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EC number: 700-835-7 | CAS number: 919005-14-4
- 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:
- 26 February 2007 - 02 March 2007
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study conducted under GLP. Study on ammonium salt.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: EEC directive 92/69, Part C.3, 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: ISO International Standard 8692:2004
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- ADONA
- IUPAC Name:
- ADONA
- Details on test material:
- - Name of test material (as cited in study report): MTDID 6675
- Substance type: single-constituent substance
- Physical state: clear colorless liquid
- Analytical purity: 29.9 ±0.1% in water
- Lot/batch no.: 140499-19/10
- Stability under test conditions: Stable in water at least 96 hours
- Storage condition of test material: At room temperature in the dark
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling method: At the end of the exposure period, the replicates with algae were pooled at each concentration before sampling. Control and test substance vessels had 2 mL aliquots taken at 0h, 24h, and 96h.
- Sample storage conditions before analysis: Samples were stored in a freezer until analysis.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
Method: ADONA consists of 29.9% active ingredient (a.i.) in water. The lower concentrations were prepared by subsequent dilutions of the highest test concentration (334 mg/L in test medium). No special treatment other than a short magnetic stirring period was necessary to completely dissolve the test substance in the test medium.
- Controls: Test medium without test substance or other additives
- Evidence of undissolved material (e.g. precipitate, surface film, etc): None, final test solutions were all clear and colorless.
Test organisms
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Details on test organisms:
- TEST ORGANISM
- Common name: Green algae
- Strain: NIVA CHL 1
- Source (laboratory, culture collection): In-house laboratory culture
- Age of inoculum (at test initiation): 3 days before the start of the test, cells from the algal stock culture were inoculated in culture medium at a cell density of 1E+04 cells/ml. The pre-culture was maintained under the same conditions as used in the test. The cell density was measured immediately before use.
- Method of cultivation: Algae stock cultures were started by inoculating growth medium with algal cells from a pure culture on agar. The suspensions were continuously aerated and exposed to light in a climate room at a temperature of 21-24°C.
ACCLIMATION
- Acclimation period: None
- Culturing media and conditions (same as test or not): cultures maintained under the same conditions as those used for testing.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Remarks on exposure duration:
- Combined limit/range-finding test
Test conditions
- Hardness:
- 24 mg/L CaCO3
- Test temperature:
- 22.1 - 22.5 °C
- pH:
- 8.0 - 9.9
- Nominal and measured concentrations:
- Nominal concentrations: 0.334, 3.34, 33.4, and 334 mg/L
Corresponding to analytically confirmed active ingredient concentrations: 0.1, 1.0, 10, and 100 mg a.i./L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 100 mL all-glass container, 50 mL fill volume
- Agitation: Yes, during incubation the algal cells were kept in suspension by continuous shaking
- Initial cells density: 1E+04 cells/mL
- Control end cells density: 742.4E+04 cells/mL
- No. of vessels per concentration (replicates): 3 (each treatment group except the highest, with algae), 1 (each treatment group, without algae), 6 (highest concentration), 1 (each test group for sampling)
- No. of vessels per control (replicates): 6
GROWTH MEDIUM
- Standard medium used: Yes, M1
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Tap water purified by reverse osmosis; (Milli-RO water, Millipore Corp., Bedford, Mass., USA)
- Culture medium different from test medium: yes, propagation in M1, pre-culture established in M2 medium 3 days before test initiation to use in test, test in M2
- Intervals of water quality measurement: pH at beginning and end of test, temperature continuously
OTHER TEST CONDITIONS
- Adjustment of pH: No
- Photoperiod: Continuous using TLD-lamps (cool-white)
- Light intensity and quality: 30 Watt, with a light intensity within the range of 78 - 84 µE/(m²∙s)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- Determination of cell concentrations: Cell counts at 0h were determined using a microscope and a counting chamber. For 24h, 48h, and 72h samples, they were determined by spectrophotometric measurement at 720 nm using a Varian Cary 50 single beam spectrophotometer with immersion probe (pathlength = 20 mm). Algal medium was used as a blank and the extra replicates as background for the treated solutions.
