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Chemosphere, Vol. 31, Nos 9-12. pp. 2139-2152, 1998 0 1998 Elsevier Science Ltd
All rights reserved. Printed in Great Britain 0045.6535/98 $19.00+0.00
PII: SO0456535(98)00276-S
PARTITION CONSTANTS OF CHLORINATED DIBENZOFURANS AND
DIBENZO-P-DIOXINS
Harrie A. J. Covers and Hildo B. Krop
Department of Environmental and Toxicological Chemistry, ARISE, University of Amsterdam,
Nieuwe Achtergracht 166, 1018 WV Amsterdam, The Netherlands
Abstract
Vapour pressure, aqueous solubility, Henry law constant, n-octanol- and sediment-water partition
coefficient and bioconcentration factor of all chlorinated dibenzofurans (PCDF) and dibenzo-p-dioxins
(PCDD), in addition to those of the parent compounds DF and DD, were calculated via the SOFA (SOlubi-
lity parameters for Fate Analysis)- model. The derivation of these 1272 values was based on 120
experimental data. Mean deviation of calculated values from experimental data amounted to 0.39,0.25, 0.3 1,
0.19, 0.34 and 0.18 log units for the properties mentioned. The values of all compounds were tabulated.
Variation of values within isomer groups turned out to be the highest for vapour pressure of the tetra
substituted group, but were below 1.40 orders of magnitude. Variation in the complete series amounted to
7.78 orders at a maximum, again for vapour pressure. Accurate, almost linear, relationships were established
between the n-octanol-water partition coefficient and aqueous solubility and sediment-water partition
coefficient, whereas a parabolic relationship turned out to hold with the bioconcentration factor.
01998 Elsevier Science Ltd. All rights reserved
Introduction
The last few years reviews have been published on the fate determining conservative properties of
PCDF/D, collected, o.a., in the handbook of Mackay, Shiu and Ma [l]. Yet the data-sets are incomplete,
even at the level of the seventeen 2378-substituted congeners.
We have recently developed the SOFA model using methyl-chloro-benzenes as pilot compounds [2] and
applied it succesfully to the compound series of polychlorinated biphenyls (PCBs) [3], benzyltoluenes
(TCBTs) [4] and PCDF/Ds [5,6].
The model allows for a consistent description of all equilibrium partitioning properties and of the
relationships between them. Partition properties and their relationships are explained in terms of the single
2139
2140
component parameters molar liquid volume (V/cm3.mol’), heat of vaporization (AH/cal.mol-‘) and solubility
parameter or cohesion energy density (6/[cal.cm-3]“2), derived from these by 6’= (AH-RT)N, with R (Cal.
moll’.deg-‘) as gas constant and T (K) as absolute temperature. These key parameters are included in the
model for both the solute and the phases, they are partitioning over. So far predictions turned out to be
accurate, enabling the discrimination between isomer values even at the level of accurate chromatographic
retention data. SOFA is a thermodynamic lattice model. The quantification of the specific enthalpic and
entropic contributions to the partitioning process and of its temperature dependence are possible.
In order to complete available data sets the (subcooled) liquid vapour pressure (P/Pa), aqueous solubility
(S/mol.l“), Henry law constant (H /kPa.m’.mol-‘), n-octanol-water partition coefficient (K,,), sediment (par-
title)-water partition coefficient (K,,) and bioconcentration factor or biotic (guppy) lipid-water partition
coefficient ( Kba ) at 25°C are calculated for PCDFiD and their parents DF and DD.
Method
The SOFA model has been explained in detail elsewhere [2,3,4,5,6]. The basic equations for the
vapour pressure (P,), solubility (S,J and the partition coefficients (K,,,,) of compound i over the phases s
(= n-octanol, o; = sediment, p; or = biotic lipid, b) and water (w) read:
In P, = a, +c,,,ln A, -b,AH,/RT (1)
In S,,, = -v,[&~ +&’ -2~,~,~,,,,,(~,.,,,~,+6,)~(6,+~~,,,~~~)1~~~
-X,,, -c,,,,,ln A, -ln(V,/VJ +V,N, -1 -ln(VJ103) (2)
ln K,,,,= -V,[6,2 +&* -~~,S,C,,,,,(C,.,,,S,+~,)/(~,+C~.,,~S,)I’RT
+xw,w +c3,,.,w In A, +V,N, -V,N, (3)
Henry law constants can be derived directly from vapour pressure and solubility data by a log H= 1ogP -logs
type relationship.
