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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
Toxicity to aquatic algae and cyanobacteria
Administrative data
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009-10-16 to 2009-10-23
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well documented GLP and guideline study.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- GLP compliance statement and certificate included in full study report.
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: The concentrations of the test item were analytically determined from all test concentrations and the control after 0 h (test start) and 72 h (test end).
- Sampling method: Samples at start and end of the test were taken directly from the test replicates.
- Sample storage conditions before analysis: All samples were stored at 6 ± 2 °C until start of analysis, if necessary.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A saturated solution* was prepared. A dispersion of 1440 mg/L prepared in dilution water was shaken with 20 rpm for 48 h at ambient temperature and filtrated with 0.45 µm RC filter.
- Eluate: Dilution water
- Differential loading: The saturated solution and further four dilution levels were tested in a geometrical series with a dilution factor √10: 1.0 - 3.2 - 10 - 32 and 100 % of the saturated solution corresponding to initial measured concentrations of 0.106 – 0.323 – 0.974 – 3.26 – 9.92 mg/L.
- Controls: Six replicates (without test item) were tested under the same test conditions as the test replicates.
Test organisms
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: Desmodesmus subspicatus Chodat
- Strain: SAG 86.81
- Source (laboratory, culture collection): SAG Pflanzenphysiologisches Institut der Universitaet Goettingen, Nikolausberger Weg 18, D-37073 Goettingen, Germany
- Age of inoculum (at test initiation):4 days
- Method of cultivation: Fresh stocks were prepared from Z-Agar. Light intensity amounted 35 - 70 µE x m-2 x s-1 for 24 h per day.
ACCLIMATION
- Culturing media and conditions (same as test or not): Same as test
- Any deformed or abnormal cells observed: No
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Post exposure observation period:
- No
Test conditions
- Hardness:
- Not measured
- Test temperature:
- Mean: 23.5 °C, Min: 23 °C, Max: 25 °C
- pH:
- Initial measured test item concentration pH-value
[mg/L] Start; 0 h End; 72 h
9.92 8.12 8.13
3.26 8.12 8.35
0.974 8.10 8.32
0.323 8.09 8.33
0.106 8.06 8.34
Control 7.96 8.34 - Dissolved oxygen:
- Not measured
- Salinity:
- Not measured, freshwater
- Nominal and measured concentrations:
- Please refer to "Any other information on materials and methods incl. tables"
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 250 mL Erlenmeyer flasks
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: sterile 250 mL Erlenmeyer flasks, test volume 100 mL
- Aeration: Test containers were placed on a rotary shaker and oscillated at appr. 70 rpm
- Type of flow-through (e.g. peristaltic or proportional diluter): None
- Renewal rate of test solution (frequency/flow rate): One application at test start
- Initial cells density: 5074 cells/mL
- Control end cells density: Mean 492829 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): None
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Dilution water, composition acc. to the guideline
- Hardness: 0.24 mmol Ca+Mg/L
- pH-value: 8.1 +/- 0.2
- Culture medium: Nutrient Medium Z acc. to LÜTTGE et al. (1994)
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: 24 h
- Light intensity and quality: 60 - 120 µE x m-2 x s-1
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: [counting chamber; electronic particle counter; fluorimeter; spectrophotometer; colorimeter] Fluorimeter, via Chlorophyll-a fluorescence (excitation at 436 nm, emission at 685 nm), cell concentrations were related to all cell density values acc. to a calibration curve.
TEST CONCENTRATIONS
- Range finding study: Yes - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.26 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 9.92 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 6.46 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: (3.26 - 9.92)
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.26 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 9.92 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 7.1 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- cell number
- Remarks on result:
- other: CI: 3.26 - 9.92
- Details on results:
- - Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): no
- Unusual cell shape: No
- Colour differences: Not reported
- Flocculation: No data
- Adherence to test vessels: No
- Aggregation of algal cells: yes
- Other: Not reported
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: Not reported - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50: Rate-related inhibition: 0.600 (CI 0.545 - 0.653) mg/L
Yield Inhibition: 0.280 (CI 0.266 - 0.299) mg/L - Reported statistics and error estimates:
- EC10-, EC20- and EC50-values of the growth rate and yield inhibition after 72 h were calculated by linear dose-response regression. Calculation of the confidence intervals were estimated empirically.
