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EC number: 223-517-5 | CAS number: 3937-56-2
- 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:
- 2004-01-27 to 2004-01-30
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Version / remarks:
- June 1984
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- Updating 29 December 1992
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 850.5400 (Algal Toxicity, Tiers I and II) (January 2012)
- Version / remarks:
- Public Draft, April 1996
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No.of test material: batch No. 42638, substance no. 03/0183-1
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: ambient, under N2
- Stability under test conditions: The stability of the test substance under storage conditions over the exposure period was confirmed by reanalysis
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: Before weighting the test substance was melted in water quench at circa 60°C for circa 1.5 hours.
FORM AS APPLIED IN THE TEST (if different from that of starting material): liquid - Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0, 1.56, 6.25, 25 and 100 mg/L, after 0 hours (start of exposure) and 72 h (end of exposure)
- Sampling method: Twenty milliliters (20 mL) samples were applied onto SPE-columns (solid phase extraction column, Chromabond easy). The columns were then eluted with five 5 mL acetonitrile each. Aliquots of the solutions were used for GC - analysis.
- Sample storage conditions before analysis: None (analyzed immediately after sample delivery) - Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: A stock solution of 125.4 mg/L was freshly prepared. Before weighting the test substance was melted in water quench at circa 60°C for circa 1.5 hours. Circa 800 mL deion. water were put into 1000 mL flask .The water was stirred and heat to circa 60°C. The test substance (125 mg/L) was weighed on plastic pad and put into the flask. The flask was filled to 1000 mL with deion. water. The stock solution was stirred circa 0.5 hours.
- Evidence of undissolved material (e.g. precipitate, surface film, etc.): The stock solution was clear. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green algae
- Strain: CHODAT SAG 86.81
- Source (laboratory, culture collection): The test strain of Desmodesmus subspicatus CHODAT SAG 86.81 is obtained at regular intervals from SAG (Sammlung von Algenkulturen/Collection of algal cultures in Göttingen) and is kept in liquid culture in the Laboratory of Experimental Toxicology and Ecology.
- Age of inoculum (at test initiation): 3 days
- Method of cultivation:
seed-culture: A seed culture was incubated for 4 days at 23 ± 2°C final cell density: 78 x 10^4 ceIls/mL
pre-culture: Seed-culture was taken to inoculate a pre-culture (initial cell density: 1 x 10^4 cells/mL). The pre-culture was incubated for 3 days at 23 ± 2°C. Final celI density: 36 x 10^4 cells/mL.
ACCLIMATION
- Culturing media and conditions (same as test or not): same as test - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 23 ± 2°C
- pH:
- 8 - 8.2
After 0 h and 72 h in an additional uninoculated replicate and after 72 h in the inoculated replicate No. 1 of each concentration. - Nominal and measured concentrations:
- nominal: 0 (control), 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50, 100 mg/L
measured: The concentration control analyses were performed with test solutions of the following nominal concentrations of the test substance (mg/L):
0 (control) = < LOQ
1.56 = 1.46 (mean of measured concentration d0)
6.25 = 5.60 (mean of measured concentration d0)
25 = 22.60 (mean of measured Ohconcentration d0)
100 = 102.59 (mean of measured concentration d0)
The analytical recovery rates in the range of the EC-values were > 80%. Therefore no transformation of the nominal EC-values into the values of the concentration control analysis occurs. - Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flasks (nominal volume 250 mL)
- Type: closed, plugged with gas permeable siliconsponge caps
- Material, size, headspace, fill volume: Size: 250 mL, fill volume: 100 mL
- Initial cells density: 1 x 10^4 cells/mL
- Control end cells density: The cell multiplication factor in the untreated control was after 72 hours: 28-fold (counted).
- No. of vessels per concentration (replicates): 3 replicates
- No. of vessels per control (replicates): 3 replicates
GROWTH MEDIUM
- Standard medium used: yes (OECD medium)
OTHER TEST CONDITIONS
- Sterile test conditions: no
- Adjustment of pH: no
- Photoperiod: permanent illumination
- Light intensity and quality: artificial light, type universal white (OSRAM L 25), about 60 - 120 µE/(m^2*s) at a wave length of 400 - 700 nm
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: After 72 h in a counting chamber (Neubauer improved)
- Chlorophyll measurement: in vivo chlorophyll-a-fluorescence (pulsed excitation with light flashes having a wavelength of 435 nm), after 0, 24, 48 and 72 h
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study: yes (non-GLP) - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 24.8 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 72 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- EC10
- Effect conc.:
- 53.9 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 50 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- - Observation of abnormalities (for algal test): no information available
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- EC50 (72h): 0.42 mg/L - Validity criteria fulfilled:
- yes
- Conclusions:
- The toxicity of Nonane-1,9-diol on Desmodesmus subspicatus was determined in a reliable GLP study according to OECD 201. The algae were exposed to 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50 and 100 mg/L of Nonane-1,9-diol for 72 hours. The concentrations were analytically verified via GC-FIS and recovery rates were > 80%. Therefore, results were given based on nominal concentrations. Inhibition of growth rate (ErC50) and biomass (EyC50) of the algae were observed at > 100 mg/L and 72 mg/L, respectively. The NOEC and LOEC of both, inhibition of growth rate and biomass, were 50 mg/L and 100 mg/L, respectively.