Apart from the key descriptors (AH, V and 6) the following additional constants appear in these equations:
- a, X and c1 containing terms quantify (exchange) substitutional and orientational disorder entropic
contributions, where Ai is a molecular descriptor accounting for the number of orientations a solute molecule
2141
can take at a lattice site,
- b, c, and c2 containing terms quantify (exchange) enthalpic contributions: when c,=l and c,=l simple
Scatchard-Hildebrand solubility parameter models result. Deviations from 1 indicate specific interactions.
such as hydrogen bond formation, leading to non-ideal behaviour,
- V,N, containing terms quantify combinatorial entropy effects, accounting for size differences between
solute and solvent molecules similar to Flory-Huggins models.
AH, V and 6 values of all (PC)DF/D solutes have been derived from gas chromatographic retention data [6].
A, values of these solutes were directly derived as previously from the numbers of various atoms within a
molecule.
V and 6 values of s and w phases were all taken from the literature [2,3,4,5,6], except for the sediment
phase (p), where methylsalicylate was taken as a model compound with V = 130.43 cm3.mol and 6 = 10.6
[cal.cm-3]“2 [7,8].
a, b, X and c parameters are constants characteristic for the entire series of compounds or the series in
combination with a certain phase. They were determined by nonlinear regression fitting procedures. Starting
values for these constants were taken from previous calculations or theoretical considerations.
All calculations were carried out by the GWBASIC SOFA software on a Highscreen Pentium personal
computer with a 60 Mhz Intel microprocessor. Once key descriptors are available less than 30 minutes were
required for nonlinear regression. The programme provides as statistical data: the number of data points (N),
mean deviation of calculated values from experimental data (<dev>), correlation coefficient (r, not corrected
for degrees of freedom) and 95% confidence limits of derived a, b, X and c constants.
From calculated values of log K,,, log S,, log Krw and log Kbw, relationships between these properties were
calculated using the SGPLUS (1993, OASIS b.v., Nieuwe Gein, The Netherlands) software.
Results and discussion
General
Calculations resulted in a set of 1272 values derived from only 120 experimental data tabulated in
Table 1. a, b, X and c constants derived (not shown here) were not statistically significant in some cases and
the corresponding term could be removed from eqs. (l)-(3). This holds for c3 orientational exchange entropy
terms of K,, and Krw in contrast to the P, S, H and K,,,,, cases. The c,,~ constant of K,,, Krw and K,, could
be fixed at the value of 1 indicating the absence of strong interaction between solute and solvent in the
relatively moderately or a-polar s phases. Some statistics of these derivations are included in the last three
lines of Table 1. Mean deviations from experimental data are of the same order of magnitude as the errors
in experimental data. However both experimental and calculational errors turn out to be too high in many
2142
cases in order to reliably distinguish (small) isomer differences. Correlation coefficients are high when the
range of values is sufficiently wide.
