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EC number: 439-840-1 | CAS number: 20846-91-7
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 26 to 29 April 1995
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP study, similar to guidelines, with acceptable deviations; on related material
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
- Objective of study:
- absorption
- distribution
- excretion
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- yes
- Remarks:
- only one low dose used
- GLP compliance:
- yes
Test material
- Reference substance name:
- Trisodium EDDS
- IUPAC Name:
- Trisodium EDDS
- Reference substance name:
- l-aspartic acid, N,N'-1,2-ethanediylbis-, trisodium salt
- IUPAC Name:
- l-aspartic acid, N,N'-1,2-ethanediylbis-, trisodium salt
- Reference substance name:
- 178949-82-1
- EC Number:
- 605-842-8
- Cas Number:
- 178949-82-1
- IUPAC Name:
- 178949-82-1
- Reference substance name:
- -
- EC Number:
- 416-530-4
- EC Name:
- -
- IUPAC Name:
- 416-530-4
- Details on test material:
- - Name of test material (as cited in study report): radiolabelled-trisodium EDDS
- Molecular formula (if other than submission substance): C10-H13-N2-O8. 3Na
- Molecular weight (if other than submission substance): 358
- Smiles notation (if other than submission substance): [Na+].[Na+].[Na+].OC(=O)[C@H](CC([O-])=O)NCCNC(CC([O-])=O)C([O-])=O
- Substance type: technical product
- Physical state: clear liquid
- Radiochemical purity (if radiolabelling): 98.7%
- Specific activity (if radiolabelling): 16.1 uCi/mg
- Locations of the label (if radiolabelling): 14C
- Expiration date of radiochemical substance (if radiolabelling): 9 September 1993
- Stability under test conditions: no data
- Storage condition of test material: at about 4oC
Constituent 1
Constituent 2
Constituent 3
Constituent 4
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- other: Crl: (WI)BR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Canada, St-Constant, Quebec
- Age at study initiation: 6-8 weeks
- Weight at study initiation: males: 191-303 g; females 173-253 g
- Fasting period before study: no data
- Housing: in glass metabolism cages
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): conventional, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 3
- Humidity (%): 50 +/- 20
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 26 April 1993 To: 29 April 1993
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: dosing solution pre-prepared at the appropriate concentration by the sponsor
HOMOGENEITY AND STABILITY OF TEST MATERIAL: no data - Duration and frequency of treatment / exposure:
- single exposure
Doses / concentrations
- Remarks:
- Doses / Concentrations:
gavaged with 1 mL to give about 10 uCi/rat and 0.5 mg/rat (about 3 mg/kg bw) of 14C-[S,S]-EDDS trisodium salt
- No. of animals per sex per dose / concentration:
- 5/sex
- Control animals:
- no
- Positive control reference chemical:
- none
- Details on study design:
- - Dose selection rationale: selected to provide sufficient material to determine the distribution, elimination and mass balance of radioactivity
- Rationale for animal assignment (if not random): random - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, blood, plasma, cage washes, expired air, adipose tissue, brain, bone marrow (femur), femur bone, gonads, heart, GI (combined stomach, large and small intestine), GI contents, kidneys, liver, lungs, muscle (right leg adductor), pancreas, spleen, carcass
- Time and frequency of sampling: urine, faeces and cage washes were collected at 24, 48 and 72 h; expired air was trapped in potassium hydroxide and collected at 12, 24, 36, 48 and 72 h. Tissues and organs were sampled for radioactivity at study termination at 72 h.
- Statistics:
- Bartlett's test and t-tests were used to determine any gender differences in the recovery of radioactivity. A ln-transformation on the percent of dose was used to correct the non-homogeneity of the variances when appropriate.
Results and discussion
- Preliminary studies:
- none
Main ADME resultsopen allclose all
- Type:
- absorption
- Results:
- after 72 h, at least 5% of the dose was considered absorbed
- Type:
- distribution
- Results:
- after 72 h, a total of about 0.15% of the dose was recovered in the blood and organs (including carcass)
- Type:
- excretion
- Results:
- after 72 h, about 75% of the dose was excreted in the faeces, and about 2 and 3% in the urine and expired air, respectively
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Only about 5% of the dose was absorbed from the gastrointestinal tract as shown by the radioactivity recovered from urine, expired air and recovered in the tissues during the 72 h exposure period. The cage wash may have contained some further absorbed material (excreted as urine). See Tables 1 and 2 for further details.
