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Registration Dossier
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EC number: 204-847-9 | CAS number: 127-52-6
- 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

Additional information on environmental fate and behaviour
Administrative data
- Endpoint:
- additional information on environmental fate and behaviour
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- January to May 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted non-GLP. A testing guideline was not applied.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Solutions of the test material at different concentrations were exposed under "clean" and "dirty" conditions for various times. At various intervals, samples were taken and submitted to chemical analysis in order to determine the decompositoin (dechlorination) of the substance. Dirty conditions simulated conditions under which disinfection is appliacalbe. They furthermore are equivalent to methods for efficacy testing.
- GLP compliance:
- no
Test material
- Reference substance name:
- Sodium N-chlorobenzenesulphonamide
- EC Number:
- 204-847-9
- EC Name:
- Sodium N-chlorobenzenesulphonamide
- Cas Number:
- 127-52-6
- Molecular formula:
- C6H6ClNO2S.Na
- IUPAC Name:
- sodium chloro(phenylsulfonyl)azanide
- Test material form:
- other: liquid
- Details on test material:
- - Name of test material (as cited in study report): Chloramine B
- Lot/batch No.: 050125
-Packaging: PE dose 1000 g
Constituent 1
Results and discussion
Any other information on results incl. tables
The following results were obtained:
Chloramin B (BCHA) 0,01g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
8 |
21 |
23 |
30 |
46 |
51 |
95 |
97 |
Content of BCHA in g/L |
0,0115 |
0,0090 |
0,0075 |
0,0062 |
0,0054 |
0,0031 |
0,0028 |
0,0024 |
0,0014 |
0,0013 |
0,0003 |
0,0002 |
Content of BCHA (%) |
100 |
78,3 |
65,2 |
53,9 |
47,0 |
27,0 |
24,3 |
20,9 |
12,2 |
11,3 |
2,6 |
1,7 |
Chloramin B (BCHA) 0,01g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
|||||||
Content of BCHA in g/L |
0,0104 |
0,0002 |
< 0,0002 |
no det. |
|||||||
Content of BCHA (%) |
100 |
2,7 |
< 2,7 |
Chloramin B (BCHA) 0,1g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
6 |
8 |
22 |
26 |
71 |
|||
Content of BCHA in g/L |
0,1050 |
0,0994 |
0,0932 |
0,0865 |
0,0845 |
0,0683 |
0,0693 |
0,0484 |
|||
Content of BCHA (%) |
100 |
94,6 |
88,7 |
82,3 |
80,4 |
65,0 |
66,0 |
46,1 |
Chloramin B (BCHA) 0,1g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
6 |
8 |
14 |
18 |
26 |
71 |
||
Content of BCHA in g/L |
0,1041 |
0,0705 |
0,0551 |
0,0360 |
0,0309 |
0,0094 |
0,0025 |
0,0023 |
< 0,0002 |
||
Content of BCHA (%) |
100 |
67,7 |
52,9 |
34,6 |
29,7 |
9,0 |
2,4 |
2,2 |
< 0,2 |
Chloramin B (BCHA) 1g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
6 |
8 |
19 |
29 |
92 |
124 |
29d |
Content of BCHA in g/L |
1,0296 |
1,0296 |
1,0025 |
1,0025 |
1,0025 |
1,0025 |
1,0025 |
0,8229 |
||
Content of BCHA (%) |
100 |
100 |
97,4 |
97,4 |
97,4 |
97,4 |
97,4 |
79,9 |
Chloramin B (BCHA) 1g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
6 |
8 |
19 |
29 |
92 |
124 |
29d |
Content of BCHA in g/L |
1,0296 |
0,9212 |
0,8213 |
0,7315 |
0,7044 |
0,6232 |
0,5419 |
0,3238 |
||
Content of BCHA (%) |
100 |
89,5 |
79,8 |
71,0 |
68,4 |
60,5 |
52,6 |
31,4 |
Chloramin B (BCHA) 10g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
9 d |
38 d |
Content of BCHA in g/L |
10,162 |
10,162 |
10,162 |
10,162 |
10,162 |
10,162 |
10,162 |
10,162 |
10,162 |
9,982 |
9,131 |
|
Content of BCHA (%) |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
98,2 |
89,9 |
Chloramin B (BCHA) 10g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
38 d |
