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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:
2015
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
GLP compliance:
yes
Specific details on test material used for the study:
N/A
Analytical monitoring:
yes
Details on sampling:
N/A
Vehicle:
no
Details on test solutions:
N/A
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Details on test organisms:
TEST ORGANISM
- Common name: Green algae
- Strain: Pseudokichneriella subcapitata (ID: PS-IHB-140104)
- Source (laboratory, culture collection): institute of hydrobiology, Chinese Academy of Sciences
- Method of cultivation: The algae were inoculated in 250 mL glass flasks with a concentration of 10^4 cells/mL, incubated during 3 days and then inoculated to another flask. At the beginning of the test, the algae were in the exponential growth phase when inoculated into the test solutions.


ACCLIMATION
- Acclimation period: The algae were inoculated in 250 mL glass flasks with a concentration of 10^4 cells/mL, incubated during 3 days and then inoculated to another flask. At the beginning of the test, the algae were in the exponential growth phase when inoculated into the test solutions.
Test type:
static
Water media type:
freshwater
Limit test:
yes
Total exposure duration:
72 h
Post exposure observation period:
none
Hardness:
no details mentioned
Test temperature:
23.2 - 23.6 °C
pH:
8.02 - 9.33
Dissolved oxygen:
not mentioned
Salinity:
N/A
Conductivity:
N/A
Nominal and measured concentrations:
Nominal: 100 mg/L
measured concentration below the limit of detection (LOD = 0.214 mg/L)
Details on test conditions:
lnoculation and incubation
An inoculum culture in the test medium was pre-cultured for 3 days before start of the test under the test conditions. At the begining of the test, the alga was in the exponential growth phase when inoculated to the test solutions and the density of the alga was 9.103 x 10^5/mL. For the treatment group, 3.30 mL of the alga culture were inoculated into 300mL of test solution and the initial cell density of the test solution was about 10^4 /mL (for the control cultures, 6.59 mL of the alga culture were inoculated into 600mL of alga medium). 100mL of test solution was added into each of 250 mL glass conical flasks.

Conditions of incubation
Each flask was then capped with Parafilm and put in a culturing chamber by shaking at a speed of 130rpm.
Temperature: 23.2°C-23.6°C.
Illumination: the surface where the cultures are incubated received continuous, uniform fluorescent illumination at equivalent range of 5614-5842 lux for cool white light. Any differences from the selected light intensity over the test area did not exceed the range of ±15%.

Observation and measurements
The algal biomass in each vessel was determined by a cell counter at the beginning and the end of the test. The light density was determined at 0, 24, 48 and 72h during the test period. At the beginning of the test, pH values for the control and each test concentration were measured using the remaining test solutions. At the end of the test, one vessel was randomly taken from each treatment group and the control group for pH measurement and microscopic observation of the algae. The concentrations of the test substance were determined at 0 and 72h of the test. 10 mL of test solution was taken from one test vessel of each concentration. Before sampling, separation of algae from the test medium was made by syringe filters.

- Test vessel: sterile-aerated Erlenmeyes flasks
- Initial cells density: 10000 cells/mL
- Control end cells density: 1162833 cells/mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per vehicle control (replicates): not applicable


GROWTH MEDIUM
- Standard medium used: yes
Analytical grade salts were dissolved in deionised water to obtain separate alga medium stock solutions. The stock solutions were filtrated with 0.22 µm filter membrane and kept at 2-8 °C. The alga medium was prepared by diluting the stock solutions in deionised water shortly before the test began.


