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EC number: 209-544-5 | CAS number: 584-84-9
- 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
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- 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
Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Accetible standard publication
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 999
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 4-methyl-m-phenylene diisocyanate
- EC Number:
- 209-544-5
- EC Name:
- 4-methyl-m-phenylene diisocyanate
- Cas Number:
- 584-84-9
- Molecular formula:
- C9H6N2O2
- IUPAC Name:
- 2,4-diisocyanato-1-methylbenzene
- Details on test material:
- - Name of test material (as cited in study report): 2,4-diisocyanatotoluene (2,4-TDI); 2,6-diisocyanatotoluene (2,6-TDI);
80:20 mixture of 2,4- and 4,6-isomers of TDI (TDI 80)
This study was carried out using mixed isomers of TDI. As mixed isomers of TDI contains generally 655 or 80% of the 2,4-TDI isomer, (the remainder being 2,6-TDI), this study can also be considered to be a valid test of 2,4-TDI. No claim is made as to the contribution or otherwise of the 2,6-TDI isomer in this assay.
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Vehicle / solvent:
- Ethyleneglycol dimethylether (EDGE), dimethylsulphoxide (DMSO)
- Details on test system and experimental conditions:
- Ames test
Results and discussion
Test results
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- positive
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity, but tested up to precipitating concentrations
- Additional information on results:
- Positive (with S9 activation) - TA 100, TA 1537 and TA 98
Negative (with S9 activation) - TA 1535
Negative (without S9 activation) - all strains
2,4-TDI, 2,6-TDI, and TDI 80, all of which were dissolved in EGDE, showed a consistently negative response in the absence of S9 mix. Furthermore, no mutagenicity was observed in any of the TA 1535 strain experiments. Clearly positive results were obtained in the other strains after metabolic activation of 2,4-TDI,2,6-TDI, and TDI 80.
The HPLC analyses of the dissolved aromatic diisocyanates indicate that their degradation is considerably accelerated if DMSO is the solvent and may be completed before the Salmonella microsome test has even begun.
2,4-TDI, 2,6-TDI and TDI 80, all of which were dissolved in EGDE, showed a consistently negative response in the absence of S9 mix. Furthermore, no mutagenicity was observed in any of the TA 1535 strain experiments. With respect to these findings, the results of the TDIs were in complete agreement with those obtained for the MDIs. In contrast to the MDIs, however, clearly positive results were obtained in the other strains after metabolic activation of 2,4-TDI, 2,6-TDI and TDI 80. The results are summarised in Tables 1-3. Consistently positive results were obtained in strain TA 98 with all types of TDI tested. In TA 1537, clearly positive results were obtained for 2,4-TDI (Table 1) and weak effects were observed for TDI 80 whereas no effects were found for 2,6-TDI (Tables 2 and 3). Weak positive results were also obtained for TDI 80 with TA 100 (Table 3). S9 mixtures with varying amounts of the S9 fraction (10 and 30%) were used for 2,4- and 2,6-TDI. The results demonstrate (Table 1 and 2) that effects are slightly reduced in the presence of the S9 mix containing 30% of the S9 fraction. This reduction of effects may be examined with a selective or at least preferred reaction of the test samples with the proteins of the S9 fraction. [See remarks on results below for Tables 1-3) - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'. Remarks: Salmonella typhimurium strains TA1535, TA 100, TA 1537 and TA 98
Any other information on results incl. tables
See Additional information on results for Tables 1 -3.
