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Diss Factsheets

Ecotoxicological information

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:
1997-01-13 - 1997-01-14
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
test procedure in accordance with national standard methods

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1997
Report date:
1997

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
other: DIN 38412 Part L8
Version / remarks:
03-1991
Qualifier:
according to guideline
Guideline:
other: NEN-EN-ISO 10712
Version / remarks:
1996
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
4-bromobenzonitrile
EC Number:
210-764-9
EC Name:
4-bromobenzonitrile
Cas Number:
623-00-7
Molecular formula:
C7H4BrN
IUPAC Name:
4-bromobenzonitrile
impurity 1
Chemical structure
Reference substance name:
2-bromobenzonitrile
EC Number:
218-045-1
EC Name:
2-bromobenzonitrile
Cas Number:
2042-37-7
Molecular formula:
C7H4BrN
IUPAC Name:
2-bromobenzonitrile
impurity 2
Chemical structure
Reference substance name:
3-bromobenzonitrile
EC Number:
230-127-9
EC Name:
3-bromobenzonitrile
Cas Number:
6952-59-6
Molecular formula:
C7H4BrN
IUPAC Name:
3-bromobenzonitrile
impurity 3
Chemical structure
Reference substance name:
Benzonitrile
EC Number:
202-855-7
EC Name:
Benzonitrile
Cas Number:
100-47-0
Molecular formula:
C7H5N
IUPAC Name:
benzonitrile
impurity 4
Chemical structure
Reference substance name:
Water
EC Number:
231-791-2
EC Name:
Water
Cas Number:
7732-18-5
Molecular formula:
H2O
IUPAC Name:
Water
Test material form:
solid

Sampling and analysis

Analytical monitoring:
not specified

Test solutions

Vehicle:
no

Test organisms

Test organisms (species):
other: Psreudomonas putida
Details on test organisms:
TEST ORGANISM
- Common name:
- Strain:
- Source (laboratory, culture collection):
- Age of inoculum (at test initiation):
- Method of cultivation:

ACCLIMATION
- Acclimation period:
- Culturing media and conditions (same as test or not):
- Any deformed or abnormal cells observed:

Study design

Test type:
static
Water media type:
freshwater
Total exposure duration:
16 h

Test conditions

Test temperature:
23 +/- 1
pH:
7.1 - 7.4
Details on test conditions:
TEST SYSTEM
- Test vessel: Erlenmeyer flasks
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glas, 100 mL, ./. 40 mL
- Aeration: no
- Type of flow-through (e.g. peristaltic or proportional diluter): na
- Renewal rate of test solution (frequency/flow rate): na
- Initial cells density: FNU/436 nm = 50
- Control end cells density:
- No. of organisms per vessel:
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 10
- No. of vessels per vehicle control (replicates): 0

GROWTH MEDIUM
- Standard medium used: no
- Detailed composition if non-standard medium was used:
Solution I: 10.0 g NaNO3
2.4 g K2HPO4
1.2 g KH2PO4
1.0 g yeast extract
Dissolved in 500 mL water
Silution II: 10.0 g NaNO3
2.4 g K2HPO4
1.2 g KH2PO4
Dissolved in 500 mL water
Solution III: 40.0 g D(+)-glucose monohydrate
Dissolved in 500 mL water
Solution IV: 0.01 g Fe(III)citrate
4.0 g MgSO4 * 7 H2O
Dissolved in 1 L water

test medium: 25 mL I
25 mL III
50 mL IV
made up to 1 L with water

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water:
tab water purified by reverse osmosis and subsequently passed over activated carbon and ion-exchange cartiges
- Total organic carbon:
- Particulate matter:
- Metals:
- Pesticides:
- Chlorine:
- Alkalinity:
- Ca/mg ratio:
- Conductivity:
- Culture medium different from test medium:
- Intervals of water quality measurement:

OTHER TEST CONDITIONS
- Sterile test conditions:
- Adjustment of pH: 7.1 - 7.4
- Photoperiod:
- Light intensity and quality:
- Salinity (for marine algae):

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: spectrophotometer
- Chlorophyll measurement: na
- Other:

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Justification for using less concentrations than requested by guideline:
- Range finding study na
- Test concentrations (mg/L): 0; 6.3; 12.5; 25; 50; 100; 200
- Results used to determine the conditions for the definitive study:
Reference substance (positive control):
yes
Remarks:
3,5-Dichlorophenol

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
16 h
Dose descriptor:
EC10
Effect conc.:
ca. 57 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Key result
Duration:
16 h
Dose descriptor:
EC50
Effect conc.:
ca. 135 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
cell number
Results with reference substance (positive control):
- Results with reference substance valid? yes
- EC50: 22 mg/L
- Other:
Reported statistics and error estimates:
Linear regression

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
Based on the result of the test presently performed, the toxicity threshold value (EC10) of 4-Bromobenzonitrile was 57 mg/L. The "Bewertungszahl" is therefore 4.2 (Bewertung wassergefährdender Stoffe, 1989).
The EC50 was calculated to be 135 mg/L.
Executive summary:

4 -Bromobenzonitril was investigated for its ability to inhibit the cell multiplication of the bacteria species Pseudomonas putida according to DIN 38412 Part L 8 (March 1991) and NEN-EN-ISO 10712 (1996).

Suspensions of Speudomonas putida were exposed th concentrations ranging from 6.3 to 200 mg/L 4 -Bromobenzonitrile.

After incubation for 16 h the extinction values of the bacterial cell suspensions were measured. Significant (> 10 %) toxicity was observed at 100 and 200 mg/L.

Based on the result of the test presently performed, the toxicity threshold value (EC10) of 4-Bromobenzonitrile was 57 mg/L. The "Bewertungszahl" (Assessment figure or value for bacterial toxicity) is therefore 4.2 (Bewertung wassergefährdender Stoffe, 1989). The EC50 was calculated to be 135 mg/L.

The EC50 value for the reference substance, 3,5 -dichlorophenol, tested during the same experiment, was 22 mg/L. Since this value was within the eccepted range of 10 - 30 mg/L for the EC50, and the multiplication factor of the bacteria within the test was over 60, it was concluded that the test conditions were optimal and the results obtained were valid.