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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Administrative data

Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2001-11-16 to 2002-02-13
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2002
Report date:
2002

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Version / remarks:
1984
Deviations:
no
GLP compliance:
yes

Test material

Constituent 1
Chemical structure
Reference substance name:
Glycollic acid
EC Number:
201-180-5
EC Name:
Glycollic acid
Cas Number:
79-14-1
Molecular formula:
C2H4O3
IUPAC Name:
glycol acid
Test material form:
liquid

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
- Concentrations: 10, 20, 40, and 75 mg/L
- Sampling method: Samples from each of the working stock, test concentrations, and blank control solutions were collected on day 0. An aliquot from each of the test concentrations and blank control solutions was taken prior to the addition of Selenastrum capricornutum. Samples from each of the test concentrations, blank control, and abiotic control solutions also
were collected on day 3. These samples were prepared by pooling all 3 replicates for each of the test and control solutions. Aliquots were taken from each of the pooled samples and given to the analytical chemist for analysis.
- Sample storage conditions before analysis: Samples were analysed on the day of receipt.

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method:
Preparation of AAP nutient medium: Adding 1mL of each of 6 macronutrient stock solutions and 1 mL of the micronutrient stock solution to approximately 800 mL of Milli-Q water (deionized), with mixing after addition. The volume was brought to 1 L with additional Milli-Q water. The test stock solution consisted of nominal 100 mg/L glycolic acid in 1000 mL sterilized AAP nutrient medium. The other nominal concentrations used in the test were made by respective dilutions of this stock solution.

Test organisms

Test organisms (species):
Selenastrum sp.
Details on test organisms:
TEST ORGANISM
- Common name: Green algae
- Strain: Selenastrum sp.
- Strain: Selenastrum capricornutum
- Method of cultivation: The organisms were cultured in sterilized 250 mL Erlenmeyer flasks containing approximately 50 mL of filtered (= filter-sterilized) synthetic algal-assay-procedure (AAP) nutrient medium and were aseptically transferred to fresh medium every 3 to 7 days. The flasks were fitted with foam stoppers to permit gas exchange.

ACCLIMATION
- Culturing media and conditions (same as test or not): same as test

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Post exposure observation period:
At the end of the 72-hour exposure period, a single randomly selected replicate from the blank control and an aliquot from each of the replicate flasks from each of the test concentrations exhibiting a 50% or greater inhibition of cell counts relative to the blank control (nominal 40, 75, and 100 mg/L) were selected for the recovery test.

Test conditions

Test temperature:
24 ± 2°C
pH:
pH at test start:
concentration:
10 mg/L 7.39
20 mg/L 6.74
40 mg/L 5.16
75 mg/L 3.96
100 mg/L 3.70

pH at the end of exposure
10 mg/L 7.63
20 mg/L 7.55
40 mg/L 7.37
75 mg/L 7.39
100 mg/L 7.29
Nominal and measured concentrations:
Nominal concentrations: 0, 10, 20, 40, 75 and 100 mg/L
Measured concentrations: 0, 7.52, 14.5, 30.3 and 54.6 mg/L, which represents 106, 102, 107 and 103% recovery of the active ingredient.
Details on test conditions:
TEST SYSTEM
- Test vessel: Erlenmeyer flasks
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: Glass, 250 mL fill volume, 50 mL solution volume
- Initial cells density: 10,000 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3

GROWTH MEDIUM
- Standard medium used: yes

TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Milli-Q water
- Culture medium different from test medium: No

OTHER TEST CONDITIONS
- Sterile test conditions: yes
- Adjustment of pH: no
- Photoperiod: Illumination: with 6000 to 10000 lux for 24h

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: The counts were conducted using a hemacytometer and a compound microscope. An aliquot of each sample was loaded into the hemacytometer and 16 grids were selected. All cells located in the 16 grids were counted and recorded as healthy or unhealthy.

TEST CONCENTRATIONS
- Test concentrations: 10, 20, 40, 75 and 100 mg/L
Reference substance (positive control):
no

Results and discussion

Effect concentrationsopen allclose all
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
44 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
20 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
22.5 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
cell number
Key result
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
10 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
cell number
Reported statistics and error estimates:
The mean healthy cell count, area under the growth curve, and growth rate at the 72-hour interval for each test concentration were expressed relative to the blank control. The growth rate and the percent inhibition as well as the EC50 value and the NOEC were calculated as described previously (OECD Test Guideline 201).

Any other information on results incl. tables

Table 1: Effect of glycolic acid on growth of Selenastrum capricornutum

Treatment nominal concentration (mg/l)

Initial cell density

Cell density at

24 hours

48 hours

72hours

Cell count

% inhibition (mean)

Negative control

Replicate #1

10,000

100,000

260,000

3,900,000

 

Replicate #2

10,000

150,000

720,000

3,920,000

Replicate #3

10,000

70,000

580,000

3,630,000

10

Replicate #1

10,000

70,000

320,000

3,710,000

2.27

Replicate #2

10,000

140,000

290,000

3,630,000

Replicate #3

10,000

110,000

460,000

3,850,000

20

Replicate #1

10,000

20,000

270,000

2,370,000

37.21

Replicate #2

10,000

20,000

220,000

2,400,000

Replicate #3

10,000

20,000

380,000

2,420,000

40

Replicate #1

10,000

10,000

30,000

180,000

94.59

Replicate #2

10,000

10,000

40,000

240,000

Replicate #3

10,000

10,000

20,000

200,000

75

Replicate #1

10,000

10,000

10,000

40,000

99.04

Replicate #2

10,000

10,000

60,000

30,000

Replicate #3

10,000

10,000

20,000

40,000

100

Replicate #1

10,000

20,000

10,000

30,000

99.30

Replicate #2

10,000

20,000

20,000

20,000

Replicate #3

10,000

10,000

10,000

30,000

In aqueous solutions glycolide significantly decreases pH. The following pH values were measured during the study:

pH at test start:

concentration:

10 mg/L       7.39

20 mg/L       6.74

40 mg/L       5.16

75 mg/L       3.96

100 mg/L       3.70

pH at the end of exposure

10 mg/L       7.63

20 mg/L       7.55

40 mg/L       7.37

75 mg/L       7.39

100 mg/L       7.29

The inhibitory effect is likely caused by the acidification of the growth medium. However, the growth inhibitory effect was reduced in the 10 and 20 mg/L incubation groups in which the pH returned to physiological values during the observation period.

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Conclusions:
The present study was conducted according to OECD Test Guideline 201, the green alga Selenastrum capriconutum was incubated with nominal concentrations of 0, 10, 20, 40, 75 and 100 mg/L glycolic acid (70.81%) for 72h under static conditions. Just before exposure and after 72 h exposure time the cells were counted in order to determine the growth rate. There was an inhibitory effect of glycolic acid of more than 10% in concentrations of 20 mg/L and above, thus, glycolic acid is considered to be algistatic at nominal concentrations less than or equal to 100 mg/L. The NOEC of 20 mg/L and an EC50 of 44.0 mg/L for the growth rate was determined. However, the algistatic effect is most likely caused by the strong acidification of the medium at concentrations higher than 20 mg/L. Thus, the determined EC50 and NOEC are established based on a worst case scenario.