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EC number: 230-086-7 | CAS number: 6940-53-0
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 20110-06-02 to 2010-08-04
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study, followed international guidelines, no deviations
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 1-chloro-2,5-dimethoxy-4-nitrobenzene
- EC Number:
- 230-086-7
- EC Name:
- 1-chloro-2,5-dimethoxy-4-nitrobenzene
- Cas Number:
- 6940-53-0
- Molecular formula:
- C8H8ClNO4
- IUPAC Name:
- 1-chloro-2,5-dimethoxy-4-nitrobenzene
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: all concentrations and blank
- Sampling method: from the middle of the water column and from the middle of the tanks
- Sample storage conditions before analysis: frozen, thawed just befor analysing
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: OECD 23, WAF
- Eluate: filtered through 0.45 µm sieve
- Differential loading: by dilution
- Controls: yes, blank controls
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): not applicable
- Concentration of vehicle in test medium (stock solution and final test solution(s) including control(s)): not applicable
- Evidence of undissolved material (e.g. precipitate, surface film, etc): no
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Water flea
- Strain: Clone V
- Source: Laboratory bred, originally purchased in a healthy condition from the Umweltbundesamt in Berlin/Germany.
- Age at study initiation (mean and range, SD): freshly hatched, age between 6 - 24 hours
- Peripheral shell growth removed prior to test initiation: no
- Method of breeding: single culture (one daphnid per 100 mL) in water composed of dechlorinated drinking water and deionised water.
- Feeding during test: no
- Food type: not applicable
- Amount: not applicable
- Frequency: not applicable
ACCLIMATION
- Acclimation period: not applicable, breeding water is the same as test water
- Acclimation conditions (same as test or not): yes
- Type and amount of food: not during test
- Feeding frequency: not during test
- Health during acclimation (any mortality observed): not applicable
QUARANTINE (wild caught)
- Duration: not applicable
- Health/mortality: not applicable
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Post exposure observation period:
- no
Test conditions
- Hardness:
- 9°dH (160.63 mg/L as CaCO3) at test initiaition
- Test temperature:
- 21.1°C +/- 0.5°C
- pH:
- 8.25 +/- 0.29
- Dissolved oxygen:
- 99 +- 1.8 % (Std. Dev.)
- Salinity:
- no data
- Nominal and measured concentrations:
- see block any other information on material and methods
- Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beaker
- Type (delete if not applicable): no data
- Material, size, headspace, fill volume: 100 ml beaker, filled 50 ml
- Aeration: no
- Type of flow-through (e.g. peristaltic or proportional diluter): not applicable
- Renewal rate of test solution (frequency/flow rate): no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): not applicable
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: dechlorinated drinking water and deionised water
- Total organic carbon: no data
- Particulate matter: no data
- Metals: no data
- Pesticides: no data
- Chlorine: "dechlorinated"
- Alkalinity: no data
- Ca/mg ratio: no data
- Conductivity: no data
- Culture medium different from test medium: no
- Intervals of water quality measurement: no data
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: test was performed in the dark since the test item is known to be substject to photolysis
- Light intensity: not applicable
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : swimming behaviour
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2,2
- Justification for using less concentrations than requested by guideline: not applicable
- Range finding study: yes
- Test concentrations:: 0-0,01 - 0,1 - 1-10-10 mg/L
- Results used to determine the conditions for the definitive study: yes - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: measured: 13 mg/L
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: not reported
- Observations on body length and weight: not reported
- Other biological observations: not reported
- Mortality of control: not signifcant
- Other adverse effects control: not reported
- Abnormal responses: not reported
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: yes - Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Mortality: see table in block "any other information on results..."
- EC50/LC50: see table in block "any other information on results..."
- Other:
Any other information on results incl. tables
I. ECx-values of daphnids exposed to the test item (nominal / actual concentrations)
No EC50 value could be derived since no mortality was performed up to the tested concentration of 100 mg/L (nominal loading). Hence, the NOEC is 100 mg/L (nominal loading).
For nominal 100 mg/L the corresconding measured value from the chemical analysis was found to be 13 mg/L.
Raw data 48 h
|
Control |
0.01 |
0.1 |
1 |
10 |
100 |
|
|
[mg/L] |
||||
|
immobilised daphnids after 48 h |
|||||
Group 1 |
0 |
0 |
0 |
0 |
0 |
0 |
Group 2 |
0 |
0 |
0 |
0 |
0 |
0 |
Group 3 |
0 |
0 |
0 |
0 |
0 |
0 |
Group 4 |
0 |
0 |
0 |
0 |
0 |
0 |
S |
0 |
0 |
0 |
0 |
0 |
0 |
% |
0 |
0 |
0 |
0 |
0 |
0 |
Toxic Reference
|
24 h |
48 h |
||||
K2Cr2O7 |
1.0 |
2.0 |
1.0 |
2.0 |
||
[mg/L] |
immobilised daphnids |
|||||
Group 1 |
0 |
0 |
0 |
4 |
||
Group 2 |
0 |
0 |
0 |
5 |
||
Group 3 |
1 |
2 |
1 |
5 |
||
Group 4 |
0 |
0 |
0 |
5 |
||
S |
1 |
2 |
1 |
19 |
||
% |
5 |
10 |
5 |
95 |
The results indicate an EC50(48 h) of the reference item potassium dichromate between 1.0 mg/L and 2.0 mg/L. Since the results fall within the historical data generated with the reference item at the testing facility, the daphnids were suitable for the determination of the toxicological effects of the test item.
