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Diss Factsheets

Administrative data

Endpoint:
adsorption / desorption
Remarks:
adsorption
Type of information:
experimental study
Adequacy of study:
key study
Study period:
21 May 1996 to 19 August 1996
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP study conducted in accordance with a scentifically acceptable method with GLP certificate.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1996
Report date:
1996

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
The determination was carried out using an HPLC screening method. The procedure employed is that outlined in the draft "HPLC-Screening Method for the Determination of the Adsorption Coefficient on Soil - Comparison of Different Stationary Phases", W Kordel, J Stutte and G Kotthoff, Fraunhofer - Institut fur Umweltchemie and Okotoxikologie.
GLP compliance:
yes (incl. QA statement)
Type of method:
HPLC estimation method
Media:
soil/sewage sludge

Test material

Constituent 1
Chemical structure
Reference substance name:
N1-(5-methylhexan-2-yl)benzene-1,4-diamine
Cas Number:
63302-43-2
Molecular formula:
C13H22N2
IUPAC Name:
N1-(5-methylhexan-2-yl)benzene-1,4-diamine
Details on test material:
Sponsor's identification: TRAE
Description: Very dark purple solid block
Label: Distilled TRAE Y-775 Jan30, 96 Naugatuck Rhyang
Date received: 22 April 1996
Specific details on test material used for the study:
Details on properties of test surrogate or analogue material (migrated information):
Not applicable
Radiolabelling:
no

Study design

Test temperature:
No data

HPLC method

Details on study design: HPLC method:
Determination of retention time:
The sample, formamide and reference standard solutions were injected in duplicate using the following HPLC parameters:
Column: Zorbax CN (250 x 4.6 mm id)
Mobile phase: pH 4.55 : acetonitrile:0.06M potassium dihydrogen orthophosphate (50:50) adjusted to pH 4.55 using orthophosphoric acid
pH 8.78 : acetonitrile:water (50:50)
Flow rate: 1 ml/min
Injection volume: 25 ul
Wavelength: dead time and references - 210 nm, sample - 240 nm
Temperature: 22 + 2 degrees C

As it was expected that TRAE would show a mode of dissociation, the determination as carried out using mobile phases of varying pH in order to measure the retention of both associated and dissociated species.

Calibration
Organic reference standards were prepared in acetonitrile at the concentrations indicated.

Sample
An aliquot (0.0489 g) of test material was diluted to 100 ml with acetonitrile.

Dead time
The dead time was determined by measuring the retention time of a 224 mg/l solution of formamide (purity 99.5%*).

Construction of calibration curve:
A calibration curve was constructed from the retention time data of the formamide and reference standard solutions. The capacity factors (k), for
the reference standards were calculated.

Adsorption coefficient or sample:
Capacity factors were calculated from the retention time data. Log10 Koc values were then determined with reference to the calibration curves.


Batch equilibrium or other method

Details on sampling:
Not applicable
Details on matrix:
Not applicable
Details on test conditions:
Not applicable
Computational methods:
Not applicable

Results and discussion

Adsorption coefficientopen allclose all
Type:
Koc
Value:
271
Remarks on result:
other: At pH = 4.55
Type:
log Koc
Value:
2.43
Remarks on result:
other: At pH = 4.55
Type:
Koc
Value:
8 280
Remarks on result:
other: At pH = 8.78
Type:
log Koc
Value:
3.92
Remarks on result:
other: At pH = 8.78

Results: HPLC method

Details on results (HPLC method):
Dead time
The retention times determined for formamide are shown below:

pH 4.55
Retention time (min) for injection 1 and injection 2 = 2.661. Mean = 2.661

pH 8.78
Retention time (min) for injection 1 = 2.720, for injection 2: 2.723. Mean = 2.722

The retention times obtained for the calibration standards are detailed under any other information below.




Results: Batch equilibrium or other method

Adsorption and desorption constants:
Not applicable
Recovery of test material:
Not applicable
Concentration of test substance at end of adsorption equilibration period:
Not applicable
Concentration of test substance at end of desorption equilibration period:
Not applicable
Details on results (Batch equilibrium method):
Not applicable
Statistics:
Not applicable

Any other information on results incl. tables

The calibration curves are attached under background information below.