NOEC, LOEC NOEC/LOEC was determined by calculation of statistical significance of growth rates and yield. One Way Analysis of Variance (ANOVA) and DUNNETT’s test was used for NOEC/LOEC calculations. When running a One Way Analysis of Variance a Normality test and an Equal Variance test were done first. P-values for both Normality and Equal Variance test are 0.05. The a-value (acceptable probability of incorrectly concluding that there is a difference) was a=0.05.
Any other information on results incl. tables
NOEC, LOEC and EC - values of 1-Chlor-2,5-dimethoxy-4-nitrobenzol trocken (0-72 h)
based on initial measured test item concentrations [mg/L]
Rate-related Inhibition |
|
NOEC |
3.26 |
LOEC |
9.92 |
ErC10 |
4.12 (3.26 – 9.92) |
ErC20 |
4.60 (3.26 – 9.92) |
ErC50 |
6.46 (3.26 – 9.92) |
Inhibition of Yield |
|
NOEC |
3.26 |
LOEC |
9.92 |
EyC10 |
5.40 (3.26 – 9.92) |
EyC20 |
5.77 (3.26 – 9.92) |
EyC50 |
7.10 (3.26 – 9.92) |
Cell Densities
|
Initial measured test item concentration |
Replicate |
Cell density [cells/mL] |
||||||
[mg/L] |
No. |
0 h |
24 h |
48 h |
72 h |
|
|||
9.92 |
1 |
5074 |
9391 |
7915 |
14906 |
|
|||
2 |
5074 |
11245 |
8735 |
7481 |
|
||||
3 |
5074 |
13602 |
7058 |
5988 |
|
||||
Mean |
5074 |
11413 |
7903 |
9458 |
|
||||
3.26 |
1 |
5074 |
19170 |
127885 |
882978 |
|
|||
2 |
5074 |
18657 |
127344 |
729392 |
|
||||
3 |
5074 |
18776 |
141100 |
795743 |
|
||||
Mean |
5074 |
18868 |
132110 |
802704 |
|
||||
0.974 |
1 |
5074 |
17116 |
91646 |
602272 |
|
|||
2 |
5074 |
16144 |
99460 |
599824 |
|
||||
3 |
5074 |
21310 |
119710 |
578033 |
|
||||
Mean |
5074 |
18190 |
103605 |
593376 |
|
||||
0.323 |
1 |
5074 |
16628 |
87816 |
641997 |
|
|||
2 |
5074 |
20478 |
76283 |
531317 |
|
||||
3 |
5074 |
18079 |
131387 |
587877 |
|
||||
Mean |
5074 |
18395 |
98495 |
587064 |
|
||||
0.106 |
1 |
5074 |
15254 |
80707 |
515889 |
|
|||
2 |
5074 |
15898 |
75533 |
536282 |
|
||||
3 |
5074 |
17784 |
99665 |
578701 |
|
||||
Mean |
5074 |
16312 |
85302 |
543624 |
|
||||
Control |
1 |
5074 |
18538 |
79173 |
455381 |
|
|||
2 |
5074 |
16402 |
73470 |
461560 |
|
||||
3 |
5074 |
19826 |
88862 |
599549 |
|
||||
4 |
5074 |
17727 |
86135 |
466550 |
|
||||
5 |
5074 |
17747 |
76611 |
463257 |
|
||||
6 |
5074 |
17919 |
101695 |
510678 |
|
||||
Mean |
5074 |
18027 |
84324 |
492829 |
|
Evaluation after 72 h
Statistically significant differences of growth rates and yield compared to
control values are marked (+), not significant differences are marked (-).
