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Physical & Chemical properties

Partition coefficient

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Reference
Endpoint:
partition coefficient
Type of information:
experimental study
Adequacy of study:
key study
Study period:
This study was conducted between 23 September 2016 and 23 March 2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: The study is considered to be a reliability 1 as it has been conducted according to OECD TG 117 (HPLC method) and in compliance with GLP.
Qualifier:
according to guideline
Guideline:
OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
Version / remarks:
13 April 2004
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method A.8 (Partition Coefficient - HPLC Method)
Version / remarks:
EC 440/2008 of 30 May 2008
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Type of method:
flask method
Partition coefficient type:
octanol-water
Specific details on test material used for the study:
Identification : μ(5-amino-1,3,3-trimethylcyclohexylamine-N,N')hexafluorodiboron
Appearance/Physical state: Clear colorless liquid
Batch : AEF0009100
Purity : 51.8%
Expiry date : 29 August 2017
Storage conditions: Room temperature, in the dark.
Analytical method:
gas chromatography
Key result
Type:
log Pow
Partition coefficient:
< -2.34
Temp.:
21 °C
pH:
3.2
Type:
Pow
Partition coefficient:
< 0.004
Temp.:
21 °C
pH:
3.2
Details on results:
Preliminary Estimate

Approximate solubility in n-octanol: 2.7 x 10^-2 g/L
Approximate solubility in water: >119 g/L
Approximate Pow: <2.27 x 10^-4
Log10 Pow: <-3.65


 Definitive Test

The mean peakareasobtained for the standard, stock and sample solutions are shown in the following two tables:

Table 1            Organic Phase

Solution

Mean peakarea

Standard 173 mg/L

2.1940 x 106

Standard 165 mg/L

2.2583 x 106

Organic phase matrix blank

None detected

Sample 1

None detected

Sample 2

None detected

Sample 3

None detected

Sample 4

None detected

Sample 5

None detected

Sample 6

None detected

 

Table 2 Aqueous Phase

Solution

Mean peakarea

Standard 81.9 mg/L

7.2227 x 105

Standard 83.0 mg/L

7.3681 x 105

Aqueous phase matrix blank

None detected

Sample 1

1.9485 x 106

Sample 2

2.0936 x 106

Sample 3

2.2823 x 106

Sample 4

2.2263 x 106

Sample 5

2.3217 x 106

Sample 6

2.5078 x 106

Stock solution A

2.3670 x 106

Stock solution B

2.2846 x 106

The total weights (mg) and analyzed concentration (mg/L) of the respective phases are shown in the following table. As no test item peak was detected within the organic phase a limit value of the lowest detectable standard within the linearity was used (10 mg/L):

Table 3

Sample number

Total weight (mg)*

Organic phase

Aqueous phase

% recovery

Analyzed concentration (mg/L)

Weight (mg)†

Analyzed concentration (mg/L)

Weight (mg)†

pH

1

105.1

<10

<0.400

2.20 x 103

88.1

3.21

~84.2

2

105.1

<10

<0.400

2.37 x 103

94.6

3.22

~90.4

3

141.9

<10

<0.270

2.58 x 103

139

3.20

~98.3

4

141.9

<10

<0.270

2.52 x 103

136

3.22

~95.9

5

70.96

<10

<0.540

2.62 x 103

70.8

3.26

~101

6

70.96

<10

<0.540

2.83 x 103

76.5

3.26

~109

pH of n-octanol saturated water:       6.7
pH of stock solution:                         3.2
Temperature:                                     21.0 ± 0.5°C

The partition coefficient determined for each sample is shown in the following table:

Table 4

Sample number

Organic/aqueous volume ratio

Partition coefficient

Log10Pow

Mean partition coefficient

1

1:1

<4.54 x 10-3

<-2.34

<4.54 x 10-3

2

<4.23 x 10-3

<-2.37

3

1:2

<3.88 x 10-3

<-2.41

<3.98 x 10-3

4

<3.98 x 10-3

<-2.40

5

2:1

<3.81 x 10-3

<-2.42

<3.81 x 10-3

6

<3.53 x 10-3

<-2.45

Mean Pow :<3.81x 10-3                    log10Pow:<-2.34                  

 Validation

The aqueous linearity of the detector response with respect to concentration was assessed over the nominal concentration range of50to400mg/L. The results were satisfactory with a correlation coefficient (r) of 0.998 being obtained. Theorganiclinearity of the detector response with respect to concentration was assessed over the nominal concentration range of10to200mg/L. The results were satisfactory with a correlation coefficient (r) of0.998being obtained.

Discussion

The determination of partition coefficient was performed using the shake-flask method. This was due to the expected partition coefficient obtained in the preliminary assessment.

The stock solution was prepared in n-octanol saturated water in place of water saturated
n-octanol. This was due to the relative insolubility of the test item in the organic phase. This issue has been considered to have had a negligible impact on the overall result and has been considered to be more appropriate to obtain a more realistic partition coefficient value.

Analysis was carried out using unbuffered n-octanol saturated water. The pH of the stock solution decreased from pH 7 (n-octanol saturated water) to pH 3 (stock solution), this also occurred at lower concentrations (approximately 2.5 mg/L), suggesting that the pH change was due to the test item and not an impurity. The test item was still in its unionised form at pH 3, and therefore this had no impact on the test.

Multiple peaks were integrated during analysis, all peaks were processed as a group for quantification.

As no test item peak was detected within the organic phase a limit value of the lowest detectable standard within the linearity was used (10 mg/L)


* From analysis of the stock solution

† From analysis of therespective phase

Conclusions:
The partition coefficient of the test item has been determined to be less than 3.81 x 10^-3 at 21.0 ± 0.5 °C, log10 Pow< -2.34.
Executive summary:

The general physico-chemical properties of μ(5-amino-1,3,3-trimethylcyclohexylamine-N,N')hexafluorodiboron have been determined. 

Partition Coefficient (n-octanol/water). The partition coefficient(Pow)of the test item has been determined to beless than 3.81 x 10-3at21.0±0.5°C, log10Pow<-2.34, using the shakeflask method, designed to be compatible with Method A.8 Partition Coefficient of Commission Regulation (EC) No 440/2008 of 30 May 2008andMethod 107 of the OECD Guidelines for Testing of Chemicals, 27 July 1995. 

Description of key information

Key value for chemical safety assessment

Log Kow (Log Pow):
-2.34
at the temperature of:
21 °C

Additional information