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EC number: - | CAS number: -
- 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
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 14 September - 17 September 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Fully documented study run under GLP and according to international guidelines.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- yes
- Remarks:
- Temperature in reference study and main study higher as in guideline. pH values of the controls in main study varied more than stated in the guideline. As the controls showed a normal exponential growth, these deviations can be stated as uncritical.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- yes
- Remarks:
- Temperature in reference study and main study higher as in guideline. pH values of the controls in main study varied more than stated in the guideline. As the controls showed a normal exponential growth, these deviations can be stated as uncritical.
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- At the beginning and at the end of the test, the content of test item was determined by DOC-determination in the test solutions.
- Vehicle:
- no
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: Desmodesmus subspicatus
- Strain: CHODAT
- Source (laboratory, culture collection): MBM Sciencebridge GmbH (Institut für Pflanzenphysiologie of Universität Göttingen)
- Age of inoculum (at test initiation): From September 2010
- Method of cultivation: The algae are kept as stock culture on solid agar at 8 °C. From an aliquot of this stock culture the preculture was prepared.
ACCLIMATION
- Acclimation period: Four days before the start of each test, an aliquot of the stock culture containing a few cells was brought into preculture medium and incubated for 72 hours. The resulting culture is growing exponentially.
Before usage, the culture was checked on the absence of cell aggregates. After the adjustment to a cell concentration of about 6*10 E4/mL through photometric measurement and addition of algal medium, the culture was usable for the test. The adjusted preculture was mixed with the same amount of 10-fold-nutrient solution. This mixture was the test culture.
- Culturing media and conditions (same as test or not): same as test (without substance) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 24 - 27 °C
- pH:
- 7 - 9.5 (in controls 7 - 9)
- Nominal and measured concentrations:
- Nominal and measured concentrations: See table in "Any other information on materials and methods incl. tables"
- Details on test conditions:
- TEST SYSTEM
- Test vessel: closed glass beakers
- Type (delete if not applicable):closed
- Material, size, headspace, fill volume: glass, 130 mL
- Aeration: no (indirectly by shaking)
- Initial cells density: 6*10^4/mL
- Control end cells density:487*10^4/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: according to guideline
- Intervals of water quality measurement: all 24h
OTHER TEST CONDITIONS
- Sterile test conditions: yes/no: no information
- Adjustment of pH: To avoid a high pH increase, 700 ml deionised water were mixed with 6 mL sodium hydrogencarbonate solution (50 g/L). Then, pH was adjusted to 7.0 (±0.2) with HCl.
- Photoperiod: 72 hours
- Light intensity and quality: 5800 – 5900 Lux
- Salinity (for marine algae): not applicable
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: spectrophotometer
- Chlorophyll measurement: no - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 8.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 8.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 8.6 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 19 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 19 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 19 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 58 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 23 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 25 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- dissolved
- Remarks:
- dissolved organic carbon
- Basis for effect:
- other: yield
- Duration:
- 72 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 63 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- other: dissolved organic carbon
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 63 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- other: dissolved organic carbon
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 63 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- other: dissolved organic carbon
- Basis for effect:
- other: yield
- Results with reference substance (positive control):
- NOEC 72 h 0.4 mg/L
LOEC 72 h 0.63 mg/L
72h ErC50 2.0 mg/L
72h EbC50 0.49 mg/L
72h EyC50 0.34 mg/L - Reported statistics and error estimates:
- For the treatments with the nominal test item concentrations 18 and 32 mg/L (measured concentrations 8.6 and 18.7 mg/L), it was tested whether the differences between treatment and control were significant. The values for the area under the curve, yield and the growth rate were used for the assessment of observed effect levels.
In order to select a suitable test for significance, it was checked whether equality of variance was given.
The calculated value F is compared with the F-test table (level of significance 95%). If the calculated value is smaller than the tabular value, equality of variance is given. If equality of variance is given, the t-test is used; else, the WEIR test is used. With the t-Test it was checked whether the differences are significant. Significance is given if the calculated t-value is bigger than the limit of significance (t-value taken from the table with grade of freedom: n1 + n2 – 2, level of significance 95%).
Determination of the NOEC
For the endpoints µ, AUC and yield, the differences between the treatment 18 mg/L (measured concentration 8.6 mg/L) and the control can be considered as not significant (level of significance: 97.5%) as the calculated t-values were smaller than the limit of significance. Therefore, the measured concentration 8.6 mg/L is stated as NOEC for these endpoints.
