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Environmental fate & pathways

Adsorption / desorption

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Reference
Endpoint:
adsorption / desorption: screening
Type of information:
experimental study
Adequacy of study:
key study
Study period:
2014-03-10
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
EU Method C.19 (Estimation of the Adsorption Coefficient (KOC) on Soil and Sewage Sludge Using High Performance Liquid Chromatography (HPLC))
Deviations:
no
Qualifier:
according to guideline
Guideline:
OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Type of method:
HPLC estimation method
Radiolabelling:
no
Test temperature:
25 °C
Details on study design: HPLC method:
EQUIPMENT
- Apparatus: HPLC System Agilent 1100 series
- Type, material and dimension of analytical (guard) column: commercially available cyanopropyl solid phase containing lipophilic and polar moieties, stainless steel, 150 mm x 4.6 mm, particle size: 5 µM

MOBILE PHASES
- Type: methanol/distilled water 70:30 % (v/v)
- pH: 5.4

DETERMINATION OF DEAD TIME
- Method: by inert substances which are not retained by the column

REFERENCE SUBSTANCES
- Identity: Acetanilide, Atrazin, Triadimenol, Linuron, Pyrazophos, Diclofop-methyl, 4,4`-DDT

DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 50 µL (0.41 µg)
- Quantity of reference substances: 10 µL (0.2 - 1.16 µg)

REPETITIONS
- Number of determinations: 2

EVALUATION
- Calculation of capacity factors k': according to OECD TG 121
- Calculation of retention times: were measured
- Determination of the log Koc value: according to OECD TG 121
Key result
Type:
log Koc
Value:
> 5.6 dimensionless
pH:
5.4
Temp.:
25 °C
Details on results (HPLC method):
- Average retention data for test substance: retention time = 10.44 (1st measurement), 10.48 (2nd measurement)

Table 1: Determination of the dead time t0 


















Dead time marker 



tR/min 


1st injection 



tR/min 


2nd injection 



tR/min 


3rd injection 



Formamide 



1.72



1.72



1.72



 


 dead time t0=1.72 min 


 


Table 2: Calibration data 1st injection 






























































Calibration substance 



tR/min 





Log k 



Log Koc 



Acetanilide 



1.89



0.10



-1.02



1.25



Atrazin  



1.96



0.14



-0.85



1.81



Triadimenol



2.11



0.23



-0.64



2.40



Linuron 



2.28



0.32



-0.49



2.59



Pyrazophos 



2.61



0.51



-0.29



3.65



Diclofop-methyl 



2.66



0.55



-0.26



4.20



4,4’-DDT



3.43



0.99



0.00



5.63



 


Regression: log Koc = a+ b · log k 


Parameters: a=5.17, b=4.13, r2=0.9432 


 


Table 3: Log Pow of the test item 1st injection 




















 



tR/min 





Log k 



Log Koc 



Test item 



10.44



5.07



0.70



>5.6 1)


(8.1) 2)



1) above the highest log Koc value of calibration substances (DDT) 


2) via extrapolation


 


Table 4: Calibration data 2nd injection 






























































Calibration substance 



tR/min 





Log k 



Log Koc 



Acetanilide 



1.89



0.10



-1.02



1.25



Atrazin  



1.96



0.14



-0.85



1.81



Triadimenol



2.11



0.23



-0.64



2.40



Linuron 



2.28



0.33



-0.49



2.59



Pyrazophos 



2.61



0.52



-0.29



3.65



Diclofop-methyl 



2.67



0.55



-0.26



4.20



4,4’-DDT



3.43



0.99



0.00



5.63



 


Regression: log Koc = a+ b · log k 


Parameters: a=5.17, b=4.12, r2=0.9424 


 


Table 5: Log Pow of the test item 2nd injection 




















 



tR/min 





Log k 



Log Koc 



Test item 



10.48



5.08



0.71



>5.6 1)


(8.1) 2)



1) above the highest log Koc value of calibration substances (DDT) 


2) via extrapolation


 


Within two injections, the adsorption coefficient Koc of the test item was determined to be: 


Log Koc  > 5.6 1) (log Koc  = 8.1) 2)


1) above the highest log Koc value of calibration substances (DDT) 


2) via extrapolation

Validity criteria fulfilled:
yes
Conclusions:
The log Koc of the test substance was determined to be > 5.6.
Executive summary:

A study was conducted in accordance with OECD 121 to determine the adsorption coefficient of the test substance using the HPLC method. The adsorption coefficient of the test substance was derived from its retention time and the calibration graph. The retention time of the test item was above the retention time of the highest calibration standard (log Koc 5.63) and thus out of the calibration range. Therefore, the adsorption coefficient of the test substance was determined to be above 5.6.

Description of key information

The adsoprtion coefficient (log Koc) of the test item was determined to be greater than 5.6 according to OECD Guideline 121. Since the log Koc is greater than 3 the test substance has an adsorption potential.

Key value for chemical safety assessment

Koc at 20 °C:
398 107

Additional information

A study was conducted in accordance with OECD 121 to determine the adsorption coefficient of the test substance using the HPLC method. The adsorption coefficient of the test substance was derived from its retention time and the calibration graph. The retention time of the test item was above the retention time of the highest calibration standard (log Koc 5.63) and thus out of the calibration range. Therefore, the adsorption coefficient of the test substance was determined to be above 5.6.