Reference
Table 1: Analytical recovery rates (%)
time (h) |
inoculation |
Test solution |
|
minimum |
maximum |
||
0 |
yes |
89.6 |
102.6 |
72 |
yes |
72.3 |
120.9 |
Table 2: pH values at the start (t = 0 h) and at the end (t = 72 h) of the test (pa = parallel)
Concentration (mg/L) |
uninoculated (pa.5) 0 h |
uninoculated (pa.6) 72 h |
inoculated (pa.1) 72 h |
0 (control) |
8.0 |
8.0 |
8.1 |
100 |
8.0 |
8.1 |
8.1 |
50 |
8.0 |
8.1 |
8.1 |
25 |
8.0 |
8.1 |
8.2 |
12.5 |
8.0 |
8.1 |
8.1 |
6.25 |
8.0 |
8.1 |
8.1 |
3.13 |
8.0 |
8.1 |
8.1 |
1.56 |
8.1 |
8.1 |
8.1* |
0.781 |
8.1 |
8.1 |
8.1 |
0.391 |
8.1 |
8.1 |
8.1 |
Remark: * inoculated parallel 4
Table 3 – Test Data: Measured fluorescence (relative units) after 0 h, 24 h, 48 h and 72 h
time (h) |
flask No. |
concentration (mg/L) |
|||||||||
0 (control) |
100 |
50 |
25 |
12.5 |
6.25 |
3.13 |
1.56 |
0.781 |
0.391 |
||
0 |
1 |
38 |
39 |
38 |
38 |
35 |
38 |
38 |
37 |
38 |
37 |
2 |
38 |
39 |
38 |
39 |
35 |
37 |
39 |
37 |
37 |
37 |
|
3 |
37 |
38 |
40 |
39 |
35 |
37 |
38 |
37 |
37 |
38 |
|
no |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
24 |
1 |
140 |
85 |
120 |
140 |
120 |
130 |
140 |
120 |
140 |
150 |
2 |
130 |
86 |
120 |
140 |
120 |
120 |
130 |
130 |
140 |
140 |
|
3 |
130 |
80 |
110 |
130 |
130 |
130 |
130 |
130 |
130 |
150 |
|
no |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
48 |
1 |
600 |
140 |
500 |
540 |
530 |
670 |
570 |
570 |
620 |
530 |
2 |
550 |
140 |
430 |
430 |
580 |
510 |
530 |
540 |
550 |
680 |
|
3 |
530 |
140 |
440 |
500 |
510 |
520 |
490 |
540 |
540 |
550 |
|
no |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|
72 |
1 |
1240 |
230 |
1120 |
1040 |
1260 |
1940 |
1280 |
1620 |
1230 |
980 |
2 |
1040 |
200 |
860 |
990 |
1980 |
920 |
1160 |
940 |
1090 |
1680 |
|
3 |
970 |
220 |
820 |
930 |
1030 |
960 |
890 |
990 |
980 |
1000 |
|
no |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Table 4: Test Results: CeII density after 0 h, 24 h, 48 h and 72 h
The measured fluorescence was corrected by the fluorescence of the test substance and converted into celI densities (cells x 1 0000/mL) by the following correlation:
ceII density (cells x 10000/mL) = fluorescence (relative units) / slope (m); m = 22.779
The linear correlation was obtained from a calibration curve (cell density versus fluorescence).