Determination of the LOEC
For the endpoints µ, AUC and yield, the differences between the treatment 32 mg/L (measured concentration 18.7 mg/L) and the control must be considered as significant (level of significance: 97.5%), the measured concentration 18.7 mg/L can be stated as LOEC for these endpoints.
The estimation of the EC50s of the test item was accomplished using the software OriginTM. - Validity criteria fulfilled:
- yes
- Remarks:
- except for the pH in the reference study
- Conclusions:
- The following results for the test item "2-propanol and 2-butanol production, distn. residues" were determined:
The NOECs of the growth rate, AUC and yield were 8.6 mg/L and the LOECs 19 mg/L. The EC50 value for the growth rate was 58 mg/L, for the AUC 23 mg/L and for the yield also 23 mg/L.
Based on these data in combination with the fact that the substance is not readily biodegradable, a classification into aquatic chronic category 3 (H412) (corresponding to R52/53) is necessary (EC50 band 10 - 100 mg/L). - Executive summary:
The 72h-EC50 of reaction mass of "2-propanol and 2-butanol production, distn. residues" (main constituent 2,2'-oxybisbutane (DSBE), DIPE, SBA and 2 -methylpropan-2 -ol (TBA)) against Desmodesmus subspicatus was determined according to OECD 201 resp. EU C.3.
One valid main study was performed.
The study was performed using five concentrations ranging from 10 to 100 mg/L. The treatments were used to incubate the unicellular freshwater green alga Desmodesmus subspicatus for a period of 72 hours. The cell concentration of each replicate was determined by measuring the absorption of the cuvettes at 440 nm every 24 hours with a spectral photometer. With these measured values, the number of cells was calculated (linear correlation between cell concentration and absorption given). Then the growth rate µ, the area under the growth curve (AUC [1]) and the Yield [2] were determined.
At the beginning and at the end of the test, the content of test item was determined by DOC-determination in the test solutions. The content of the test item was calculated from content of organic carbon of the test item (76 %) The recovery after 72 hours ranged from 64 to 93 % of the start concentration. The correlation between nominal and measured concentration was poor. Therefore, the geometric mean of the measured concentration was used for the determination of the biological results and the determination of the biological results was based on the mean of the measured concentrations.
The EC50s of potassium dichromate were tested in a current reference test. The values lay within the normal range of the laboratory.
The following results for the test item "2-propanol and 2-butanol production, distn. residues" were determined:
Growth Rate: NOEC 8.6 mg/L, LOEC 19 mg/L, EC50 58 mg/L
AUC: NOEC 8.6mg/L, LOEC 19 mg/L, EC50 23 mg/L
Yield: NOEC 8.6mg/L, LOEC 19 mg/L, EC50 25 mg/L
[1] AUC1 (Area Under Curve according to EU Method C.3) means the integral of the biomass.
[2] Yield (according to OECD Guideline 201) is defined as the biomass at the end of the exposure period minus the biomass at the start of the exposure period.
Reference
Main Study
Cell Numbers
The cell numbers were determined by photometric measurement of optical density. The means and standard deviations of the cell numbers of the control and the treatments are presented in the following table:
Cell Number/mL Main Study
Nominal Concentration in mg/L |
Parameter |
Cell Number/mL |
|||
|
|
0 h |
24 h |
48 h |
72 h |
0 |
Mean |
7354 |
24513 |
106633 |
486590 |
0 |
SD |
0 |
6005 |
12084 |
48873 |
10 |
Mean |
7354 |
22062 |
115213 |
563807 |
10 |
SD |
0 |
0 |
22467 |
88350 |
18 |
Mean |
7354 |
24513 |
151983 |
720692 |
18 |
SD |
0 |
4246 |
4246 |
36770 |
32 |
Mean |
7354 |
25739 |
73540 |
290483 |
32 |
SD |
0 |
5200 |
10400 |
98801 |
56 |
Mean |
7354 |
17159 |
26965 |
88248 |
56 |
SD |
0 |
4246 |
15309 |
44733 |
100 |
Mean |
7354 |
9805 |
12257 |
75991 |
100 |
SD |
0 |
4246 |
8492 |
29721 |
SD = Standard Deviation
Temperature, Light Intensity, pH
The pH values in the control ranged from 7.0 to 9.0. The light intensity was in a range of 5800 – 5900 lux. Temperature range was 24.0 – 27.0 °C. The details are given in the following table:
Temperature, Light Intensity, pH Main Study
|
0 h |
24 h |
48 h |
72 h |
|
Temperature [°C] |
24 |
25 |
24 |
27 |
|
Light intensity [lux] |
5800 |
5800 |
5900 |
5900 |
|
pH |
Conc. in mg/L |
|
- |
- |
|
|
0 |
7.0 |
- |
- |
9.0 |
|
10 |
7.0 |
- |
- |
9.5 |
|
18 |
7.0 |
|
|
9.5 |
|
32 |
7.0 |
|
|
9.1 |
|
56 |
7.0 |
- |
- |
7.3 |
|
100 |
7.0 |
- |
- |
7.1 |
Microscopical Observations
In the following table, the appearance of the alga at the end of the test is stated:
Microscopical Observation Main Study
Nom. Conc. in mg/L |
Observation |
0 |
normal growth |
10 |
normal growth |
18 |
normal growth |
32 |
smaller cells |
56 |
no cells |
100 |
no cells |
Analytical Determination
The measured and calculated concentrations for treatment and control are given in the following table. The concentration of test item was calculated through measured DOC divided by the content of organic carbon (76%) of the test item.