Table 1. Results with 2,4-TDI (dissolved in EGDE) and metabolic activation
Strain S9, ug/plate |
TA 1537 |
TA 98 |
||
10% S9 |
30% S9 |
10% S9 |
30% S9 |
|
0 |
19 |
12 |
54 |
39 |
50 |
18 |
16 |
64 |
52 |
100 |
23 |
16 |
104* |
76* |
200 |
44*b |
25 |
117* |
76* |
400 |
52*b |
22b |
153*b |
87*b |
600 |
51*b |
45*b |
172*b |
93*b |
800 |
49*bp |
41*b |
125*bp |
128*bp |
1000 |
41*bp |
42*bp |
117*bp |
58*bp |
AA3 |
233* |
80*bp |
1245* |
509* |
AA = 2-aminoanthracene * = mutagenic effect, b = background growth reduced, p = precipitation
Table 2. Results with 2,6-TDI (dissolved in EGDE) and metabolic activation
Strain S9, ug/plate |
TA 1537 |
TA 98 |
||
10% S9 |
30% S9 |
10% S9 |
30% S9 |
|
0 |
12 |
14 |
47 |
45 |
150 |
13 |
21 |
67 |
57 |
300 |
13 |
16 |
87* |
61 |
600 |
15 |
15p |
130* |
73* |
1200 |
7p |
10p |
166*p |
97*p |
2400 |
7p |
9p |
128*p |
82*p |
4800 |
p |
p |
p |
p |
AA 3 |
360* |
66* |
1538* |
618* |
AA = 2-aminoanthracene * = mutagenic effect, b = background growth reduced, p = precipitation
Table 3. Results with TDI 80 (dissolved in EGDE) and 10% S9 mix
Strain S9, ug/plate |
TA 100 |
TA 1537 |
TA 98 |
0 |
71 |
9 |
36 |
125 |
143 |
12 |
86* |
250 |
188* |
15 |
101* |
500 |
211*p |
21p |
123*p |
1000 |
57p |
28*bp |
88*p |
2000 |
21bp |
2bp |
23bp |
AA 3 |
869* |
306* |
888* |
Results
The stability of TDI solutions prior to salmonella /microsome tests was investigated (Table 4). The N=C=O content of 50-500 mg TDI, dissolved in 100 ml relatively 'dry' DMSO (0.02-0.03% water), dropped to 60% or less within the first 15 min of the test. Theoretically, the hydrolysis of 174 mg (1.0 mM) of TDI could consume 18 mg (1.0 mM) of water to form highly reactive intermediates, the aminoisocyanatotoluenes (TDAIs), and carbon dioxide. A homogeneous solution containing 0.02% (1.11 mM) water, as was the case for the 500 mg (2.86 mM) 2,4-TDI sample, would therefore convert about 40% of the TDI into reactive intermediates on a purely stoichiometric basis. These aminoisocyanates would then be available for further reactions with remaining 2,4-TDI or with themselves to produce a number of monomeric, oligomeric and polymeric ureas, which may be terminated by N=C=O and / or NH2 groups. At this point it is important to recall that a residual N=C=O content by no means indicates the presence of unmodified 2,4-TDI. The IR spectrum provides only insufficient information on the location of the N=C=O groups. The observed decline of isocyanate absorptions is, however, proof of the fact that chemical reactions have occurred.
In an additional experiment, 500 mg (2.86 mM) 2,4-TDI was dissolved in DMSO with an increased water content of 0.1% (5.56 mM), a level perfectly conceivable in practice. This amount of water led to an accelerated reduction of the N=C=O absorptions, so that after 15 min, only 43%, and after 4 h, 14% of the isocyanate groups could be detected.
The fate of aromatic diisocyanates in Salmonella/microsome tests were also investigated (Table 5). When a sample of 500 mg 2,6-TDI / 100 ml EGDE solution was mixed with the test ingredients or with water (0.1:2.6 ml), up to 6.6% of the TDI was converted into 2,6-TDA within 45s (Table 5). With respect to the amount of diamine produced, no difference was seen between the distilled water and the aqueous system of the Salmonella/microsome test. Concerning the decline of diisocyanate content, however, the transfer to a different environment became apparent. In water, the 2,6-TDI concentration dropped to around 60%, which is basically in agreement with the results of the 10-fold approaches shown in Table 4 for the different types of TDI. When the ingredients of the Salmonella/microsome test replaced water, more than 90% of the initial 2,6-TDI disappeared within 15-45s. In this case, not 500 ug, but less than 50 ug 2,6-TDI, enriched with around 25 ug 2,6-TDA and further unquantified products will be poured onto the plate.
Table 4a. Stability TDI (in EGDE) during the first minute of a simulated test(a); HPLC determination of residual TDI and its reaction products. [This table has been separated by TDI type : 2,4-TDI)
Diisocyanate |
2,4-TDI |
|||
TDI in 100 ml EGDE |
5000 mg |
500 mg |
||
Dose / plate |
5000 ug |
500 ug |
||
Analysed products (b) |
2,4-TDI [%] |
2,4-TDA [%] |
2,4-TDI [%] |
2,4-TDA [%] |
Start |
100 |
nd |
100 |
nd |
After 15 s |
95 |
0.35 |
57 |
3.9 |
After 30 s |
83 |
0.65 |
48 |
5.7 |
After 45 s |
93 |
0.60 |
41 |
6.6 |
After 60 s |
93 |
0.65 |
35 |
7.4 |
nd: Not detectable, detection limit: 0.1%, e.g., 0.5 ug for the 500 mg/100 ml concentration.. na: Not available. (a) Simulating the mixing of dissolved TDI with the test ingredients (1 ml:26 ml mix with water). (b) Ureas and (insoluble) polyureas were not quantified.
