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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
25 April - 19 May 2017
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Remarks:
Use of THF as test material carrier
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Version / remarks:
Adopted 23 March 2006
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Remarks:
The Department of Health of the Government of the United Kingdom, London, UK
Analytical monitoring:
yes
Details on sampling:
- Concentrations: culture medium control, solvent control, 0.056, 0.1, 0.18, 0.32, 0.56 and 1.0 mg/L
- Sampling method: Samples were taken at 0 (test start), 24, 48 and 72 (test end) hours.
Vehicle:
yes
Remarks:
THF
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A primary stock concentrate of the test item, with a nominal concentration of 10 g/L, was prepared by adding a nominal 0.1 g of test substance to 10 mL of tetrahydrofuran (THF). The stock solution was used to prepare the test solutions by the direct addition of the appropriate amount of concentrate to dilution water via a microliter syringe into a stirring solution in a volumetric flask. The solvent control was prepared in the same way using solvent only. The control consisted of culture medium only.
- Controls: culture medium control, solvent control
- Chemical name of vehicle: Tetrahydrofuran (THF)
- Concentration of vehicle in test medium: 100 μl/L in all exposure solutions (except blank control)
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Common name: Freshwater algae
- Source: laboratory cultures
- Age of inoculum (at test initiation): 3 days
- Method of cultivation: grown in medium under test condition
Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Test temperature:
22 ± 2°C
pH:
range at test start: 6.99 - 7.33
range at test end: 8.18 - 8.42
Nominal and measured concentrations:
nominal: (control and solvent control), 0.056, 0.1, 0.18, 0.32, 0.56 and 1.0 mg/L
mean measured (0-72h): (control and solvent control), 0, 0, 0.067, 0.080, 0.14, 0.28 mg/L.
Where values were less than LOQ, 0 was used to calculate the mean.
Details on test conditions:
TEST SYSTEM
- Test vessel: glass conical flasks of 250 mL nominal capacity closed with foam bungs
- Type: closed
- Material, size, headspace, fill volume: each flask contained 100 mL of test solution
- Initial cells density: 0.5 × 10^4 cells/mL (nominal)
- Control end cells density: 53.65 (mean at 72 h)
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): 6

GROWTH MEDIUM
- Standard medium used: yes, AAP medium

OTHER TEST CONDITIONS
- Sterile test conditions: no
- Light intensity and quality: 5865 lux (± 15%)

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: electronic particle counter

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.75 - 1.80
- Range finding study: yes, no results reported
- Results used to determine the conditions for the definitive study: yes
Reference substance (positive control):
no
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
> 0.28 mg/L
Nominal / measured:
meas. (arithm. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
> 0.28 mg/L
Nominal / measured:
meas. (arithm. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
0.14 mg/L
Nominal / measured:
meas. (arithm. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
- Exponential growth in the control (for algal test): yes
Reported statistics and error estimates:
The growth rates were examined by one-way analysis of variance and a two-sample t test to identify significant differences (p<0.05) between the control and solvent control. There was no significant effect (p=0.1208) between the control and solvent control. Therefore, the solvent control was compared to the treatments by one-way analysis of variance and Bonferroni adjusted t test to identify significant differences (p<0.05).

Table 1: Analytical Results

Nominal

concentration of test item

(mg/L)

Measured concentration of test item

Mean

measured

concentration

(mg/L)

Mean

measured

concentration

(%)

 

0 hour

72 hour

 

 

 

(mg/L)

% of

nominal

(mg/L)

% of

nominal

 

 

Control

<LOQ

-

<LOQ

-

-

-

Solvent Control

<LOQ

-

<LOQ

-

-

-

0.056

<LOQ

0

<LOQ

0

0

0

0.1

<LOQ

0

<LOQ

0

0

0

0.18

0.13

75

<LOQ

0

0.067

37

0.32

0.16

50

<LOQ

0

0.080

25

0.56

0.29a

51

<LOQb

0

0.14

26

1.0

0.56

56

<LOQ

0

0.28

28

All measurements are quoted to 2 significant figures

a) Mean of triplicate analyses: 0.30, 0.29, 0.27 mg/L

b) Mean of triplicate analyses: 0, 0, 0 mg/L

The limit of quantification (LOQ) in the study was 0.1 mg/L. Where values were less than LOQ, 0 was used to calculate the mean.