TEST MEDIUM / WATER PARAMETERS
no details mentioned


OTHER TEST CONDITIONS
Illumination: the surface where the cultures are incubated received continuous, uniform fluorescent illumination at equivalent range of 5614-5842 lux for cool white light. Any differences from the selected light intensity over the test area did not exceed the range of ±15%.
At the beginning of the test, pH values for the control and each test concentration were measured using the remaining test solutions. At the end of the test, one vessel was randomly taken from each treatment group and the control group for pH measurement and microscopic observation of the algae.
- Sterile test conditions: yes
- Adjustment of pH: not adjusted
- Light intensity and quality: approx. 5614-5842 lux, white


EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Cell numbers for exposure times of 0, 24, 48, 72h
- Chlorophyll measurement: no
- Other: none


- Range finding study: The test substance is insoluble. A nominal concentration of 100mg/L was prepared and stirred (via magnetic stirrer) for 72h at 500rpm in the dark, and then filtered with 0.45µm nitrocellulose membrane to prepare the saturated solution under test conditions. One nominal concentration of the saturated solution was used in the range-finding test. Three replicates were included for each treatment as well as six for the control with alga medium. The test duration was 72h.

In the range-finding test, there was no statistically significant difference in alga growth between the treatment group and the control one (P=0.8199 for average specific growth rate and P=0.7855 for yield, 19.2). Therefore, a limit test would be performed.

Reference substance (positive control):
no
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
Remarks on result:
other: not toxic in the range of water solubility
Details on results:
- Exponential growth in the control (for algal test): yes
- Observation of abnormalities (for algal test): no observations made
- 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
- Effect concentrations exceeding solubility of substance in test medium: no


Results with reference substance (positive control):
no reference substance tested
Reported statistics and error estimates:
no statistical evaluation performed

Table 1: Cell density (cell /ml) of Pseudokirchneriella subcapitata exposed to the test substance for 72h in the limit test:

Group     0h   24h  48h  72h
  Blank control                      1  10000  60300  379500  1435000
 2   10000  58470  366800  1623000
 3   10000  62720  370300  1554000
 4   10000  57910  391800  1686000
 5   10000  62430 357600   1538000
 6   10000  62550  346600  1609000
 Mean   10000  60730  368767  1574167
 CV (%)  0  3.56  4.3  5.48
 Treatment group /saturated solution)                       1   10000  63180  372300  1551000
 2   10000  60370  369100  1546000
 3   10000  59970  351500  1577000
 4   10000  62640  364400  1589000
  10000  58300  359500  1518000
 6  10000   59130  353100  1515000
 Mean   10000   60598  361650  1549333
 CV (%)  0  3.19  2.34  1.94

Table 2: Growth of Pseudokirchneriella subcaptitata for the blank control cultures in the limit test

Blank Control      Average specific growth rate              Yield   
 0 - 24h  24 - 48h  48 - 72h  CV (%) for Section-by-section  0 - 72 h
 1  1.80  1.84  1.33  17.1  1.66  1425000
 2  1.77  1.84  1.49  10.9  1.70  1613000
 3  1.84  1.84  1.43  12.9  1.68  1544000
 4  1.76  1.91  1.46  13.5  1.71  1676000
 5  1.83  1.75 1.46   11.6  1.68  1528000
 6 1.83   1.71  1.54  8.9  1.69  1599000
 Mean  1.80 1.80   1.54  12.5  1.69  1564167
 CV (%) for replicates  1.99  4.05 4.72   -  1.10  5.51

Table 3: Growth of Pseudokirchneriella subcapitata exposed to the test substance in the limit test

 Treatment group           Avergae specific growth rate              Yield   
 0 -24 h  24 -48h  48 -72h  0 -72h

  72 h Inhibition

 0 -72h

  

 72 h Inhibition

 saturated solution

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 1

 1.84

 1.77

 1.43

 1.68

 0.27

 1541000

 1.48

 2

 1.80

1.81 

1.43 

1.68 

0.33 

1536000 

1.80 

 3

 1.79

 1.77

 1.50

 1.69

 -0.06

 1567000

 -0.18

 4

 1.83

 1.76

 1.47

1.69 

-0.21 

1579000 

-0.95 

 5

1.76 

1.82 

1.44 

1.67 

0.69 

1508000 

3.59 

 6

1.78 

1.79 

1.46 

1.67 

0.74 

1505000 

3.78 

 Mean

1.80 

1.79 

1.46 

1.68 

0.29 

1539333 

1.59 

 CV (%)