- Details on distribution in tissues:
- The total radioactivity recovered from the organs and tissues examined are given in Table 1. The combined mean radioactivity content of blood and tissues (including carcass) was 0.136 and 0.153% in males and females, respectively.
- Details on excretion:
- Radioactivity was excreted mainly in the faeces and occurred rapidly with about 62% and 71% of the dose being recovered in faeces in males and females, respectively, during the first 24 h. In total, during the 72-h collection period, faecal excretion accounted for about 75% of the administered dose in males and females. Only a small fraction of the dose was recovered in the urine (about 1.7%) and expired air (3.25%). See Tables 1 and 2 for further details.
Metabolite characterisation studies
- Metabolites identified:
- not measured
Any other information on results incl. tables
Table 1. Total recovery (mass balance) of radioactivity in excreta and tissues
Sample | Males (% of dose) | Females (% of dose) |
Urine | 1.87 ± 1.58 | 1.49 ± 0.200 |
Faeces | 75.6 ± 6.91 |
75.2 ± 7.92 |
Expired air | 3.35 ± 2.21 | 3.19 ± 0.803 |
Cage wash | 3.37 ± 2.86 | 9.38 ± 7.55 |
Blood | 0.0041 ± 0.0093 | 0.000 ± 0.000 |
Liver | 0.0424 ± 0.0353 | 0.037 ± 0.014 |
Kidneys | 0.0092 ± 0.0084 | 0.004 ± 0.001 |
Heart | 0.0003 ± 0.0008 | 0.000 ± 0.001 |
Lungs | 0.0007 ± 0.0015 | 0.000 ± 0.000 |
Pancreas | 0.0007 ± 0.0016 | 0.001 ± 0.002 |
Spleen | 0.005 ± 0.0011 | 0.001 ± 0.002 |
Brain | 0.0015 ± 0.0034 | 0.000 ± 0.000 |
Testes/ovaries | 0.0010 ± 0.0023 | 0.000 ± 0.000 |
Muscle | 0.0000 ± 0.0000 | 0.000 ± 0.000 |
Adipose tissue | 0.0283 ± 0.0127 | 0.017 ± 0.026 |
Bone marrow | 0.0000 ± 0.0000 | 0.000 ± 0.000 |
Bone femur | 0.0000 ± 0.0000 | 0.000 ± 0.000 |
GI tract | 0.0358 ± 0.0478 | 0.013 ± 0.012 |
GI contents | 0.0345 ± 0.0771 | 0.000 ± 0.000 |
Carcass | 0.114 ± 0.141 | 0.080 ± 0.083 |
Total | 84.4 ± 1.52 | 89.5 ± 2.76 |
Table 2. Percentage recovery of radioactivity in excreta
|
% of dose |
Cumulative % of dose |
||||||||
Period (h) |
Urine |
Faeces |
Cage wash |
Expired air |
Total |
Urine |
Faeces |
Cage wash |
Expired air |
Total |
Males |
|
|
|
|
|
|
|
|
|
|
0-12 |
a |
a |
a |
1.2228 ± 0.2709 |
1.2228 ± 0.2709 |
a |
a |
a |
1.2228 ± 0.2709 |
1.2228 ± 0.2709 |
12-24 |
1.3003 ± 0.4784 |
62.2836 ± 26.9438 |
2.2841 ± 2.1168 |
0.7793 ± 0.3835 |
66.6474 ± 26.2117 |
1.3003 ± 0.4784 |
62.2836 ± 26.9438 |
2.2841 ± 2.1168 |
2.0021 ± 0.1764 |
67.8702 ± 26.3440 |
24-36 |
a |
a |
a |
0.6048 ± 0.8138 |
0.6048 ± 0.8138 |
1.3003 ± 0.4784 |
62.2836 ± 26.9438 |
2.2841 ± 2.1168 |
2.6069 ± 0.9824 |
68.4750 ± 25.5306 |
36-48 |
0.4169 ± 0.8032 |
8.7869 ± 11.8536 |
0.4881 ± 0.6665 |
0.4913 ± 0.7762 |
10.2732 ± 13.9894 |
1.7173 ± 1.2524 |
71.1606 ± 15.3503 |
2.7722 ± 2.4431 |
3.0982 ± 1.7566 |
78.7482 ± 12.0645 |
48-72 |
0.1532 ± 0.3335 |
4.3958 ± 8.6421 |
0.5985 ± 1.3383 |
0.2484 ± 0.4581 |
5.3959 ± 10.7689 |
1.8705 ± 1.5803 |
75.5564 ± 6.9090 |
3.3707 ± 2.8555 |
3.3466 ± 2.2133 |
84.1441 ± 1.7590 |
Females |
|
|
|
|
|
|
|
|
|
|
0-12 |
a |
a |
a |
1.1357 ± 0.1808 |
1.1357 ± 0.1808 |
a |
a |
a |
1.1357 ± 0.1808 |
1.1357 ± 0.1808 |
12-24 |
1.2509 ± 0.1869 |