Analytical results
The test was performed under static conditions. The analytical verification of test item concentrations in daphnid test medium was done by analysing the content of 1-Chloro-2,5-dimethoxy-4-nitrobenzene in the samples during the test. Samples were taken after initiation of the test, after 24 hours and 48 hours at all concentration levels. Control and 100 mg/L were analysed at t = 0h, t = 24 h and t = 48 h.
Test item |
Sampling (h) |
1-Chloro-2,5-dimethoxy-4-nitrobenzene |
nominal (mg/L) |
mg/L |
|
0 |
0 fresh |
< LOQ |
24 aged |
< LOQ |
|
48 aged |
< LOQ |
|
100 |
0 fresh |
13 |
24 aged |
13 |
|
48 aged |
12 |
LOQ: 0.4 mg/L test item
The test was performed within the solubility limit of 1-Chloro-2,5-dimethoxy-4-nitrobenzene. At the highest test concentration of 100 mg/L nominal only 13 mg 1-Chloro-2,5-dimethoxy-4-nitrobenzene/L was found after a 48-hours stirring period and filtration. The toxicological endpoints were evaluated using nominal and actual concentrations of the test item.
Recovery of 1-chloro-2,5-dimethoxy-4-nitrobenzene from the test item spiked into test medium
The recovery was determined by fortification of test medium with the test item at the concentration levels
Fortification level |
Found |
Recovery |
Mean Recovery |
0.400 |
0.400 |
100 |
109±4 |
100 |
112 |
112 |
101±11 |
Mean recoveries and relative standard deviations per fortification fulfil the criteria of guideline SANCO/3029/99 (70-110 % mean recovery, ≤ 20 % RSD).
Linearity
The detector response for HPLC-MS/MS analysis was linear within the range from 2.00 mg/L to 0.05 mg/L with r2> 0.995Nominal concentration |
Peak area |
Calculated |
2000 |
775 113 |
2041.006 |
1000 |
340 618 |
944.212 |
500 |
141 016 |
440.363 |
200 |
41 602 |
189.409 |
100 |
17 772 |
129.253 |
50 |
8 464 |
105.757 |
% O2saturation of the test solutions
Test item |
nominal test item concentration [mg/L] |
|||||
|
Control |
0.01 |
0.1 |
1 |
10 |
100 |
Time [h] |
Oxygen |
|||||
0 fresh |
96 |
96 |
97 |
96 |
96 |
97 |
24 aged |
99 |
100 |
100 |
101 |
100 |
101 |
48 aged |
100 |
99 |
99 |
100 |
100 |
100 |
Mean |
98.3 |
98.3 |
98.7 |
99.0 |
98.7 |
99.3 |
Std. dev. |
2.1 |
2.1 |
1.5 |
2.6 |
2.3 |
2.1 |
Mean |
99 |
|||||
Std. dev. |
1.8 |
pH-values of the test solutions
|
nominal test item concentration [mg/L] |
|||||
|
Control |
0.01 |
0.1 |
1 |
10 |
100 |
Time [h] |
pH |
|||||
0 fresh |
7.87 |
7.87 |
7.85 |
7.82 |
7.88 |
7.86 |
24 aged |
8.42 |
8.45 |
8.45 |
8.47 |
8.49 |
8.49 |
48 aged |
8.36 |
8.41 |
8.44 |
8.45 |
8.46 |
8.46 |
Mean |
8.22 |
8.24 |
8.25 |
8.25 |
8.28 |
8.27 |
Std. dev. |
0.30 |
0.32 |
0.34 |
0.37 |
0.34 |
0.36 |
Mean |
8.25 |
|||||
Std. dev. |
0.29 |
Temperature of the test solutions
|
nominal test item concentration [mg/L] |
|||||
|
Control |
0.01 |
0.1 |
1 |
10 |
100 |
Time [h] |
Temperature |
|||||
0 fresh |
21.8 |
21.8 |
21.9 |
21.9 |
21.9 |
21.6 |
24 aged |
20.4 |
20.4 |
20.8 |
21.1 |
20.9 |
20.9 |
48 aged |
20.6 |
20.7 |
20.7 |
21.0 |
20.9 |
20.9 |
Mean |
20.9 |
21.0 |
21.1 |
21.3 |
21.2 |
21.1 |
Std. dev. |
0.8 |
0.7 |
0.7 |
0.5 |
0.6 |
0.4 |
Mean |
21.1 |
|||||
Std. dev. |
0.5 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity study (48h) on daphnia was determined . Up to the highest test concentration of 100 mg/L (nominal loiading) no mortalitity could be observed.
- Executive summary:
In a valid GLP study following Guideline EC-method C.2 and OECD 202 (2004) the short term toxicity of 1-Chloro-2,5-dimethoxy-4-nitrobenzene to aquatic invertebrates, represented by Daphnia magma was determined.
According to the results of the test, theEC50(48 h)of the test item was determined to be> 100mg/L(nominal).The correspondingNOEC (48 h)was100 mg/L(nominal).The correspondingactualvalueswere >13 mg/Lfor theEC50(48 h)and 13mg/Lfor theNOEC (48 h).
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