Relationships between partition constants
Previously, it has already been shown and explained that an accurate non-linear relationship between
calculated log K,,v and log K,, values exists [9], especially when the DF and DD series are treated
separately. The -log S, or IogK,, and log K,, relationships turned out to be close to linearity. Relationships
are summarized in equations (4)-(6):
Log K,, = -(l. 177kO.193) +(2.010+0.062).Log K,, -(0.164+0.005).(Log K,$
N=136 PCDFs; r=0.945; s.e.r.=0.06; F=560
Log KbW = -(4.534+0.425) +(3.065+_0.127).Log K,, -(0.232&0.009).(Log K,)’
N=76 PCDDs; r=0.948; s.e.r.=0.07; F=322
-Log S, = -(0.476*0.223) +(0.977*0.072).Log K,, +(0.023&0.006).(Log K,,J’
N=136 PCDFs; r=0.998; s.e.r.=0.07; F=16690
-Log S, = -(0.005+0.341) +(0.971fO.l02).Log K,, +(0.015fO.O08).(Log K,,)*
N=76 PCDDs; r=0.998; s.e.r.=0.06; F=9528
Log K,, = -( 1.393+0.061) +( 1.288+0.02O).Log K,, +(0.008+0.002).(Log K,,)’
N=l36 PCDFs; r=0.9999; s.e.r.=0.02; F=268747
Log K,, = -( 1.062+0.133) +( 1.173?0.04O).Log K,, +(0.017fO.O03).(Log K,,,)’
N=76 PCDDs; r==O.9998; s.e.r.=0.02; F=90744
(44
(4b)
(54
(64
(6b)
The accuracy of these relationship is higher then can be obtained by correlating experimental data. The
experimental data have inaccuracies slightly higher than standard errors of regression (ser.) of equations
(4)-(6). The high accuracy of the latter are caused by the similarities of the model equations (2)-(3) and the
use of identical key descriptors AH, V and 6 for the (PC)DD/F in these equations.
Specific comments
As Table 1 shows, the highest (but still small) variation within isomer groups, not exceeding 1.39
2143
orders of magnitude, was calculated for the vapour pressure of the tetra-substituted compounds, whereas the
highest variation in the complete series amounts to 7.78 orders (for vapour pressure again).
Only 2 orders of magnitude (or a factor of 100) variation is present in the complete series for Henry law
constant and bioconcentration. The former is caused by compensating effects in vapour pressure and solubi-
lity, the latter by the solubility properties and entropic effects of lipids [9]. For Henry law constants of tetra-
chlorinated TCBTs much larger variation has been found, leading to large variation in the environmental fate
of these flexible and nonplanar isomers [4]. It can, therefore, be expected that PCDFiD isomers behave more
similarly in fate models. Yet, isomer differences for PCDD/F turned out to be important in the case of
chromatographic retention. SOFA performed quite well in the prediction of retention on different columns
[6]. It cannot be excluded that prediction of receptor binding affinities by SOFA, as currently under
development, may reveal substantial differences between isomers as well.
With respect to sediment-water partitioning, note the high K,, values, which are a consequence of the
specific sediments used in the experimental determination, which possibly were contaminated by mineral oil
[5]. Moreover, the experimental determination of these K,, values was based on a cosolvent method using
methanol-water mixtures as an aqueous phase and subsequent extrapolation to 0% methanol. It is not yet
clear whether high K,, values result from the methanolic influence on the sediment phase or that the
cosolvent method is more accurate than other methods suffering from difficulties in determining low amounts
of solute in the aqueous phase.
Finally, calculated bioconcentration factors are based on experimental data of congeners not showing
biotransformation [9,15]. Yet many other congeners may biotransform, expecially the non 2378 substituted
ones. In these cases calculated values of K,, have to be considered as (hypothetical) maximum values.
Table 1. Calculated and experimental (in italics) values of subcooled liquid vapour pressure and aqueous solubility, Henry law constant, n-octanol-water and sediment-water partition coefficient and lipid weight based bioconcentration factors in the guppy at 25°C of all 212 (PC)DF/D and statistics of the SOFA model.
