Trimethyloctadecylammonium chloride

Toxicity to soil microorganisms

Link to relevant study record(s)

Reference

Reference 1

Endpoint:

toxicity to soil microorganisms

Type of information:

read-across based on grouping of substances (category approach)

Adequacy of study:

key study

Study period:

From January 26, 2004 to March 09, 2004

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Remarks:

RA study

Justification for type of information:

Refer to the section 13 for details on the read across justification. The toxicity to soil microorganisms study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.

Reference:

Composition 1

Qualifier:

according to

Guideline:

OECD Guideline 216 (Soil Microorganisms: Nitrogen Transformation Test)

Deviations:

no

GLP compliance:

yes (incl. certificate)

Test material information:

Composition 1

Specific details on test material used for the study:

- Purity: 49.9% of the test substance in water.

Analytical monitoring:

yes

Vehicle:

no

Details on preparation and application of test substrate:

Details on inocculum:
- Nature: soil sample (sandy loam)
- Sampling site:
Data on the history of the site: 2003 fallow soil, 2002 pumpkin, 2001 fallow soil and 400 kg/ha Nitrophoska Spezial, 2000 fallow soil and 400 kg/ha Nitrophoska Spezial, and 1999 cucumber/ leek/ strawberries and 400 kg/ha Nitrophoska Spezial.
- Use pattern: agricultural soil
- Depth of sampling [cm]: 20
- Sand / Silt / Clay content [% dry weight]: Particle sizes according to USDA (%):
< 0.002 mm : 8.5 +/- 1.4;
0.002 – 0.05 mm : 29.2 +/- 3.2
0.05 – 2.0 mm : 62.3 +/- 4.1
- pH: 6.3 +/- 0.4
- Organic carbon content [% dry weight]: 1.02 +/- 0.17
- Nitrogen content [mg/g dry weight]: 0.51
- Cation exchange capacity [mval/100 g]: 10 +/- 2
- Initial microbial biomass: The microbial carbon is 2.3% of the organic carbon present in the soil. More than 1% of the total soil organic carbon
should be biomass-carbon
- Reference of methods: The pH was measured using a pH meter. The temperature was measured and recorded with a thermo couple connected to a data logger.
The amount of inorganic carbon in the absorbers was measured by injecting samples in a Shimadzu TOC apparatus (Shimadzu, s’Hertogenbosch, the Netherlands). Samples were injected in a TOC apparatus. The active microbial biomass was determined according to the respiration method (ISO 1997; Anderson and Domsch, 1978).
- Collection / storage of samples: Sandy loam was purchased from the Landwirtschaftliche Untersuchungs- und Forschungsanstalt Speyer, Speyer,
Germany. The soil was stored in the refrigerator in polyethylene bags until use in the experiment for 10 weeks.
- Preparation of inoculum for exposure: The soil was preconditioned by incubating the soil for 7 d at 20°C at 10% of its water holding capacity
(water content of the soil as received). The soil was amended with powdered alfalfa meal (Medicago sativa), 5 g of alfalfa meal per kilogram of soil (dry weight).
- Pretreatment: No pretreatment

Test organisms (inoculum):

soil

Total exposure duration:

28 d

Test temperature:

20°C

Moisture:

The amount of water in the soil was approximately 43% of the maximum water holding capacity. This corresponds with a pF between 2.0 and 2.5.

Organic carbon content (% dry weight):

1.02 +/- 0.17

Nitrogen content (% dry weight):

0.51

Details on test conditions:

Details on the test system:
- Culturing apparatus: Glass flasks 0.25 L
- Number of vessels / concentration; 3
- Aeration device: No aeration
- Measuring equipment: Nitrate concentrations were determined with the Reflectoquant, Nitrat Test and RQFlex reflectometer, Merck Darmstadt, Germany.
- Test performed in closed vessels: Yes, to prevent water loss the flasks were covered with an oxygen permeable film.