Initial measured test item concentration |
Replicate |
Growth rate |
Rate-related inhibition |
Yield |
Inhibition of yield |
||
[mg/L] |
No. |
[d-1] |
[%] |
[cells/mL] |
[%] |
||
9.92 |
1 |
0.359 |
76.4 |
9832 |
98.0 |
||
2 |
0.129 |
91.5 |
2407 |
99.5 |
|||
3 |
0.055 |
96.4 |
914 |
99.8 |
|||
Mean |
(+) |
0.181 |
88.1 |
(+) |
4384 |
99.1 |
|
3.26 |
1 |
1.72 |
-12.9 |
877904 |
-80.0 |
||
2 |
1.66 |
-8.68 |
724318 |
-48.5 |
|||
3 |
1.69 |
-10.6 |
790669 |
-62.1 |
|||
Mean |
(-) |
1.69 |
-10.7 |
(+)* |
797630 |
-63.5 |
|
0.974 |
1 |
1.59 |
-4.50 |
597198 |
-22.4 |
||
2 |
1.59 |
-4.41 |
594750 |
-21.9 |
|||
3 |
1.58 |
-3.60 |
572959 |
-17.5 |
|||
Mean |
(-) |
1.59 |
-4.17 |
(-) |
588302 |
-20.6 |
|
0.323 |
1 |
1.61 |
-5.89 |
636923 |
-30.6 |
||
2 |
1.55 |
-1.75 |
526243 |
-7.89 |
|||
3 |
1.58 |
-3.97 |
582803 |
-19.5 |
|||
Mean |
(-) |
1.58 |
-3.87 |
(-) |
581990 |
-19.32 |
|
0.106 |
1 |
1.54 |
-1.11 |
510815 |
-4.73 |
||
2 |
1.55 |
-1.96 |
531208 |
-8.91 |
|||
3 |
1.58 |
-3.62 |
573627 |
-17.6 |
|||
Mean |
(-) |
1.56 |
-2.23 |
(-) |
538550 |
-10.4 |
|
Control |
1 |
1.50 |
450307 |
||||
2 |
1.50 |
456486 |
|||||
3 |
1.59 |
594475 |
|||||
4 |
1.51 |
461476 |
|||||
5 |
1.51 |
458183 |
|||||
6 |
1.54 |
505604 |
|||||
Mean |
1.52 |
487755 |
Section-by-Section and Average
Specific Growth Rates of the Control Group
(0 – 72 h)
Replicate No. |
Specific growth rate [d-1] |
Mean (0 - 72 h) |
SD ± |
CV |
Mean CV [%] |
|||
section-by-section |
||||||||
0 - 24 h |
24 - 48 h |
48 - 72 h |
||||||
Control |
1 |
1.30 |
1.45 |
1.75 |
1.50 |
0.231 |
15.4 |
17.5 |
2 |
1.17 |
1.50 |
1.84 |
1.50 |
0.332 |
22.1 |
||
3 |
1.36 |
1.50 |
1.91 |
1.59 |
0.284 |
17.9 |
||
4 |
1.25 |
1.58 |
1.69 |
1.51 |
0.228 |
15.2 |
||
5 |
1.25 |
1.46 |
1.80 |
1.51 |
0.276 |
18.4 |
||
6 |
1.26 |
1.74 |
1.61 |
1.54 |
0.246 |
16.0 |
||
Mean |
1.52 |
|
||||||
SD ± |
0.04 |
|
||||||
CV [%] |
2.33 |
|
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- In this study 1-Chlor-2,5-dimethoxy-4-nitrobenzol trocken was found to inhibit the growth of the freshwater green alga Desmodesmus subspicatus after 72 h. The EC50-values for inhibition of specific growth rate (ErC50) and yield (EyC50) after 72 h were 6.46 (3.26 – 9.92) mg/L and 7.10 (3.26 – 9.92) mg/L, respectively. All effect levels are given based on initial measured concentrations of 1-Chlor-2,5-dimethoxy-4-nitrobenzol trocken.
- Executive summary:
The toxicity of 1-Chlor-2,5-dimethoxy-4-nitrobenzol trocken (batch number DALA 053552) to the unicellular freshwater green alga Desmodesmus subspicatus was determined according to the principles of OECD 201 at Dr.U.Noack-Laboratorienin 31157 Sarstedt, Germany from October 16 to 23, 2009 with the definitive exposure phase being conducted from October 20 to 23, 2009. The aim of the study was to assess the effects on growth rate and yield over a period of 72 h. Due to the poor solubility of the test substance the test solutions were prepared according to OECD (diffucult substances).
All effect values are given based on initial measured concentrations of the test item.
NOEC, LOEC and EC - values of 1-Chlor-2,5-dimethoxy-4-nitrobenzol trocken (0-72 h)
based on initial measured test item concentrations [mg/L]
Rate-related Inhibition
NOEC
3.26
LOEC
9.92
ErC10
4.12 (3.26 – 9.92)
ErC20
4.60 (3.26 – 9.92)
ErC50
6.46 (3.26 – 9.92)
Inhibition of Yield
NOEC
3.26
LOEC
9.92
EyC10
5.40 (3.26 – 9.92)
EyC20
5.77 (3.26 – 9.92)
EyC50
7.10 (3.26 – 9.92)
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