Compound* -LogP” -LogSb -LogH’ LogK,wd LogK,,’ LogK,wf Pa mol.l-’ kPa.m3 l.kg-’
.mol-’
1. DF -0.91 3.43 1.67 3.68 3.45 4.08 -0.15 3.99 1.86 3.92 3.68
2. 1 0.06 4.16 1.92 4.33 4.35 4.46 4.33
3. 2 0.27 4.24 2.04 4.37 4.38 4.51 4.37
4. 3 0.31 4.22 2.11 4.35 4.34 4.53 4.35
5. 4 0.30 4.37 1.95 4.44 4.49 4.48 4.44
6. 12 1.29 5.13 2.17 5.10 5.40 4.74
2144
7. 13
8. 14
9. 16 1.16 5.00 2.16 5.03 5.31
10. 17 1.16 4.89 2.29 4.96 5.19
11. 18 1.36 4.97 2.40 4.99 5.22
12. 19 1.69 5.40 2.31 5.22 5.55
13. 23 1.55 5.20 2.36 5.11 5.39
14. 24 1.25 5.00 2.27 5.01 5.27
15. 26 1.37 5.13 2.25 5.09 5.38
16. 27 1.30 5.01 2.30 5.02 5.27
17. 28
18. 34
19. 36
20. 37
21. 46
22. 123 2.33 5.89 2.46 5.72 6.25
23. 124 2.09 5.72 2.39 5.64 6.15
24. 126 2.27 5.92 2.36 5.75 6.30
25. 127 2.19 5.83 2.37 5.70 6.23
26. 128 2.51 5.94 2.59 5.73 6.25
27. 129 3.04 6.37 2.68 5.96 6.54
28. 134 2.13 5.69 2.45 5.62 6.11
29. 136 2.07 5.57 2.52 5.44 6.00
30. 137 2.08 5.48 2.61 5.49 5.92
31. 138 2.15 5.54 2.62 5.52 5.96
32. 139 2.57 5.94 2.64 5.73 6.24
33. 146 2.21 5.67 2.55 5.60 6.07
34. 147 2.11 5.63 2.50 5.58 6.06
35. 148 2.27 5.70 2.59 5.60 6.08
36. 149 2.60 6.08 2.54 5.82 6.37
37. 234 2.57 6.10 2.49 5.83 6.40
38. 236 2.56 6.04 2.53 5.80 6.34
1.05 4.76 2.31 4.88
1.09 4.94 2.17 4.99
1.38 5.05 2.34 5.04 I.84 5.64 2.20 5.30
1.57 5.32 2.27 5.19
1.45 5.13 2.34 5.08
1.46 5.01 2.47 5.00
1.54 5.20 2.35 5.11
5.09
5.26
5.30
5.51
5.35
5.23
5.40
4.78
4.73 4.99
4.73
4.78
4.83 4.99
4.81
4.82
4.78
4.77
4.79 5.02
4.81 5.04
4.79
4.81
4.86
4.82 5.11
4.92
4.89
4.88
4.89
4.98
5.04
4.91
4.93
4.97
4.98
5.00
4.95
4.93
4.97
4.96
4.94
4.96
2145
39. 237 2.49 5.95 2.55 5.74 6.27 4.96
40. 238 2.44 5.97 2.49 5.76 6.30 4.94
41. 239 2.51 5.87 2.66 5.69 6.18 5.01
42. 246 2.37 5.77 2.62 5.64 6.12 4.99
43. 247 2.20 5.72 2.49 5.63 6.12 4.93
44. 248 2.24 5.74 2.51 5.64 6.14 4.94
45. 249 2.22 5.63 2.61 5.57 6.02 4.97
46. 346 2.73 6.12 2.63 5.82 6.37 5.01
47. 347 2.64 6.06 2.59 5.80 6.34 4.98
48. 348 2.43 6.05 2.40 5.81 6.38 4.91
49. 349 2.31 5.90 2.43 5.73 6.27 4.91
50. 1234 3.17 6.63 2.56 6.34 7.12 4.92
51. 1236 3.23 6.64 2.61 6.34 7.11 4.94
52. 1237 3.15 6.58 2.59 6.31 7.07 4.93
53. 1238 3.34 6.66 2.70 6.34 7.10 4.98
54. 1239 3.96 7.07 2.90 6.54 7.35 5.08