Nominal and measured concentrations:

0, 50, 100, 200, 400, 800, 1600, 3200 and 6400 mg a.i./kg

Reference substance (positive control):

no

Duration:

28 d

Dose descriptor:

EC10

Effect conc.:

70 mg/kg soil dw

Conc. based on:

act. ingr.

Basis for effect:

nitrate formation rate

Remarks on result:

other: calculated

Key result

Duration:

28 d

Dose descriptor:

EC50

Effect conc.:

130 mg/kg soil dw

Conc. based on:

act. ingr.

Basis for effect:

nitrate formation rate

Remarks on result:

other: 95% confidence limits: 80 and 190 mg a.i./kg

Details on results:

The activity of the microorganisms transforming nitrogen in soil was slightly inhibited at 50 mg a.i./kg. The EC50 calculated was 130 mg a.i./kg with 95% confidence limits of 80 mg a.i./kg and 190 mg a.i./kg. The EC10, EC20 and EC80 of test substance were 70, 90 and 200 mg a.i./kg respectively. In soil not only formation of nitrate occurs but also reduction of nitrate to nitrogen gas by denitrifying microorganisms. Decrease of the nitrate concentrations in the soil at test substance concentration of 400 mg a.i./kg and higher after 28d is probably the result of the activity of these denitrifying microorganisms. Denitrifying microorganisms are not affected by test substance at concentrations ranging from 400 to 3200 mg a.i./kg whereas the microorganisms responsible of the formation of nitrate are inhibited at these concentrations. The denitrifying microorganisms are inhibited at 6400 mg a.i./kg because after 28d only a limited amount of the nitrate was removed.

Results with reference substance (positive control):

-

Reported statistics and error estimates:

The EC values were computed from the best fitted line (least square method) through the points given by the probit of the percentage inhibition and the logarithm of the concentration of the test substance. The EC10, 25, 50 values were computed from the best fitted line (least-squares method) through the points given by the probit of the percentage inhibition and the logarithm of the concentration of the test substance. Confidence limits were computed on the basis of Fieller's theorem. All computations were performed using the TOXCALC version 5.0 program.

The dose response relationship showed a normal pattern. According to the OECD guidelines the variation between the three control replicates should be less than 15%. This criterion was met because the variation was only 10%. Therefore the test was considered to be valid.

Validity criteria fulfilled:

yes

Conclusions:

Based on the results of the read across study, the 28d EC50 calculated was 130 mg a.i./kg with 95% confidence limits of 80 mg a.i./kg and 190 mg a.i./kg. The 28d EC10, EC20 and EC80 of test substance were 70, 90 and 200 mg a.i./kg respectively.

Executive summary:

A study was conducted to determine the toxicity to microorganisms of the read across substance, quaternary ammonium compounds, benzyl C12-C16 (even numbered)-alkyldimethyl chlorides (C12-16 ADBAC), according to OECD Guideline 216, in compliance with GLP. A nitrogen transformation test was used in this experiment. Analytical determination was performed for the test substance. The concentrations ranged from 0, 50, 100, 200, 400, 800, 1600, 3200 and 6400 mg a.i./kg soil dw. The activity of the micro-organisms transforming nitrogen in soil was slightly inhibited at 50 mg a.i./kg soil dw. Denitrifying microorganisms were not affected at concentrations ranging from 400 to 3200 mg a.i./kg soil dw whereas the microorganisms responsible of the formation of nitrate were inhibited at these concentrations. The denitrifying microorganisms were inhibited at 6400 mg a.i./kg soil dw because after 28 days only a limited amount of the nitrate was removed. Based on the results of the read across study, the 28 d EC50 calculated was 130 mg a.i./kg with 95% confidence limits of 80 mg a.i./kg and 190 mg a.i./kg. The 28 d EC10, EC20 and EC80 of test substance were 70, 90 and 200 mg a.i./kg respectively (van Ginkel, 2004).

