AVIS et RAPPORT de lAnses relatif à la définition dune valeur
Selon la définition de la Commission européenne « on entend par indicateurs » (mesure des cassures de l'ADN
RISK ASSESSMENT
Aug 20 2008 In vitro tests for induction of sister chromatid exchanges (SCE) are available for trisodium nitrilotriacetic acid (Na3NTA)
TOXICOLOGICAL PROFILE FOR XYLENE
Human peripheral Sister chromatid Inhalation. –. Pap and Varga Mixed xylene lymphocytes exchange. (occupational. 1987 exposure).
stoddard solvent 9 2. health effects 2.1 introduction
spirits/ethanol dilutions and investigated for increased sister chromatid exchange. Two incubation periods were employed for each concentration: 1 hour and
RISK ASSESSMENT
Aug 20 2008 In vitro tests for induction of sister chromatid exchanges (SCE) are available for trisodium nitrilotriacetic acid (Na3NTA)
TOXICOLOGICAL PROFILE FOR DDT DDE
https://stacks.cdc.gov/view/cdc/6738/cdc_6738_DS1.pdf
I. Définition : II. Les phases du cycle cellulaire : Le cycle cellulaire
I. Définition : Le cycle cellulaire est Définition : La mitose est un phénomène continu qui désigne : ... chromosomes donc un par chromatide).
LE BRASSAGE ALLÉLIQUE INDUIT PAR LA MÉIOSE
définition méiose (2 divisions produisant gamètes) séparation chromatides on obtient 4 sortes de spermatozoïdes haploïdes (n).
HIGHLIGHTS OF PRESCRIBING INFORMATION These highlights
vivo sister chromatid exchange assay in Chinese hamster bone marrow cells. Impairment of Fertility — Two fertility studies conducted in adult rats at doses
SCIENTIFIC OPINION Draft guidance on aneugenicity assessment
chromatid attachment and separation tubulin
What is a chromatide in biology?
D finition simple: Une chromatide est une copie d'un chromosome nouvellement copi qui est encore joint la copie originale par un centrom re unique. Le chromosome est la structure fibreuse dans la phase primaire de condensation de l'ADN. En m taphase d'une division cellulaire (mitose ou m iose), ils s'appellent les chromatides.
What are Deux chromatides?
Deux chromatides assemblées au niveau du centromère forme un chromosome, avec un enjambement. Les chromatides sont visibles en prophase de la mitose et représentent les chromosomes pré-filles. L'ensemble de deux chromatides devient un chromosome mitotique visible pendant la prophase, la métaphase, la télophase et l'anaphase.
Is a chromatid a single chromosome?
For that reason, while the “sister chromatids” are attached to each other, they are considered to each be one half of a single chromosome. Once they are separated during anaphase, each chromatid is considered to be a chromosome of its own, just like the original chromosome that they are copied from.
What is a sister chromatid?
Chromatids may be sister or non-sister chromatids. A sister chromatid is either one of the two chromatids of the same chromosome joined together by a common centromere. A pair of sister chromatids is called a dyad.
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RISK ASSESSMENT
Trisodium Nitrilotriacetate
CAS-No.: 5064-31-3
EINECS-No.: 225-768-6
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1R307_0808_hh_env.doc
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Information on the rapporteur
Contact point:
Bundesanstalt für Arbeitsschutz und Arbeitsmedizin (BAuA)Chemikalien, Anmeldung und Zulassung
Federal Institute for Occupational Safety and HealthDivision for Chemicals and Biocides Regulation
Friedrich-Henkel-Weg 1-25
44149 Dortmund
fax: +49-(0)231-9071-2679 e-mail: chemg@baua.bund.de The first draft of the Human Health Section of the Comprehensive Risk Assessment Report Trisodium Nitrilotriacetate (NTA), a substance chosen from the EU 3rd Priority List in 1995, which is distributed for the preliminary written procedure was distributed to MS for preliminary comments in October 2006. This document is the revised draft of the Human Health Section of the RAR of NTA which is intended to be discussed in-depth at the TC NES II´07.R307_0808_hh_env.doc
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2Contents
0 OVERALL CONCLUSIONS/RESULTS OF THE RISK ASSESSMENT 4 1GENERAL SUBSTANCE INFORMATION 7
2GENERAL INFORMATION ON EXPOSURE 11
2.1Production, Import and Export 11
2.2 Processing / Application (Categories of use, Amounts) 11 2.3Use Pattern 13
3ENVIRONMENT 14
3.1Environmental exposure 14
3.1.1 General discussion 14
3.1.2 Aquatic compartment 24
3.1.3 Atmosphere 36
3.1.4 Terrestrial compartment 37
3.1.5 Non compartment specific exposure relevant to the food chain 37
3.2 Effects assessment: Hazard identification and Dose (concentration) - response (effect) assessment 373.2.1 Aquatic compartment 37
3.2.2 Atmosphere 54
3.2.3 Terrestrial compartment 54
3.2.4 Non compartment specific effects relevant to the food chain 55
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33.3 Risk characterisation 55
3.3.1 Aquatic compartment 55
3.3.2 Atmosphere 56
3.3.3 Terrestrial compartment 56
3.3.4 Non compartment specific effects relevant to the food chain 56
4HUMAN HEALTH 57
4.1HUMAN HEALTH (TOXICITY) 57
4.1.1 Exposure assessment 57
4.1.2 Effects assessment: Hazard identification and Dose (concentration) - response
(effect) assessment 834.1.3 Risk characterisation 167
4.2HUMAN HEALTH (PHYSICO-CHEMICAL PROPERTIES) 199
4.2.1 Exposure assessment 199
4.2.2 Effects assessment: Hazard identification and Dose (concentration) - response
(effect) assessment 1994.2.3 Risk characterisation 199
5CONCLUSIONS / RESULTS 201
6REFERENCES 203
APPENDIX 1 217
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40 OVERALL CONCLUSIONS/RESULTS OF THE RISK ASSESSMENT
CAS No. 5064-31-3
EINECS No. 225-768-6
IUPAC Name Trisodium nitrilotriacetate
Overall results of the risk assessment:
( ) i) There is need for further information and/or testing ( X ) ii) There is at present no need for further information and/or testing and for risk reduction measures beyond those which are being applied already ( X ) iii) There is a need for limiting the risks; risk reduction measures which are already being applied shall be taken into accountR307_0808_hh_env.doc
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5Summary of conclusions:
Environment
Conclusion ii) There is at present no need for further information and/or testing or for risk reduction measures beyond those which are being applied already. In the present risk assessment production and use of Na 3NTA are examined. For all life-cycle
steps, the PEC/PNEC ratios are below 1. Ther efore, a risk for the environment is not expected.Human Health
Workers
Conclusion (iii) There is a need for limiting the risks; risk reduction measures which are already being applied shall be taken into account Concern is derived for repeated dose toxicity and carcinogenicity. Especially dermal exposure (with a critical exposure level of 2.85 mg/kg/day) has to be reduced for scenario 2 (use of Na 3 NTA in formulation process) and 3 (high pressure cleaning), and inhalation exposure (with a critical exposure level of 2 mg/m 3 ) has to be reduced for scenario 1 (production of NTA) and 2b (use of Na 3NTA in formulation process without LEV).
Conclusion (ii) There is at present no need for further information and/or testing or for risk reduction measures beyond those which are being applied already. For the other toxicological endpoints the risk orientated conclusions result in no concern with the consequence that risk reduction measures are of low priority.Consumers
Conclusion (ii) There is at present no need for further information and/or testing and for risk reduction measures beyond those which are being applied alreadyR307_0808_hh_env.doc
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6Man exposed indirectly via the environment
Conclusion (ii) There is at present no need for further information and/or testing and for risk reduction measures beyond those which are being applied alreadyR307_0808_hh_env.doc
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71 GENERAL SUBSTANCE INFORMATION
Identification of the substance
CAS-No.: 5064-31-3
EINECS-No.: 225-768-6
IUPAC Name: Trisodium nitrilotriacetate
Synonyms: Nitrilotriacetic acid trisodium salt
NTA trisodium salt
CA-Index name: Glycine, N,N-bis(carboxymethyl)-, trisodium saltMolecular weight: 257.1 g/mol
Empirical formula: C6H6NNa3O6
Structural formula:
NCOONa
NaOOCNaOOC
Purity/impurities, additives
Purity: 92 % w/w
Impurities: < 7 % water
< 3 % sodium glycolate < 2 % disodium iminodi(acetate) < 2 % sodium hydroxide < 1.5 % methanamine < 1 % sodium formateAdditives: none
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8Physico-chemical properties
Trisodium nitrilotriacetate (Na
3 NTA) is a colourless crystalline powder at room temperature and normal pressure. Data on the physical and chemical properties are given in table 1.1. Table 1.1: Data on the physical and chemical properties of Na 3 NTAMelting point 410 °C with decomposition
above 200 °C BASF, 1996Boiling point not applicable
Relative density 1.77 at 20 °C
1)BASF, 1997
Vapour pressure not determined
no test conducted because of structural reasons Surface tension not determined no test conducted because of structural reasons Water solubility about 640 g/l at 20 °C Ullmann, 1991Partition coefficient -2.62 (calculated)
2)BASF, 1989
Flash point not determined substance is a solid
Flammability not highly flammable
3)BASF, 1998
Ignition temperature no selfignition up to
decomposition (200 °C) Chemsafe, 1997 Explosive properties not explosive no test conducted because of structural reasons Oxidising properties no oxidising properties no test conducted because of structural reasons 1)Relative density: pycnometer method
2) Partition coefficient: The logPow was calculated according to the Rekker method with the computer program Pro-logP (version 2.0). 3) Flammability: According to guideline 92/69/EEC test method A.10 (determination of the flammability for solids), the substance did not propagate combustion. The tests according to A.12 (determination of the flammability in contact with water) and A.13 (determination of pyrophoric properties) were not conducted. Due to the propertiesR307_0808_hh_env.doc
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9and the handling of the substance it has not to be assumed that
flammable gases formate in contact with water or the substance has pyrophoric properties.Classification
Environment
Proposal of the rapporteur (only environmental part) For the classification of biodegradation, the available laboratory tests with uncomplexed NTA should not be used, because biodegradation of this chelator is strongly dependent on the metal speciation. Studies on the degradation in biological treatment plants as well as degradation tests conducted in river water reveal that the degradation properties of NTA (resp. of its metal complexes) are comparable with a readily degradable substance. In addition the substance has no bioaccumulation potential. In tests on the acute toxicity on fish and daphnia effects were only observed when NTA was present in over-stoichiometric concentrations compared to the content of metal ions. The lowest LC50 values were 98 mg/l for both trophic levels. Results of algae growth inhibition tests have to be interpreted carefully, because the observed effects are mainly cause by nutrient deficiency, which is an artefact and not relevan t for the environment. Tests with increased concentrations of nutrient metals (where nutrient deficiency is suppressed) reveal that intrinsic toxicity of NTA is expected only at concen- trations far above 10 mg/l.Considering all results, a classification of Na
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