55. 1246 3.09 6.40 2.71 6.20 6.91 4.97
54. 1247 2.91 6.38 2.54 6.21 6.94 4.90
57. 1248 3.18 6.46 2.74 6.23 6.95 4.98
58. 1249 3.72 6.86 2.87 6.43 7.20 5.06
59. 1267 3.21 6.78 2.45 6.43 7.26 4.88
60. 1268 3.25 6.53 2.74 6.26 7.00 4.99
61. 1269 3.83 7.00 2.85 6.50 7.31 5.05
62. 1278 3.45 6.79 2.68 6.41 7.20 4.97
63. 1279 3.71 6.88 2.84 6.44 7.22 5.05
64. 1289 4.30 7.34 2.98 6.67 7.52 5.13
65. 1346 3.17 6.39 2.80 6.18 6.88 5.01
66. 1347 3.07 6.38 2.71 6.18 6.89 4.97
67. 1348 3.10 6.42 2.70 6.21 6.93 4.97
68. 1349 3.52 6.78 2.76 6.40 7.17 5.01
69. 1367 3.14 6.44 2.71 6.22 6.94 4.97
70. 1368 2.93 6.16 2.79 6.06 6.71 5.00
71. 1369 3.40 6.59 2.83 6.29 7.02 5.03
72. 1378 3.22 6.42 2.81 6.20 6.90 5.01
73. 1379 3.36 6.47 2.90 6.22 6.91 5.06
74. 1467 3.28 6.53 2.77 6.26 6.99 5.00
2146
75. 1468
76. 1469
77. 1478
78. 1678
79. 2346
80. 2347
81. 2348
82. 2367
83. 2368
84. 2378
85. 2467
86. 2468
87. 3467
88. 12346
89. 12347
90. 12348
91. 12349
92. 12367
93. 12368
94. 12369
95. 12378
96. 12379 4.54 7.56 3.00 7.00
97. 12389 5.02 7.99 3.04 7.22
98. 12467 3.96 7.22 2.76 6.84
99. 12468 3.96 6.95 3.02 6.67
100. 12469 4.54 7.38 3.17 6.88
101. 12478 4.05 7.28 2.79 6.87
102. 12479 4.31 7.33 2.99 6.87
103. 12489 4.86 7.76 3.11 7.09
104. 12679 4.55 7.66 2.90 7.06
105. 13467 4.16 7.23 2.95 6.82
106. 13468 3.92 6.92 3.01 6.65
107. 13469 4.39 7.32 3.08 6.86
108. 13478 4.09 7.26 2.85 6.85
3.16 6.24 2.93
3.54 6.66 2.90
3.34 6.55 2.81
3.42 6.67 2.76
3.61 6.84 2.79
3.43 6.81 2.64
3.35 6.82 2.55
3.55 6.95 2.61
3.23 6.62 2.62
3.43 6.87 2.57 3.79 6.87 2.93
3.36 6.65 2.73
3.12 6.32 2.82
3.84 7.01 2.85
4.10 7.27 2.85
3.92 7.2% 2.65
4.07 7.34 2.74
4.68 7.71 2.99
4.09 7.49 2.62
4.01 7.21 2.81
4.67 7.66 3.03
4.21 7.50 2.72
6.09
6.32
6.27
6.34
6.42
6.42
6.44
6.50
6.33
6.46
6.33
6.15
6.51
6.86
6.89
6.91
7.08
7.00
6.83
7.04
6.99
6.74
7.05
6.99
7.10
7.21
7.23
7.25
7.33
7.10
7.29 7.86
7.08
6.83
7.32
7.83
7.89
7.91
8.12
8.05
7.80
8.07
8.03 7. 77
8.01
8.31
7.82
7.55
7.83
7.86
7.84
8.12
8.10
7.78
7.54
7.81
7.82
5.06
5.06
5.02
5.00
5.02
4.96
4.92
4.95
4.94
4.93
4.99
5.01
5.05
4.88
4.80
4.84
4.95
4.80
4.86
4.97
4.84
4.95
4.98
4.84
4.94
5.02
4.85
4.94
5.01
4.91
4.92
4.93
4.98
4.88
2147
109. 13479
110. 13678