The retention times obtained for the calibration standards are shown below:

pH 4.55

Standard

Retention time (mins)

Injection 1

Injection 2

Mean

Simazine

4.540

4.538

4.539

Monolinuron

5.644

5.636

5.640

Propazine

5.707

5.705

5.706

Monuron

4.752

4.752

4.752

Atrazine

5.067

5.054

5.061

Phenamiphos

6.153

6.131

6.142

Baytan

5.636

5.620

5.628

Linuron

6.674

6.662

6.668

Endosulfan alcohol

6.604

6.604

6.604

Disulfoton

10.737

10.695

10.716

Monceren

10.907

10.906

10.907

Fenoxaprop-ethyl

11.204

11.149

11.177

Alpha-endosulfan

12.539

12.514

12.527

Pentachloronitrobenzene

11.78

11.767

11.774

Cyfluthrin

23.325

23.145

23.235

pH 8.78

Standard

 

Retention time (mins)

Injection 1

Injection 2

Mean

Simazine

4.451

4.453

4.452

Monolinuron

5.553

5.558

5.556

Propazine

5.603

5.604

5.604

Monuron

4.721

4.721

4.721

Atrazine

4.980

4.985

4.983

Phenamiphos

6.152

6.161

6.157

Baytan

5.637

5.646

5.642

Linuron

6.606

6.612

6.609

Endosulfanalcohol

6.749

6.748

6.749

Disulfoton

10.680

10.707

10.694

Monceren

11.127

11.135

11.131

Fenoxaprop-ethyl

11.378

11.394

11.386

Alpha-endosulfan

12.731

12.753

12.742

Pentachloronitrobenzene

12.081

12.093

12.087

Cyfluthrin

25.165

25.203

25.184

The capacity factors, k, for the above standards were determined from the retention times. The capacity factors are shown in the tables below together with the literature values for Log10 koc.

pH 4.55

Standard

 

Capacity factor

k

Log10k

Log10Koc

Simazine

0.706

-0.151

1.77

Monolinuron

1.120

4.903E-02

1.78

Propazine

1.144

5.854E-02

1.94

Monuron

0.786

-0.105

1.99

Atrazine

0.902

4.492E-02

2.11

Phenamiphos

1.308

0.117

2.27

Baytan

1.115

4.727E-02

2.39

Linuron

1.506

0.178

2.62

Endosulfan-alcohol

1.482

0.171

2.99

Disulfoton

3.027

0.481

3.06

Monceren

3.099

0.491

3.53

Fenoxaprop-ethyl

3.200

0.505

3.87

Alpha-endosulfan

3.707

0.569

4.06

Pentachloronitrobenzene

3.424

0.535

4.29

Cyfluthrin

7.732

0.888

4.53

pH 8.78

Standard

Capacity factor

k

Log10k

Log10Koc

Simazine

0.636

-0.197

1.77

Monolinuron

1.041

1.759E-02

1.78

Propazine

1.059

2.489E-02

1.94

Monuron

0.735

-0.134

1.99

Atrazine

0.831

-8.051E-02

2.11

Phenamiphos

1.262

0.101

2.27

Baytan

1.073

3.057E-02

2.39

Linuron

1.428

0.155

2.62

Endosulfan-alcohol

1.480

0.170

2.99

Disulfoton

2.929

0.467

3.06

Monceren

3.090

0.490

3.53

Fenoxaprop-ethyl

3.184

0.503

3.87

Alpha-endosulfan

3.682

0.566

4.06

Pentachloronitrobenzene

3.441

0.537

4.29

Cyfluthrin

8.254

0.917

4.53

Samples

The retention times of the test material are shown in the tables below:

pH 4.55

Injection

 

Retention time

(mins)

Capacity

Factor k

Log10k

Log10Koc

1

6.168

1.318

0.120

2.44

2

6.153

1.312

0.118

2.43

Mean Log10 Koc = 2.43

Koc = 271

pH 8.78

Injection

 

Retention time

(mins)

Capacity

Factor k

Log10k

Log10Koc

1

12.782

3.697

0.568

3.92

2

12.716

3.672

0.565

3.91

Mean Log10 Koc = 3.92

Koc = 8280

Applicant's summary and conclusion

Validity criteria fulfilled:
not specified
Conclusions:
The soil adsorption coefficient (Koc) values of the test substance are as follows:
pH 4.55: Koc = 271, Log10 Koc = 2.43
pH 8.78: Koc = 8280, Log10 Koc = 3.92
Executive summary:

The soil adsorption coefficient of the test substance was determined using a HPLC screening method.

As it was expected that TRAE would show a mode of dissociation, the determination as carried out using mobile phases of varying pH in order to measure the retention of both associated and dissociated species.

The soil adsorption coefficient (Koc) values of the test substance are as follows:

pH 4.55: Koc = 271, Log10 Koc = 2.43

pH 8.78: Koc = 8280, Log10 Koc = 3.92