DOC Values and Recovery
Nominal Conc. mg/L |
DOC mg/L |
Test item mg/L |
% of Nominal |
DOC mg/L |
Test item mg/L |
% of Nominal |
% Recovery |
Geom. Mean of Test Item mg/L |
0h |
72h |
|||||||
0 |
2.34 |
- |
- |
2.33 |
- |
- |
- |
- |
10 |
6.82 |
8.97 |
90% |
4.37 |
5.75 |
58% |
64% |
7.18 |
18 |
6.82 |
8.97 |
50% |
6.31 |
8.30 |
46% |
93% |
8.63 |
32 |
15.25 |
20.07 |
63% |
13.24 |
17.42 |
54% |
87% |
18.70 |
56 |
32.46 |
42.71 |
76% |
29.03 |
38.20 |
68% |
89% |
40.39 |
100 |
54.05 |
71.12 |
71% |
42.85 |
56.38 |
56% |
79% |
63.32 |
Area under the Curve, Growth Rate, Yield
From the cell numbers, the Growth Rate µ, the Area under the Curve AUC, and the Yield were calculated. The means and standard deviations at the end of the test are given in the following table:
Growth Rate µ, Area under the Curve AUC, Yield Main Study
Nom. Concentration in mg/L |
Meas. Concentration in mg/L |
|
Growth Rate [day-1] |
AUC |
Yield |
0 |
|
Mean |
1.40 |
356056 |
479236 |
SD |
0.04 |
41236 |
48873 |
||
10 |
7.2 |
Mean |
1.44 |
400793 |
556453 |
SD |
0.05 |
66492 |
88350 |
||
18 |
8.6 |
Mean |
1.53 |
518457 |
713338 |
SD |
0.02 |
22963 |
36770 |
||
32 |
18.7 |
Mean |
1.22 |
226136 |
283129 |
SD |
0.12 |
65001 |
98801 |
||
56 |
40.4 |
Mean |
0.80 |
69863 |
80894 |
SD |
0.16 |
41763 |
44733 |
||
100 |
63.3 |
Mean |
0.76 |
41673 |
68637 |
SD |
0.12 |
27598 |
29721 |
SD = Standard Deviation
Reference Study
Cell Numbers
The cell numbers were determined by photometric measurement of optical density. The means and standard deviations of the cell numbers of the control and the treatments are presented in the following table:
Cell Number/mL Reference Study
Nominal Concentration in mg/L |
Parameter |
Cell Number/mL |
|||
|
|
0 h |
24 h |
48 h |
72 h |
0 |
Mean |
7354 |
60303 |
238270 |
760404 |
0 |
SD |
0 |
9588 |
69882 |
187966 |
0.04 |
Mean |
7354 |
63735 |
230425 |
823648 |
0.04 |
SD |
0 |
8492 |
4246 |
19457 |
0.063 |
Mean |
7354 |
66186 |
227974 |
728046 |
0.063 |
SD |
0 |
0 |
7354 |
74635 |
0.1 |
Mean |
7354 |
58832 |
166691 |
539293 |
0.1 |
SD |
0 |
7354 |
48965 |
176700 |
0.16 |
Mean |
7354 |
51478 |
134823 |
485364 |
0.16 |
SD |
0 |
19457 |
73662 |
247099 |
0.25 |
Mean |
7354 |
56381 |
149531 |
436337 |
0.25 |
SD |
0 |
4246 |
74029 |
276077 |
0.4 |
Mean |
7354 |
71089 |
174045 |
509877 |
0.4 |
SD |
0 |
4246 |
4246 |
29721 |
0.63 |
Mean |
7354 |
61283 |
115213 |
296611 |
0.63 |
SD |
0 |
4246 |
8492 |
15309 |
1.0 |
Mean |
7354 |
53929 |
83345 |
98053 |
1.0 |
SD |
0 |
4246 |
18507 |
16983 |
1.6 |
Mean |
7354 |
58832 |
56381 |
83345 |
1.6 |
SD |
0 |
0 |
8492 |
8492 |
SD = Standard Deviation
Area under the Curve, Growth Rate, Yield
From the cell numbers, the Growth Rate µ, the Area under the Curve AUC, and the Yield were calculated. The means and standard deviations at the end of the test are given in the following table:
Growth Rate µ, Area under the Curve AUC, Yield Reference Study
Nominal Concentration in mg/L |
|
Growth Rate [day-1] |
AUC |
Yield |
0 |
Mean |
1.54 |
660389 |
753050 |
SD |
0.09 |
166860 |
187966 |
|
0.04 |
Mean |