time (h) |
flask No. |
concentration (mg/L) |
|||||||||
0 (control) |
100 |
50 |
25 |
12.5 |
6.25 |
3.13 |
1.56 |
0.781 |
0.391 |
||
0 |
1 |
1.7 |
1.7 |
1.7 |
1.7 |
1.5 |
1.7 |
1.7 |
1.6 |
1.7 |
1.6 |
2 |
1.7 |
1.7 |
1.7 |
1.7 |
1.5 |
1.6 |
1.7 |
1.6 |
1.6 |
1.6 |
|
3 |
1.6 |
1.7 |
1.8 |
1.7 |
1.5 |
1.6 |
1.7 |
1.6 |
1.6 |
1.7 |
|
mean |
1.7 |
1.7 |
1.7 |
1.7 |
1.5 |
1.6 |
1.7 |
1.6 |
1.6 |
1.6 |
|
24 |
1 |
6.1 |
3.7 |
5.3 |
6.1 |
5.3 |
5.7 |
6.1 |
5.3 |
6.1 |
6.6 |
2 |
5.7 |
3.8 |
5.3 |
6.1 |
5.3 |
5.3 |
5.7 |
5.7 |
6.1 |
6.1 |
|
3 |
5.7 |
3.5 |
4.8 |
5.7 |
5.7 |
5.7 |
5.7 |
5.7 |
5.7 |
6.6 |
|
mean |
5.9 |
3.7 |
5.1 |
6.0 |
5.4 |
5.6 |
5.9 |
5.6 |
6.0 |
6.4 |
|
48 |
1 |
26.3 |
6.1 |
22.0 |
23.7 |
23.3 |
29.4 |
25.0 |
25.0 |
27.2 |
23.3 |
2 |
24.1 |
6.1 |
18.9 |
18.9 |
25.5 |
22.4 |
23.3 |
23.7 |
24.1 |
29.9 |
|
3 |
23.3 |
6.1 |
19.3 |
22.0 |
22.4 |
22.8 |
21.5 |
23.7 |
23.7 |
24.1 |
|
mean |
24.6 |
6.1 |
20.0 |
21.5 |
23.7 |
24.9 |
23.3 |
24.1 |
25.0 |
25.8 |
|
72 |
1 |
54.4 |
10.1 |
49.2 |
45.7 |
55.3 |
85.2 |
56.2 |
71.1 |
54.0 |
43.0 |
2 |
45.7 |
8.8 |
37.8 |
43.5 |
86.9 |
40.4 |
50.9 |
41.3 |
47.9 |
73.8 |
|
3 |
42.6 |
9.7 |
36.0 |
40.8 |
45.2 |
42.1 |
39.1 |
43.5 |
43.0 |
43.9 |
|
mean |
47.6 |
9.5 |
41.0 |
43.3 |
62.5 |
55.9 |
48.7 |
51.9 |
48.3 |
53.6 |
Table 5 - Test Results: Calculation of biomass and inhibition of biomass after 72 h
parameter |
flask No. |
concentration (mg/L) |
|||||||||
0 (control) |
100 |
50 |
25 |
12.5 |
6.25 |
3.13 |
1.56 |
0.781 |
0.391 |
||
biomass [rel] |
1 |
56 |
11 |
48 |
49 |
52 |
74 |
55 |
62 |
56 |
47 |
2 |
49 |
10 |
39 |
42 |
70 |
44 |
50 |
46 |
50 |
69 |
|
3 |
46 |
10 |
38 |
44 |
47 |
46 |
43 |
47 |
47 |
49 |
|
mean |
50 |
10 |
41 |
45 |
57 |
54 |
49 |
52 |
51 |
55 |
|
Inhibition [%] |
|
0.0 |
79.4 |
17.3 |
10.3 |
-12.9 |
-8.4 |
1.6 |
-3.1 |
-2.0 |
-9.6 |
Table 6 - Test Results: Calculation of growth rate and inhibition of growth rate after 72 h
parameter |
flask No. |
concentration (mg/L) |
|||||||||
0 (control) |
100 |
50 |
25 |
12.5 |
6.25 |
3.13 |
1.56 |
0.781 |
0.391 |
||
growth rate [rel] |
1 |
0.0484 |
0.0246 |
0.0470 |
0.0460 |
0.0498 |
0.0546 |
0.0488 |
0.0525 |
0.0483 |
0.0455 |
2 |
0.0460 |
0.0227 |
0.0433 |
0.0449 |
0.0560 |
0.0446 |
0.0471 |
0.0449 |
0.0470 |
0.0530 |
|
3 |
0.0454 |
0.0244 |
0.0420 |
0.0441 |
0.0470 |
0.0452 |
0.0438 |
0.0456 |
0.0455 |
0.0454 |
|
mean |
0.0466 |
0.0239 |
0.0441 |
0.0450 |
0.0509 |
0.0482 |
0.0466 |
0.0477 |
0.0469 |
0.0480 |
|
Inhibition [%] |
|
0.0 |
48.7 |
5.3 |
3.4 |
-9.3 |
-3.4 |
0.0 |
-2.4 |
-0.8 |
-3.0 |
Description of key information
Effect on growth rate:
ErC10 (72 h) = 53.9 mg/L
ErC50 (72 h) > 100 mg/L
NOEC (72 h) = 50 mg/L
LOEC (72 h) = 100 mg/L
Effect on biomass:
EyC10 (72 h) = 24.8 mg/L
EyC50 (72 h) = 72.0 mg/L
NOEC (72 h) = 50 mg/L
LOEC (72 h) = 100 mg/L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
- EC10 or NOEC for freshwater algae:
- 53.9 mg/L
Additional information
The toxicity of Nonane-1,9-diol on Desmodesmus subspicatus was determined in a reliable GLP study according to OECD 201. The algae were exposed to 0.391, 0.781, 1.56, 3.13, 6.25, 12.5, 25, 50 and 100 mg/L of Nonane-1,9-diol for 72 hours. The concentrations were analytically verified via GC-FIS and recovery rates were > 80%. Therefore, results were given based on nominal concentrations. Inhibition of growth rate (ErC50) and biomass (EyC50) of the algae were observed at > 100 mg/L and 72 mg/L, respectively. The NOEC and LOEC of both, inhibition of growth rate and biomass, were 50 mg/L and 100 mg/L, respectively.
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