Reference 2

Endpoint:

toxicity to soil microorganisms

Type of information:

read-across based on grouping of substances (category approach)

Adequacy of study:

key study

Study period:

From July 13, 2000 to October 24, 2000

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Remarks:

RA study

Justification for type of information:

Refer to the section 13 for details on the read across justification. The toxicity to soil microorganisms study with the read across substance is considered sufficient to fulfil the information requirements as further explained in the provided endpoint summary.

Reference:

Composition 1

Qualifier:

according to

Guideline:

OECD Guideline 216 (Soil Microorganisms: Nitrogen Transformation Test)

Deviations:

no

Qualifier:

according to

Guideline:

OECD Guideline 217 (Soil Microorganisms: Carbon Transformation Test)

Deviations:

no

Qualifier:

according to

Guideline:

EPA OPPTS 850.5100 (Soil Microbial Community Toxicity Test)

Deviations:

no

Qualifier:

according to

Guideline:

other: Section H.4.1 of the guideline issued by the Netherlands Board for the Authorization of Pesticides (CTB)

Deviations:

no

GLP compliance:

yes (incl. certificate)

Test material information:

Composition 1

Specific details on test material used for the study:

- Analytical purity: 49-51% in aqueous solution
- Lot/batch No.: E8223267
- Storage condition of test material: Room temperature

Analytical monitoring:

not specified

Details on preparation and application of test substrate:

Amendment of soil:
- Type of organic substrate:
(1) Sandy loam - Maasdijk, Heerewaarden, Netherlands
(2) Low humic content sand - Bulb Research Institute, Lisse, Netherlands

Application of the test substance to soil:
- Method: The soil samples were air-dried, sieved to obtain soil granules of less than or equal to 2 mm. Sieved soil samples were analysed for silt, clay, sand, total nitrogen, organic matter and organic carbon content, pH as well as cation exchange capacity by Levington Agriculture, Ipswich, England.

Powdered lucerne meal (C/N ratio 13/1) was added at a concentration of 0.3 g/50 g dw pre-incubated soil. After mixing 50 ± 0.5 g dry weight of soil samples were placed in 100 mL Schott Duran bottles. For each sampling time four replicates at treated and untreated soils were prepared. Samples were treated with test substance at concentrations 0, 10, 100 and 1,000 µg a.i./g soil dw. A stock solution of the test substance was prepared by dissolving 10.0071 g of the test substance in 50 mL of ultra pure water. Further dilutions in ultra pure water were prepared to achieve final test substance concentration series of 10, 100 and 1,000 µg a.i./g soil dw.

The control soils received 0.5 mL of ultra pure water per 50g dw soil. The test substance and control solutions were mixed thoroughly with the soils and the flasks were closed with sponge caps (except during the CO2 measurements) and incubated at 20 ± 2°C for 28d in dark.

Test organisms (inoculum):

soil

Total exposure duration:

28 d

Test temperature:

20 ± 2°C

Moisture:

The moisture content of the soils was adjusted to 40-50% of maximum water holding capacity (MWHC) (i.e., 21.1% for the sandy loam and 15.6% for the low humic content soil).

Organic carbon content (% dry weight):

Sandy loam: 1.6%
Low humic content sand: 0.3%

Nitrogen content (% dry weight):

Sandy loam: 0.15%; Low humic content sand: 0.12%

Details on test conditions:

Test system:
- Testing facility: Levington Agriculture, Ipswich, England.
- Test container (type, material, size): 100 mL Schott Duran bottles
- Amount of soil: 50 ± 0.5 g dry weight of soil
- No. of replicates per concentration: Four
- No. of replicates per control: Four

Soil incubation:
- Method: Bulk / series of individual subsamples: The test substance and control solutions were mixed thoroughly with the soils and the flasks were closed with sponge caps (except during the CO2 measurements) and incubated at 20 ± 2°C for 28 d in dark.