- Other: Appearance of cells were preformed at the end of the test by microscope to verify appearance of the inoculum culture and to observe for any abnormal appearance of the algae. TEST CONCENTRATIONS - Spacing factor for test concentrations: 1.8 - Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate K2Cr2O7
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth rate
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- growth rate
- Remarks on result:
- other: Exposure concentrations were based on nominal concentrations as analytical results showed that concentrations were stable and in agreement with nominal (with and without algae) within 99 -112% during the 96h test period.
- Details on results:
- - Exponential growth in the control (for algal test): yes/no: Yes (Figure 1)
- Growth in controls (validity criteria):
- cell density increase to hour 48: factor of >16
- % Coefficient of variance in average specific growth rate at hour 96: 1% (Table 1)
- % Coefficient of variance in section-specific growth rates to hour 96: ≤ 7% (Table 2)
Test concentrations and effect parameters can be found in Table 3 and Table 4, respectively.
- Any visual signs of phytotoxicity (abnormalities): None noted
- Any stimulation of growth found in any treatment: No
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: No - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- 72h ErC50: 2.0 mg/L, 95% C.I. 1.7 - 2.4 mg/L. The historical ranges for growth rate reduction for Pseudokirchneriella subcapitata lie between 0.82 and 2.3 mg/l. Hence, the growth rate reduction 72h ErC50 for the Pseudokirchneriella subcapitata tested corresponds with this range. - Reported statistics and error estimates:
- Statistical analysis of the data was not needed as the effects recorded were not significant (<10%). No EC50-values could be calculated because the test substance proved to be non-toxic (EC50> maximum concentration test substance).
Any other information on results incl. tables
Table 1. Cell Density, Yield Inhibition, and Growth Rate Reductions |
||||||||||
Nominal Concentration¹ ADONA [mg/L] |
Vessel Number |
Individual Cell Densities [104cells/mL] |
Yield |
Yield Inhibition [%] |
Growth Rate [µ] |
Growth Rate Reduction [%] |
||||
0h |
24h |
48h |
72h |
96h |
0-96h |
0-96h |
0-96h |
0-96h |
||
1 |
1 |
7.31 |
44.00 |
240.41 |
757.16 |
756.16 |
0.06906 |
|||
2 |
1 |
7.28 |
37.58 |
238.96 |
725.58 |
724.58 |
0.06861 |
|||
3 |
1 |
7.38 |
37.74 |
255.30 |
797.60 |
796.60 |
0.06960 |
|||
Control |
4 |
1 |
8.35 |
47.80 |
278.67 |
782.14 |
781.14 |
0.06940 |
||
5 |
1 |
8.13 |
34.35 |
257.46 |
697.06 |
696.06 |
0.06820 |
|||
6 |
1 |
8.68 |
45.02 |
247.45 |
694.98 |
693.98 |
0.06817 |
|||
Mean |
741.42 |
0.06884 |
||||||||
CV |
1% |
|||||||||
1 |
1 |
9.85 |
44.38 |
249.78 |
681.44 |
680.44 |
8 |
0.06796 |
1 |
|
0.1 |
2 |
1 |
8.76 |
41.69 |
235.24 |
749.92 |
748.92 |
-1 |
0.06896 |
0 |
(0.334) |
3 |
1 |
9.46 |
45.30 |
278.14 |
767.18 |
766.18 |
-3 |
0.06920 |
-1 |
Mean |
731.85 |
1.3 |
0.06870 |
0.2 |
||||||
1 |
1 |
8.49 |
46.65 |
261.18 |
787.94 |
786.94 |
-6 |
0.06947 |
-1 |
|
1.0 |
2 |
1 |
8.05 |
47.84 |
251.57 |
