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Adsorption / desorption

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Reference
Endpoint:
adsorption / desorption: screening
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From January 25, 2010 to January 27, 2010
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Remarks:
Meets the requirements of GLP. There are no deviations from the recommended guideline.
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
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
GLP compliance:
yes (incl. QA statement)
Type of method:
HPLC estimation method
Media:
soil/sewage sludge
Radiolabelling:
no
Test temperature:
25 ± 1 ºC
Details on study design: HPLC method:
EQUIPMENT
- Apparatus: HPLC
- Type, material and dimension of analytical (guard) column: Reprosil-Pur CN Dr. Maisch, 4.6 mm i.D., 125 mm length, particle size 3 µm
- Detection system: UV (Dionex, UVD 170S)

MOBILE PHASES
- Type: methanol/water (55/45% v/v)
- Solutes for dissolving test and reference substances: mobile Phase

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

REFERENCE SUBSTANCES
- Identity: Sodium nitrate, Phenole, Methylbenzoate, 3,5-Dinitrobenzamide, Naphthaline, 1,2,3-Trichlorbenzene, Pyrazophos

DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 20 µL of 125 mg/L test substance solution

- Quantity of reference substances: 20 µL of the following reference mix.
Sodium nitrate (2.00 mq/L), Phenole (4.00 mq/L), Methylbenzoate (2.00 µL/L), 3,5-Dinitrobenzamide (2.00 mq/L), Naphthaline (2.00 mg/L), 1,2,3-Trichlorbenzene (4 00 mq/L) and Pyrazophos(6.00 mq/L)

- Intervals of calibration: the item reference mix was injected at the beginning at the end of the test.

REPETITIONS
- Number of determinations: 3 injections were measured from the reference item mix, 3 injections from the test item solution and again 3 injections from the reference mix
Key result
Type:
log Koc
Value:
3.152 dimensionless
Temp.:
25 °C
Details on results (HPLC method):
- Retention times of reference substances used for calibration: see table 1
- Details of fitted regression line (log k' vs. log Koc): r2 = 0.9534
- Graph of regression line attached: yes
- Average retention data for test substance: see table 2

Table 1: Retention Times Reference

Compound

RT1

min.

RT2

min.

RT3

min.

RT4

min.

RT5

min.

RT6

min.

Sodium nitrate

1.159

1.167

1.177

1.173

1.172

1.169

Phenole

2.933

2.935

2.936

2.936

2.938

2.933

Methvlbenzoate

3.368

3.369

3.369

3:370

3.375

3 373

3,5-Dinitrobenzamide

3.542

3.543

3.545

3.548

3.551

3.549

Naphthaline

5.228

5.227

5.222

5.233

5 238

5.236

1,2,3-Trichlorbenzene

6.644

6.651

6.641

6.662

6.653

6.659

Pyrazophos

9.183

9228

9.191

9.227

9.224

9.205

 

Table 2: Retention Times and Areas Test Substance 

Peak Test Item

RT Peak

1

Area Peak 1

RT Peak

2

Area Peak 2

RT Peak

3

Area Peak 3

 

min.

mAU*min.

min.

mAU*min.

min.

mAU*min.

Measurement1

3.577

2 6588

5.747

19.2621

6.487

87.1221

Measurement 2

3.578

1.2874

5.748

19.1548

6.484

85.7158

Measurement 3

3.579

1.2942

5.748

19.0839

6.490

84.8416

Mean

3.578

1.7468

5.74B

19.1669

6.487

85.8932

Standard deviation

0.001

0.7898

0.001

0.0897

0.003

1.1505

 

Table 3: Capacity Factor, log Capacity Factor, log KocTest Substance 

Peak 1 Test Item

k'

log k'

logKoc

Measurement 1

2.0586

0.3136

1.964

Measurement 2

2.0594

0.3137

1.964

Measurement 3

2.0503

0.3139

1.965

Mean

 

 

1.964

Standard deviation

 

 

0.001

Peak 2 Test Item

k'

log k'

logKoc

Measurement 1

3 9141

0.5926

2.927

Measurement 2

3.9149

0.5927

2.927

Measurement 3

3.9149

0.5927

2.927

Mean

 

 

2.927

Standard deviation

 

 

0.000

Peak 3 Test Item

k'

logk’

logKoc

Measurement 1

4.5466

0.6577

3.152

Measurement 2

4:5442

0.6575

3.151

Measurement 3

4 5494

0.6560

3.152

Mean

 

 

3.152

Standard deviation

 

 

0.001

Validity criteria fulfilled:
yes
Conclusions:
Log Koc of the test substance was 3.152.
Executive summary:

An estimation of the adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC) for the test substance was performed. The calibration graph log Koc versus log k’ has been established with six references substances recommended in the OECD guideline 121. The dead time to was measured by using sodium nitrate as un-retained compound. Three injections were measured from the reference item mix, three injections from the test substance solution and again three injections from the reference item mix. The values of log Koc derived of the individual measures were in the range of 0.25 log unit and the correlation log k’/log Koc was sufficiently accurate, as calibration gave a coefficient of determination r2= 0.9534.

The chromatogram of the test substance gave three peaks, two main peaks and another small peak. The corresponding log Koc were determined as 1.964 (peak 1), 2.927 (peak 2), and 3.152 (peak 3). Although area is not necessarily correlated to absolute concentration if a UV detector is used, it is believed that the test substance consists mainly of the third peak, indicating that the log Koc should be regarded as 3.152.

Description of key information

Key study: Experimental result: Test according to OECD 121 and EU method C.19. GLP study.

Log Koc:  3.152

Key value for chemical safety assessment

Additional information

Key study: Experimental result: Test according to OECD 121 and EU method C.19.

An estimation of the adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC) for the test substance was performed. The chromatogram of the test substance gave three peaks, two main peaks and another small peak. The corresponding log Koc were determined as 1.964 (peak 1), 2.927 (peak 2), and 3.152 (peak 3). Although area is not necessarily correlated to absolute concentration if a UV detector is used, it is believed that the test substance consists mainly of the third peak, indicating that the log Koc should be regarded as 3.152.