1.57 |
687599 |
816294 |
SD |
0.01 |
18385 |
19457 |
|
0.063 |
Mean |
1.53 |
639798 |
720692 |
SD |
0.03 |
42405 |
74635 |
|
0.1 |
Mean |
1.42 |
476784 |
531939 |
SD |
0.11 |
138039 |
176700 |
|
0.16 |
Mean |
1.36 |
410598 |
478010 |
SD |
0.18 |
215107 |
247099 |
|
0.25 |
Mean |
1.31 |
405696 |
428983 |
SD |
0.22 |
215327 |
276077 |
|
0.4 |
Mean |
1.41 |
481687 |
502523 |
SD |
0.02 |
13258 |
29721 |
|
0.63 |
Mean |
1.23 |
306417 |
289257 |
SD |
0.02 |
18869 |
15309 |
|
1.0 |
Mean |
0.86 |
167916 |
90699 |
SD |
0.06 |
25826 |
16983 |
|
1.6 |
Mean |
0.81 |
138500 |
75991 |
SD |
0.04 |
11233 |
8492 |
Inhibition
The following mean inhibition values were calculated for the Growth Rate µ, the Area under the Curve AUC, and the yield. Individual inhibition values are given in the annex.
Inhibition Values Reference Study
Nominal Concentration in mg/L |
% Inhibition |
||
Growth Rate µ |
Area under the Curve AUC |
Yield |
|
0 |
0! |
0! |
0! |
0.04 |
-2.36 |
-4.12 |
-8.40 |
0.063 |
0.39 |
3.12 |
4.30 |
0.1 |
7.63 |
27.80 |
29.36 |
0.16 |
11.16 |
37.82 |
36.52 |
0.25 |
14.56 |
38.57 |
43.03 |
0.4 |
8.06 |
27.06 |
33.27 |
0.63 |
19.81 |
53.60 |
61.59 |
1.0 |
44.01 |
74.57 |
87.96 |
1.6 |
47.41 |
79.03 |
89.91 |
Description of key information
The following results were determined for the test item "2-propanol and 2-butanol production, distn. residues" (species: Desmodesmus subspicatus): 72h-ErC50 (growth rate) = 58 mg/L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 58 mg/L
- EC10 or NOEC for freshwater algae:
- 8.6 mg/L
Additional information
The EC50 value and the NOEC for growth inhibition, AUC and yield of "2 -propanol and 2 -butanol, distn residues" was measured according to OECD 201, respectively EU C.3 guideline under GLP. Following results were obtained:
Endpoint |
NOEC |
LOEC |
EC50 |
Growth Rate |
8.6 mg/L |
19 mg/L |
58 mg/L |
AUC |
8.6 mg/L |
19 mg/L |
23 mg/L |
Yield |
8.6 mg/L |
19 mg/L |
25 mg/L |
The analytical determinations of the test item showed poor correlation between nominal and measured concentrations and acceptable recovery rates. The poor correlation is probably caused by the high volatility of the test item. Therefore, the determination of the results of the test item "2 -propanol and 2 -butanol, distn. residues" was based on the geometric means of the measured concentrations.
Based on these data in combination with the fact that the substance is not readily biodegradable, a classification into aquatic chronic category 3 (H412) according to the CLP regulation (corresponding to R52/53) is necessary (EC50 10 - 100 mg/L).
Based on the lowest EC50 value of three species daphnia, algae and fish (available studies), an aquatic PNEC value was calculated for the risk assessment. As values from algae test based on growth rate, not on biomass or yield, should be employed for classification and risk assessment, the relevant EC50 value is 58 mg/L. Therefore, the value for algae does not represent the lowest value of three species daphnia, algae and fish.
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