Table 2: Algal cell particle density

Nominal concentration of test item

(mg/L)

Mean measured concentration of test item

(mg/L)

Replicate

Algal cell particle density

(104cells/mL)

24 hours

 

48 hours

 

72 hours

 

Culture medium control

 

-

A

2.32

10.80

50.90

B

2.64

11.30

50.60

C

2.49

11.10

57.00

D

2.36

10.50

47.00

E

2.58

10.60

51.30

F

2.65

12.70

65.10

Mean

2.51

11.17

53.65

Solvent control

 

-

A

2.11

11.00

48.70

B

2.09

10.50

50.20

C

2.23

10.70

56.00

D

2.05

9.11

43.60

E

2.14

10.20

50.50

F

1.91

11.20

49.70

Mean

2.09

10.45

49.78

0.056

0

A

1.93

10.50

39.80

B

2.22

10.20

45.60

C

2.18

10.40

45.60

Mean

2.11

10.37

43.67

0.1

0

A

2.13

10.30

51.00

B

2.14

10.10

43.70

C

2.36

10.40

47.40

Mean

2.21

10.27

47.37

0.18

0.067

A

2.01

9.94

47.90

B

2.40

11.20

58.30

C

2.16

9.97

46.90

Mean

2.19

10.37

51.03

0.32

0.080

A

2.21

10.70

44.70

B

2.44

10.50

49.60

C

2.17

11.00

47.80

Mean

2.27

10.73

47.37

0.56

0.14

A

1.99

10.40

50.10

B

2.26

11.90

57.00

C

2.75

11.70

57.60

Mean

2.33

11.33

54.90

1.0

0.28

A

1.93

9.20

42.10

B

2.12

9.34

38.10

C

2.04

9.24

41.80

Mean

2.03

9.26

40.67

Inoculum (Day 0) cell density = 0.578 x 104 cells/mL

All values are quoted to 2 decimal places

Table 3: Mean growth rates over the test period

Nominal concentration of the test item

(mg/L)

Mean measured concentration of the test item

(mg/L)

Mean growth rate/day

(0-72 hours)

Mean growth rate/day

95% Cl

Percentage of solvent control (%)

Culture medium control

-

1.51

1.47-1.55

102

Solvent control

-

1.49

1.46-1.51

-

0.18

0.067

1.49

1.39-1.59

101

0.32

0.080

1.47

1.43-1.51

99

0.56

0.14

1.52

1.45-1.58

102

1.0

0.28

1.42*

1.37-1.46

95

* Significant difference (p <0.05) from the solvent control

All biological measurements are quoted to 3 significant figures and percentages to the nearest integer

Table 4: Mean yields over the test period

Nominal concentration of the test item

(mg/L)

Mean measured concentration of the test item

(mg/L)

Mean yield

(0-72 hours)

(104Cells/ml)

Percentage of solvent control (%)

Culture medium control

-

53

108

Solvent control

-

49

-

0.18

0.067

50

103

0.32

0.080

47

95

0.56

0.14

54

110

1.0

0.28

44

90

No significant differences (p <0.05) from the control

All measurements are quoted to 2 significant figures and percentages to the nearest integer

NOEyC(72 h): >= 0.28 mg/L, EyC10(72 h): 0.26 mg/L EyC50(72 h) >0.28 mg/L

Table: 5 Validity criteria for OECD 201.

Criterion from the guideline

Outcome

Validity criterion fulfilled

The biomass in the control cultures should have increased exponentially by a factor of at least 16 within the 72-hour test period.

factor 93 (control)
factor 86 (sovent control)

 

yes

The mean coefficient of variation for section-by-section specific growth rates (days 0-1, 1-2 and 2-3, for 72-hour tests) in the control cultures must not exceed 35%

4.5% (control)
13% (sovent control)

 

yes

The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures must not exceed 7% in tests with Pseudokirchneriella subcapitata and Desmodesmus subspicatus. For other less frequently tested species, the value should not exceed 10%.

2.6% (control)
1.8% (sovent control)

yes

 

Validity criteria fulfilled:
yes
Remarks:
see Table 5 at "Any other information on results incl. tables"

Description of key information

Aquatic algae:

ErC50 (72 h) >0.28 mg/L (meas. arith. mean)

ErC10 (72 h) was >0.28 mg/L (meas. arith. mean).

Key value for chemical safety assessment

Additional information

The toxicity of the source substanceGlycerol monomyristate (CAS 27214-38-6) to aquatic algaewas tested according to OECD 203 under GLP conditions. The green algae Pseudokirchneriella subcapitata was exposed to nominal test substance concentrations of 0.056, 0.1, 0.18, 0.32, 0.56 and 1.0 mg/L. The test concentration was prepared using tetrahydrofuran (THF) as vehicle. The concentration of vehicle in test medium was 0.1 mL/L. The test substance concentration was analytically verified by HPLC with a detection limit of 0.1 mg/L. The mean measured test substance concentrations were 0, 0, 0.067, 0.080, 0.14, 0.28 mg/L. In case measured values were less than LOQ, 0 mg/L was used to calculate the mean.

Based on the algal growth rate an ErC50 (72 h) >0.28 mg/L (meas. arith. mean) was determined. The reported ErC10 (72 h) was >0.28 mg/L (meas. arith. mean).

The growth rate in the highest test concentration (0.28 mg/L, mean measured) was reduced by approx. 5% compared to the solvent control and thus a NOEC of 0.14 mg/L was reported. However, an effect below 10% is considered not relevant in algal growth tests. Thus according to the Guidance on the Application of the CLP Criteria (ECHA, 2017) preference is given to the EC10 for the assessment of the chronic aquatic toxicity of a substance.