<p>
Table 4b. Stability TDI (in EGDE) during the first minute of a simulated test(a); HPLC determination of residual TDI and its reaction products. [This table has been separated by TDI type : 2,6-TDI)
Diisocyanate |
2,6-TDI |
|||
TDI in 100 ml EGDE |
5000 mg |
500 mg |
||
Dose / plate |
5000 ug |
500 ug |
||
Analysed products (b) |
2,6-TDI [%] |
2,6-TDA [%] |
2,6-TDI [%] |
2,6-TDA [%] |
Start |
100 |
nd |
100 |
nd |
After 15 s |
91 |
0.27 |
67 |
3.5 |
After 30 s |
92 |
0.56 |
50 |
6.6 |
After 45 s |
92 |
0.81 |
37 |
9.5 |
After 60 s |
90 |
0.98 |
40 |
10.7 |
nd: Not detectable, detection limit: 0.1%, e.g., 0.5 ug for the 500 mg/100 ml concentration.. na: Not available. (a) Simulating the mixing of dissolved TDI with the test ingredients (1 ml:26 ml mix with water). (b) Ureas and (insoluble) polyureas were not quantified.
<p>
Table 4c. Stability TDI (in EGDE) during the first minute of a simulated test(a); HPLC determination of residual TDI and its reaction products. [This table has been separated by TDI type : TDI 80)
Diisocyanate |
TDI 80 |
|||
TDI in 100 ml EGDE |
5000 mg |
500 mg |
||
Dose / plate |
5000 ug |
500 ug |
||
Analysed products (b) |
2,4-TDI [%] |
2,6-TDI [%] |
2,4-TDA [%] |
2,6-TDA [%] |
Start |
100 |
100 |
nd |
nd |
After 15 s |
61 |
68 |
3.1 |
0.7 |
After 30 s |
52 |
61 |
4.4 |
1.0 |
After 45 s |
36 |
47 |
5.7 |
1.6 |
After 60 s |
35 |
45 |
6.0 |
1.9 |
nd: Not detectable, detection limit: 0.1%, e.g., 0.5 ug for the 500 mg/100 ml concentration.. na: Not available. (a) Simulating the mixing of dissolved TDI with the test ingredients (1 ml:26 ml mix with water). (b) Ureas and (insoluble) polyureas were not quantified.
<p>
Table 5. Stability of 2,6-TDI during the first minute of the mutagenicity test(a): HPLC determination of residual 2,6-TDI and its reaction products
2,6-TDI in 100 ml solvent |
500 mg EGDE |
500 mg/EGDE |
500 mg/DMSO |
|||
Reaction medium |
Dist. water |
Test ingredients(b) |
Test ingredients(b) |
|||
2,6-TDI/plate |
500 ug |
500 ug |
500 ug |
|||
Analysed products(c) |
2,6-TDI [%] |
2,6-TDA [%] |
2,6-TDI [%] |
2,6-TDA [%] |
2,6-TDI [%] |
2,6-TDA [%] |
Start |
100 |
nd |
99.5 |
0.5 |
12.3 |
9.1 |
After 5 s |
77.8 |
1.6 |
23.1 |
1.6 |
2.3 |
6.4 |
After 15 s |
70.0 |
3.4 |
8.4 |
4.7 |
3.0 |
8.4 |
After 30 s |
60.7 |
5.3 |
5.6 |
5.8 |
2.6 |
9.1 |
After 45 s |
61.9 |
6.6 |
8.1 |
5.6 |
2.5 |
8.3 |
nd: Not detectable; detection limit: 0.1%, e.g. 0.5 ug. (a) Mixing 0.1 ml dissolved 2,6-TDI with 2.6ml water or 2.6ml test ingredients. (b) 2.0ml agar + 0.5 ml S9 mix + 0.1 ml nutrient broth. (c) Ureas and (insoluble) polyureas were not quantified.
Applicant's summary and conclusion
- Conclusions:
- The authors concluded that these results were in good agreement with their chemical stability and concluded that the mutagenicity was a consequence of breakdown of TDI and the formation of TDA in the aqueous environment of the test system.
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