70.6335 ± 5.9226 |
9.0715 ± 7.3306 |
1.4762 ± 0.4461 |
82.4320 ± 3.5779 |
1.2509 ± 0.1869 |
70.6335 ± 5.9226 |
9.0715 ± 7.3306 |
2.6119 ± 0.5366 |
83.5677 ± 3.6176 |
24-36 |
a |
a |
a |
0.3144 ± 0.1596 |
0.3144 ± 0.1596 |
1.2509 ± 0.1869 |
70.6335 ± 5.9226 |
9.0715 ± 7.3306 |
2.9263 ± 0.6461 |
83.8821 ± 3.5258 |
36-48 |
0.2609 ± 0.2946 |
3.9687 ± 3.8809 |
0.2423 ± 0.3216 |
0.2029 ± 0.1229 |
4.6226 ± 3.8030 |
1.4596 ± 0.1392 |
74.6022 ± 7.7342 |
9.3138 ± 7.5307 |
3.1292 ± 0.7494 |
88.5047 ± 2.7321 |
48-72 |
0.0289 ± 0.0647 |
0.6468 ± 0.2785 |
0.0622 ± 0.0956 |
0.0614 ± 0.0666 |
0.7993 ± 0.3595 |
1.4885 ± 0.2003 |
75.2490 ± 7.9168 |
9.3760 ± 7.5495 |
3.1906 ± 0.8025 |
89.3041 ± 2.7273 |
a: not sampled
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
In a GLP study, similar to OECD Guideline 417, a single dose of radiolabelled trisodium EDDS (about 2-3 mg/kg bw/day) administered by gavage to male and female rats was rapidly eliminated, mainly in the faeces (about 75% of the administered dose), with at least 5% considered absorbed from the gastrointestinal tract. - Executive summary:
In a GLP study conducted according to a protocol similar to OECD Guideline 417, the absorption, distribution and elimination of 14C-labelled trisodium EDDS was determined in male and female Wistar rats. The radiolabelled test substance was administered by single oral gavage (in water) to five rats of each sex at a dose level of 0.5 mg/rat (about 2-3 mg/kg bw) and the animals placed in individual metabolism cages. Urine, faeces and cage washes were collected at 24, 48 and 72 h and expired air was collected in 12, 24, 36, 48 and 72 h samples. At study termination (72 h), blood samples were taken and plasma separated and selected tissues and gastrointestinal contents were collected and the levels of radioactivity were determined by liquid scintillation counting (after solubilising the tissues as necessary).
Trisodium EDDS was rapidly excreted, mainly in the faeces. In the first 24 h, approximately 62 and 71% of the administered dose, respectively in males and females, was excreted in the faeces, and after 72 h about 75% was excreted in the faeces. Overall, at least 5% of the test substance was absorbed from the GI tract as determined by the amount of radioactivity in urine, expired air and in the tissues. Some further absorbed material may have been found in the cage wash and possibly any faeces produced after 36 hr. The combined mean radioactivity content of blood and tissues (including carcass) was 0.136 and 0.153% of the administered dose in males and females, respectively. No statistically significant gender differences were evident in the absorption, distribution or excretion patterns.
In conclusion, at least 5% of an administered dose of trisodium EDDS was considered absorbed from the gastrointestinal tract, with most being excreted in the faeces within the first 24 h after administration.
[Data on trisodium EDDS is considered relevant to use for understanding the basic toxicokinetics of EDDS acid, and is acceptable for using as read-across information.]
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