Content of BCHA in g/L |
10,162 |
10,117 |
10,072 |
10,027 |
9,937 |
9,937 |
9,891 |
9,801 |
9,666 |
8,636 |
|
Content of BCHA (%) |
100 |
99,6 |
99,1 |
98,7 |
97,8 |
97,8 |
97,3 |
96,4 |
95,1 |
85,0 |
Chloramin B (BCHA) 20g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
|
Content of BCHA in g/L |
20,086 |
20,086 |
20,086 |
20,086 |
20,086 |
20,086 |
20,086 |
20,086 |
20,086 |
||
Content of BCHA (%) |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
Chloramin B (BCHA) 20g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
|
Content of BCHA in g/L |
20,086 |
20,074 |
20,069 |
20,022 |
20,001 |
19,998 |
19,974 |
19,901 |
19,889 |
||
Content of BCHA (%) |
100 |
99,9 |
99,9 |
99,7 |
99,6 |
99,6 |
99,4 |
99,1 |
99,0 |
Chloramin B (BCHA) 50g/L, clean conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
|
Content of BCHA in g/L |
49,998 |
49,998 |
49,998 |
49,998 |
49,998 |
49,998 |
49,998 |
49,998 |
49,998 |
||
Content of BCHA (%) |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
100 |
Chloramin B (BCHA) 50g/L, dirty conditions
Time of analyse [hour] |
Start |
0,5 |
2 |
5 |
11 |
24 |
27 |
31 |
48 |
72 |
|
Content of BCHA in g/L |
49,998 |
49,997 |
49,991 |
49,876 |
49,801 |
49,706 |
49,665 |
49,611 |
49,599 |
||
Content of BCHA (%) |
100 |
100 |
100 |
99,8 |
99,6 |
99,4 |
99,3 |
99,2 |
99,2 |
Applicant's summary and conclusion
- Conclusions:
- A 90% dechlorination under realistic application conditions was verified in 0.01 and 0.1 g/L aqueous solutions within 0.5 and 14 hours, respectively. At an initial concentration of 0.01 g/L, the substance was not detectable after 5 hours of exposure to "dirty" conditions. Chloramin B in higher concentrations 1-50g/L however was rather stable even under dirty conditions.
- Executive summary:
In a non-GLP study, aqueous solutions (application solutions) of the test material at concentrations 0.01, 0.1, 1, 10, 20 and 50 g/L were exposed to „clean“ and „dirty“ conditions. „Clean” conditions: 1 L of the Chloramin B application solution, 0,3 g Albumin (Adult Bovine Serum, Lot B01110-2358); “Dirty” conditions: 1 L of Chloramin B application solution, 3 g Albumin (Adult Bovine Serum, Lot B01110-2358), 3 ml sheep erythrocytes. The “dirty” conditions were meant to simulate situations, were disinfection measures are required. The “dirty” conditions are equivalent to the conditions for efficacy testing of disinfectants. Samples were taken at regular intervals (hours and days) in order to measure the decomposition/dechlorination of the test material. The following analytical methods were applied: A validatedHPLC Method for the concentration 0.01 and 0.1 g/L and a validated iodometric titration methodfor the concentrations1 – 50 g/L. The measurements showed that at an initial concentration of 0.01 g/L, the substance was not detectable after 5 hours of exposure to "dirty" conditions.
A 90% dechlorination under realistic "dirty" application conditions was verified in 0.01 and 0.1 g/L aqueous solutions within 0.5 and 14 hours, respectively. Dechlorination in clean solutions was longer, i.e. 90% of 0.01 g/L solution were dechlorinated within 95 hours and abolut 50% of 0.1 g/l solutoin within 71 hours. Chloramin B in higher concentrations 1 -50g/L however was rather stable even under “dirty” conditions. Taking into consideration that during its way to the STP Chloramine B is diluted with the other waste waters - highly contaminated with bacteria and organic materials - and that a worst case dilutions factor of 500 (50 g/L time 0.1 g/L) is very realistic, it can be concluded that no Chloramine B is reaching the STP but its dechlorinated form – benzenesulphonamide.
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