762.86 |
761.86 |
-3 |
0.06914 |
0 |
(3.34) |
3 |
1 |
8.08 |
41.22 |
243.02 |
697.46 |
696.46 |
6 |
0.06820 |
1 |
Mean |
748.42 |
-0.9 |
0.06894 |
-0.1 |
||||||
1 |
1 |
8.00 |
62.89 |
248.56 |
680.30 |
679.30 |
8 |
0.06794 |
1 |
|
10 |
2 |
1 |
8.58 |
48.13 |
243.65 |
739.62 |
738.62 |
0 |
0.06881 |
0 |
(33.4) |
3 |
1 |
7.84 |
47.65 |
264.82 |
723.10 |
722.10 |
3 |
0.06858 |
0 |
Mean |
713.34 |
3.8 |
0.06845 |
0.6 |
||||||
1 |
1 |
8.04 |
49.17 |
252.29 |
740.90 |
739.90 |
0 |
0.06883 |
0 |
|
2 |
1 |
7.45 |
38.09 |
228.82 |
770.66 |
769.66 |
-4 |
0.06924 |
-1 |
|
3 |
1 |
7.89 |
38.38 |
225.05 |
659.48 |
658.48 |
11 |
0.06762 |
2 |
|
100 |
4 |
1 |
8.03 |
43.58 |
264.82 |
726.80 |
725.80 |
2 |
0.06863 |
0 |
(334) |
5 |
1 |
8.12 |
45.44 |
251.22 |
803.98 |
802.98 |
-8 |
0.06968 |
-1 |
6 |
1 |
8.11 |
47.17 |
255.17 |
728.68 |
727.68 |
2 |
0.06866 |
0 |
|
Mean |
737.42 |
0.5 |
0.06878 |
0.1 |
||||||
1) Analytically confirmed nominal concentrations of the active ingredient corrected for purity of the test product (29.9%). Nominal total product concentration in parentheses [mg/L]. |
Table 2 Growth rate: section-by-section |
|||||||||
Nominal Concentration¹ ADONA [mg/L]A |
Vessel Number |
Growth rate (µ) |
Growth rate reduction (%) |
||||||
0-24h |
24-48h |
48-72h |
72-96h |
0-24h |
24-48h |
48-72h |
72-96h |
||
1 |
0.08289 |
0.07479 |
0.07076 |
0.04780 |
|||||
2 |
0.08271 |
0.06839 |
0.07708 |
0.04628 |
|||||
3 |
0.08328 |
0.06800 |
0.07965 |
0.04747 |
|||||
Control |
4 |
0.08843 |
0.07270 |
0.07346 |
0.04300 |
||||
5 |
0.08732 |
0.06004 |
0.08393 |
0.04150 |
|||||
6 |
0.09004 |
0.06859 |
0.07100 |
0.04303 |
|||||
Mean |
0.08578 |
0.06875 |
0.07598 |
0.04485 |
|||||
CV% |
4 |
7 |
7 |
6 |
|||||
Mean CV for section-by-section specific growth rate was 6% |
|||||||||
1 |
0.09531 |
0.06272 |
0.07199 |
0.04182 |
-11 |
9 |
5 |
7 |
|
0.1 |
2 |
0.09042 |
0.06500 |
0.07210 |
0.04831 |
-5 |
5 |
5 |
-8 |
(0.334) |
3 |
0.09363 |
0.06526 |
0.07562 |
0.04227 |
-9 |
5 |
0 |
6 |
Mean |
0.09312 |
0.06433 |
0.07324 |
0.04413 |
-8.6 |
6.4 |
3.6 |
1.6 |
|
1 |
0.08912 |
0.07099 |
0.07177 |
0.04601 |
-4 |
-3 |
6 |
-3 |
|
1.0 |
2 |
0.08690 |
0.07426 |
0.06916 |
0.04622 |
-1 |
-8 |
9 |
-3 |
(3.34) |
3 |
0.08706 |
0.06790 |
0.07393 |
0.04393 |
-1 |
1 |
3 |
2 |
Mean |
0.08769 |
0.07105 |
0.07162 |
0.04539 |
-2.2 |
-3.3 |
5.7 |
-1.2 |
|
1 |
0.08664 |
0.08591 |
0.05726 |
0.04195 |
-1 |
-25 |
25 |
6 |
|
10 |
2 |
0.08956 |
0.07185 |
0.06758 |
0.04627 |
-4 |
-5 |
11 |
-3 |
(33.4) |
3 |
0.08580 |
0.07519 |
0.07147 |
0.04185 |
0 |
-9 |
6 |
7 |
Mean |
0.08733 |
0.07154 |
0.06543 |
0.04336 |
-1.8 |
-4.1 |
13.9 |
3.3 |
|
1 |
0.08685 |
0.07545 |
0.06814 |
0.04489 |
-1 |
-10 |
10 |
0 |
|
2 |
0.08368 |
0.06799 |
0.07471 |
0.05060 |
2 |
1 |
2 |
-13 |
|
100 |
3 |
0.08607 |
0.06591 |
0.07370 |
0.04480 |
0 |
4 |
3 |
0 |
(334) |
4 |
0.08680 |
0.07048 |
0.07519 |
0.04207 |
-1 |
-3 |
1 |
6 |
5 |
0.08726 |
0.07175 |
0.07125 |
0.04847 |
-2 |
-4 |
6 |
-8 |
|
6 |
0.08721 |
0.07336 |
0.07034 |
0.04372 |
-2 |
-7 |
7 |
3 |
|
Mean |
0.08631 |
0.07082 |
0.07222 |
0.04576 |
-0.6 |
-3.0 |
4.9 |
-2.0 |
|