 1.76

 1.32

1.93 

0.38 

1.95 

                                                                           

Validity criteria fulfilled:
yes
Remarks:
mean biomass control cultures increased 157 fold, mean coefficient of variation section-by-section specific growth rates control cultures 12.5%, coefficient of variation of average specific growth rates test period in replicate control cultures 1.1 %
Conclusions:
Not toxic to algae under test conditions in the range of water solubility.
Executive summary:

The growth inhibition effect of 1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters to Pseudokirchneriella subcapitata was determined in a 72h test according to OECD 201.

A nominal concentration of 100 mg/L of the test substance was prepared and stirred for 72 h at 500 rpm in the dark followed by filtration using a 0.45 µm nitrocellulose membrane to make a saturated solution of test system (referred to as "saturated "solution" in this report, since the measured concentration was below LOD, LOD = 0.214 mg/L). Based on the results of the range-finding test, one treatment group of saturated solution and one control group of alga medium were included in the limit test. Six replicates for each group were run. The duration was 72h.

The mean biomasss of the control cultures was increased by 157 folds, which is higher than the validity criterion of at least 16 within the 72h test period., corresponding to a specific growth rate of 0.92 day-1 . The mean coefficient of variation for section-by-section specific growth rates in the control cultures was 12.5 %, which was below 35 %. The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures was 1.1%, which was below 7 %. Hence, the test was cosidered to be valid. During the test, the measured concentrations of the tst substance analyzed by gas chromatography were below the limit of detection (LOD, LOD=0.214 mg/L).

Under the present test conditions, no inhibition effects were observed on Pseudokirchneriella subcapitata exposed to the test substance. Therefore, based on average specific growth rate, the 72h NOEC was not less than the measure concentration of the saturated solution, the LOEC were also higher than the measured concentration of the saturated solution. The concentration was below LOD, LOD=0.214 mg/L.

Not toxic to algae under test conditions in the range of water solubility.

Description of key information

1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters under test conditions has shown no toxic effects to Pseudokirchneriella subcapitata in the range of water solubility.

Key value for chemical safety assessment

EC50 for freshwater algae:
100 mg/L

Additional information

The growth inhibition effect of 1,2,4 -Benzenetricarboxylic acid, mixed dodecyl and octyl triesters to Pseudokirchneriella subcapitata was determined in a 72h test according to OECD 201.

A nominal concentration of 100 mg/L of the test substance was prepared and stirred for 72 h at 500 rpm in the dark followed by filtration using a 0.45 µm nitrocellulose membrane to make a saturated solution of test system (referred to as "saturated "solution" in this report, since the measured concentration was below LOD, LOD = 0.214 mg/L). Based on the results of the range-finding test, one treatment group of saturated solution and one control group of alga medium were included in the limit test. Six replicates for each group were run. The duration was 72h.

 

The mean biomasss of the control cultures was increased by 157 folds, which is higher than the validity criterion of at least 16 within the 72h test period., corresponding to a specific growth rate of 0.92 day-1 . The mean coefficient of variation for section-by-section specific growth rates in the control cultures was 12.5 %, which was below 35 %. The coefficient of variation of average specific growth rates during the whole test period in replicate control cultures was 1.1%, which was below 7 %. Hence, the test was cosidered to be valid. During the test, the measured concentrations of the tst substance analyzed by gas chromatography were below the limit of detection (LOD, LOD=0.214 mg/L).

 

Under the present test conditions, no inhibition effects were observed on Pseudokirchneriella subcapitata exposed to the test substance. Therefore, based on average specific growth rate, the 72h NOEC was not less than the measure concentration of the saturated solution, the LOEC were also higher than the measured concentration of the saturated solution. The concentration was below LOD, LOD=0.214 mg/L.