Source and properties of substrate (if soil):
- Geographical reference of sampling site (latitude, longitude):
Sandy loam – Maasdijk, Heerewaarden, Netherlands (51°48'N, 5°22'E)
Low humic content sand – Bulb Research Institute, Lisse, Netherlands (51° 15'N, 4°33'E)

Sandy loam
- % sand: 60
- % silt: 24
- % clay: 16

Low humic content sand
- % sand: 97
- % silt: 1
- % clay: 2

- Soil taxonomic classification: Sandy loam and Sand
- Soil classification system: USDA classification
- pH (in water): Sandy loam: 7.9; Low humic content sand: 6.8
- Maximum water holding capacity (in % dry weigth): MWHC: 21.1% for the sandy loam and 15.6% for the low humic content soil.
- Cation exchange capacity (meq/100 g): Sandy loam: 10.6; Low humic content sand: 4
- Initial microbial biomass as % of total organic C: Sandy loam: 0.9%; Low humic content sand: 0.5%
-Total nitrogen (%): Sandy loam: 0.15%; Low humic content sand: 0.12%

Preincubation of soil (if any): at 20 ± 2°C for 7d

Effect parameters measured (with observation intervals if applicable) : Nitrite, nitrate, ammonium and carbon dioxide formation

Vehicle control: yes, aqueous vehicle control

Nominal and measured concentrations:

Nominal: 0, 10, 100 and 1,000 µg a.i./g soil dw

Reference substance (positive control):

no

Key result

Duration:

28 d

Dose descriptor:

EC50

Effect conc.:

> 1 000 mg/kg soil dw

Nominal / measured:

nominal

Basis for effect:

other: quantities of nitrate, nitrite and ammonium

Remarks on result:

other: <25% reduction after 28 days (i.e., The difference in CO2 production and nitrogen transformation between the treated and untreated soil samples did not exceed 25% after 28 d of incubation).

Details on results:

The difference in CO2 production and nitrogen transformation between the treated and untreated soil samples did not exceed 25% after 28d of incubation. The highest inhibition recorded was 82.5% in the nitrite formation rate after 5d at 10 mg a.i./kg soil dw in the sandy loam soil. After 28d of incubation, however, no relevant effect was observed (i.e., less than 25% reduction). Test substance is therefore considered to have a low potential for adversely affecting the microbial functions of sandy loam and low humic content sand soils.

Results with reference substance (positive control):

-

Reported statistics and error estimates:

Two tailed Dunnett test (multiple comparison with a control).

Validity criteria fulfilled:

yes

Remarks:

The variation between replicate control samples was less than ±15%, which means that the results are within the validity criteria stated in the guidelines.

Conclusions:

Based on the results of the read across study, the difference in CO2 production and nitrogen transformation between the treated and untreated soil samples did not exceed 25% after 28d of incubation. The highest inhibition recorded was 82.5% in the nitrite formation rate after 5d at 10 mg a.i./kg soil dw in the sandy loam soil. After 28d of incubation, however, no relevant effect was observed (i.e., less than 25% reduction). The test substance was therefore considered to have a low potential for adversely affecting the microbial functions of sandy loam and low humic content sand soils. Test substance can be characterised as having no long-term influence on nitrogen and carbon transformations in soils.

Executive summary:

A study was conducted to determine the toxicity to soil microorganisms of the read across substance, quaternary ammonium compounds, benzyl C12-C16 (even numbered)-alkyldimethyl chlorides (C12-16 ADBAC), according to OECD Guideline 216 and 217, and US EPA OPPTS 850.5100, in compliance with GLP. The effects of the test substance on carbon mineralization and nitrogen transformation activity of soil micro-organisms in a sandy loam soil and a low humic content sand soil were investigated in a 28 day study. Fifty grams dry weight of soil samples were mixed with lucerne meal and placed in 100 mL bottles. The samples were incubated in the dark at 20±2°C for 28 days. The moisture content of the samples was checked weekly. Samples were dosed with test substance at concentrations 0, 10, 100 and 1,000 mg a.i./kg soil dw. No analytical determination was performed for the test substance. CO2 evolution was determined on Days 5 – 8 and 25 – 28. Based on the results of the read across study, the difference in CO2 production and nitrogen transformation between the treated and untreated soil samples did not exceed 25% after 28 d of incubation. The highest inhibition recorded was 82.5% in the nitrite formation rate after 5 d at 10 mg a.i./kg soil dw in the sandy loam soil. After 28 d of incubation, however, no relevant effect was observed (i.e. less than 25% reduction). The test substance was therefore considered to have a low potential for adversely affecting the microbial functions of sandy loam and low humic content sand soils. Test substance can be characterised as having no long-term influence on nitrogen and carbon transformations in soils (de Vette, 2001).

Key value for chemical safety assessment

Short-term EC50 or LC50 for soil microorganisms:

130 mg/kg soil dw

Long-term EC10, LC10 or NOEC for soil microorganisms:

70 mg/kg soil dw

Additional information

Study 1. A study was conducted to determine the toxicity to microorganisms of the read across substance, quaternary ammonium compounds, benzyl C12-C16 (even numbered)-alkyldimethyl chlorides (C12-16 ADBAC), according to OECD Guideline 216, in compliance with GLP. A nitrogen transformation test was used in this experiment. Analytical determination was performed for the test substance. The concentrations ranged from 0, 50, 100, 200, 400, 800, 1600, 3200 and 6400 mg a.i./kg soil dw. The activity of the micro-organisms transforming nitrogen in soil was slightly inhibited at 50 mg a.i./kg soil dw. Denitrifying microorganisms were not affected at concentrations ranging from 400 to 3200 mg a.i./kg soil dw whereas the microorganisms responsible of the formation of nitrate were inhibited at these concentrations. The denitrifying microorganisms were inhibited at 6400 mg a.i./kg soil dw because after 28 days only a limited amount of the nitrate was removed. Based on the results of the read across study, the 28 d EC50 calculated was 130 mg a.i./kg with 95% confidence limits of 80 mg a.i./kg and 190 mg a.i./kg. The 28 d EC10, EC20 and EC80 of test substance were 70, 90 and 200 mg a.i./kg respectively (van Ginkel, 2004).

Study 2. A study was conducted to determine the toxicity to soil microorganisms of the read across substance, quaternary ammonium compounds, benzyl C12-C16 (even numbered)-alkyldimethyl chlorides (C12-16 ADBAC), according to OECD Guideline 216 and 217, and US EPA OPPTS 850.5100, in compliance with GLP. The effects of the test substance on carbon mineralization and nitrogen transformation activity of soil micro-organisms in a sandy loam soil and a low humic content sand soil were investigated in a 28 day study. Fifty grams dry weight of soil samples were mixed with lucerne meal and placed in 100 mL bottles. The samples were incubated in the dark at 20±2°C for 28 days. The moisture content of the samples was checked weekly. Samples were dosed with test substance at concentrations 0, 10, 100 and 1,000 mg a.i./kg soil dw. No analytical determination was performed for the test substance. CO2 evolution was determined on Days 5 – 8 and 25 – 28. Based on the results of the read across study, the difference in CO2 production and nitrogen transformation between the treated and untreated soil samples did not exceed 25% after 28 d of incubation. The highest inhibition recorded was 82.5% in the nitrite formation rate after 5 d at 10 mg a.i./kg soil dw in the sandy loam soil. After 28 d of incubation, however, no relevant effect was observed (i.e. less than 25% reduction). The test substance was therefore considered to have a low potential for adversely affecting the microbial functions of sandy loam and low humic content sand soils. Test substance can be characterised as having no long-term influence on nitrogen and carbon transformations in soils (de Vette, 2001).