1) Analytically confirmed concentrations of active ingredient, corrected for purity of the test product (29.9%). Nominal concentrations of total product presented in parentheses. |
Table 3. Concentrations of ADONA in test medium |
||||
Time of sampling (hours) |
Concentration¹ |
|||
Nominal (mg/L) |
Measured (mg/L) |
Relative to nominal (%) |
Relative to initial (%) |
|
0 |
n.d.² |
n.a.³ |
||
0 |
99.9 |
99.1 |
99 |
|
99.9 (abiotic) |
111 |
112 |
||
0 |
n.d.² |
n.a.³ |
||
24 |
99.9 |
104 |
104 |
105 |
99.9 (abiotic) |
109 |
109 |
98 |
|
0 |
n.d.² |
n.a.³ |
||
96 |
99.9 |
104 |
104 |
105 |
99.9 (abiotic) |
110 |
110 |
98 |
|
1) Concentrations for active ingredient, corrected for purity of test substance (29.9%) 2) Not detected 3) Not applicable Limit of detection (LOD): 0.0056 mg/L, taking a dilution factor of 2 into account |
Table 4. Effect parameters |
||
Parameter |
Concentration ADONA (mg/L) |
|
Total Product |
Active ingredient ¹ |
|
NOERC |
334 |
100 |
96h-ERC50 |
> 334 |
> 100 |
NOEYC |
334 |
100 |
96h-EYC50 |
> 334 |
> 100 |
1) Analytically confirmed nominal concentration of active ingredient corrected for purity of the test product (29.9%) |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- Control cell densities increased by avg. factor >16 within 2 days. Coefficient of variation of sec.-by-sec. growth during whole test in controls <35%. Coefficient of variation of avg. specific growth during whole test in replicate controls <7%.
- Conclusions:
- The 96-hour ErC50 of ADONA to Pseudokirchneriella subcapitata is >100 mg/L (as active ingredient). The 96-hour NOEC (growth rate) of ADONA to Pseudokirchneriella subcapitata is 100 mg/L (as active ingredient).
- Executive summary:
DONA is an acid with pKa ca.2 and will be entirely dissociated in aquatic systems. Aquatic toxicity testing would require neutralization of stock solutions, and DONA would in practice be testing of a neutral salt. This test examined the ammonium salt of DONA (ADONA).
The toxicity of ADONA to the green algae, Pseudokirchneriella subcapitata, was assessed in a 96-hour toxicity test conducted according to the OECD 201 (2006) method. An exponential growth was observed during the entire period of exposure in the control vessel and validity criteria were met. Exposure concentrations were based on nominal concentrations as analytical results showed that concentrations were stable and maintained within 99 -112% of nominal during the 96h test period.
The 96-hour ErC50 of ADONA to Pseudokirchneriella subcapitata for growth rate was > 100 mg/L (active ingredient).
The study was performed in accordance with internationally-accepted test guidelines and Good Laboratory Practice (GLP) standards. Therefore, use of this study for DONA is reliable with restrictions and the results are suitable for purposes of Risk Assessment, Classification & Labeling, and PBT Analysis.
Results Synopsis
Test Type: static (based on data obtained using OECD 201 methodology)
96-hr ErC50: >100 mg/L active ingredient
96-hr NOEC: 100 mg/L active ingredient
The ErC50 and NOEC results correspond to nominally 334 mg/L total product.
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