and discussion
Results of examinations
- 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
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Lipid peroxidation and 8-HO-Deoxyguanosine level in kidney DNA
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- only kidney examined
- Gross pathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- CLINICAL SIGNS AND MORTALITY: no animal died during the study
BODY WEIGHT AND WEIGHT GAIN: no substance-related effects observed
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): no substance-related effects observed
FOOD EFFICIENCY: no substance-related effects noted
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): no substance-related effects observed
The following examinations were not performed: OPHTHALMOSCOPIC EXAMINATION, HAEMATOLOGY, CLINICAL CHEMISTRY, URINALYSIS, NEUROBEHAVIOUR, GROSS PATHOLOGY, HISTOPATHOLOGY: NON-NEOPLASTIC, HISTOPATHOLOGY: NEOPLASTIC , and HISTORICAL CONTROL DATA .
ORGAN WEIGHTS determined only on kidneys: no substance-related effects observed
OTHER FINDINGS: determination of the 8-HO-2-deoxyguanosine (8-HO-dG) content noted a statistically significant reduction in the 8-HO-dG level (by 35% in kidney DNA of rats treated with NTA).
Effect levels
- Dose descriptor:
- LOEL
- Effect level:
- 150 ppm
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: decrease of 8-HO-dG levels in kidney DNA (suggesting protective effect)
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
|
Group 0: Control |
Group 1: 150 ppm NTA |
Kidney weight |
0.9559 |
0.9939 |
Mean TBA-reactive material (MDA-equivalents) [nmol/g tissue] |
114.7 (±22.1) |
114.3 (±20.9) |
Mean 8-OH-dG-level [8 -HO-dG/105dG] |
131.2 (± 54.0) |
85.9 (±38.9) |
Applicant's summary and conclusion
- Conclusions:
- Administering 150 ppm Na3NTA over 28 days to male Wistar rats did not affect kidney weight but caused a significant decrease in the 8-HO-dG-level in kidney DNA. This is considered to be biologically relevant (oxidative stress), and confirms the analysis of a previous study (BASF, 1998 (99S0061/95057)).
- Executive summary:
In a subchronic toxicity study Na3NTA (92.4%) was administered to male Wistar rats at dietary concentrations of 150 ppm (appr. 9 mg/kg bw/d) for 4 weeks. There is no guideline for such subchronic toxicity study to assess oxidative stress in kidneys using male Wistar rats.
Subgroups of 10 animals received 0 (control group) and 150 ppm Na3NTA. Animals were examined for clinical effects, food consumption, body weight (change), and pathology of the kidneys. 8-HO-deoxyguanosine levels and lipid peroxidation in kidneys (being measured as the amount of TBA-reactive material) was determined as indicators of oxidative stress. Kidney weights and lipid peroxidation were not altered. The 8-HO-dG-level in the kidney was statistically significantly lower in treated rats than the control group. This is considered to be biologically relevant suggesting a protective effect of Na3NTA with regards to oxidative stress in the kidneys. The data confirmed the analysis of a previous study (BASF, 1998 (99S0061/95057).
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