111. 14678
112. 23467
113. 23468
114. 23478
115. 23489
116. 123467
117. 123468
118. 123469
119. 123478
4.24 7.27 2.98
4.05 7.19 2.88
4.28 7.25 3.05
4.52 7.70 2.84
4.16 7.36 2.82
4.26 7.68 2.59 4.71 7.47 3.24
4.25 7.54 2.72
4.89 8.08 2.83
4.76 7.79 2.99
5.43 8.19 3.25
4.86 8.15 2.72 5.25 8.67 2.58
5.20 8.17 3.04
5.62 8.58 3.06
4.92 8.22 2.72 5.23 8.28 2.96
5.31 8.31 3.02
5.50 8.39 3.13
5.65 8.64 3.02
6.84
6.81
6.82
7.09
6.91
7.11
7.02
7.48
7.31
7.49
7.53
120. 123479
121. 123489
122. 123678
7.51
7.72
7.57
123. 123679
124. 123689
125. 123789
7.58
7.61
7.76
126. 124678 4.87 7.92 2.97 7.38
127. 124679 5.18 8.00 3.19 7.40
128. 124689 5.45 8.09 3.38 7.43
129. 134678 4.96 7.92 3.05 7.37
130. 134679 5.15 7.96 3.20 7.38
131. 234678 5.12 8.38 2.75 7.65
132. 1234678 5.60 8.76 2.85 5.85 9.40 2.46
5.99 8.80 3.19
6.14 8.86 3.29
6.18 9.20 3.00
8.01
133. 1234679
134. 1234689
135. 1234789
8.00
8.02
8.23
136. 12346789 6.74 9.64 3.11 8.60 6.15 9.28 2.88 8.78
7.80
7.77
7.76
8.15
7.90
8.20 8.05
8.07
8.72
8.47
8.70
8.80 8.83
8.74
9.03
8.85
8.84
8.87
9.08 9.28
8.58
8.57
8.58
8.55
8.54
8.96 8.56
9.48 9.97
9.43
9.45
9.76 9.78
10.30
4.93
4.89
4.96
4.89
4.87
4.79 5.14
4.84
4.61
4.66
4.78
4.57
4.70
4.72
4.58 4.95
4.69
4.74
4.71
4.66
4.75
4.84
4.69
4.75
4.59
4.26 4.46
4.38
4.42
4.32
3.88 10.49 3.90
137. DD 0.60 4.65 1.96 4.49 4.54 4.68 0.29 4.36 1.93 4.20 4.49
2148
138. 1
139. 2
140. 12
141. 13
142. 14
143. 16
144. 17
145. 18
146. 19
147. 23
148. 27
149. 28
150. 123
151. 124
152. 126
153. 127
154. 128
155. 129
156. 136
157. 137
158. 138
159. 139
160. 146
161. 147
162. 178
163. 237
164. 1234
165. 1236
166. 1237
167. 1238
1.66 5.43 2.24 5.17 1.12 4.92 2.20 4.75
1.63 5.31 2.34 5.10 1.14 5.24 1.90 5.08
2.74 6.24 2.51 5.84
2.46 5.89 2.58 5.65
2.53 6.04 2.50 5.74
2.60 6.11 2.50 5.78
2.57 6.03 2.56 5.73
2.61 6.05 2.58 5.74
2.98 6.26 2.73 5.84
2.71 6.12 2.60 5.77 2.03 5.86 2.18
2.46 5.93 2.55 5.68 2.09 6.00 2.09 5.75
2.58 5.95 2.64 5.68 2.61 5.93 2.67
3.58 6.85 2.75 6.40
3.38 6.66 2.74 6.29 2.97 6.55 2.42 6.45
3.56 6.86 2.71 6.41
3.44 6.80 2.66 6.38
3.60 6.84 2.78 6.39
3.98 7.03 2.96 6.47
3.32 6.53 2.80 6.22
3.29 6.47 2.83 6.19
3.21 6.47 2.75 6.19
3.66 6.66 3.01 6.27
3.74 6.78 2.97 6.34
3.36 6.60 2.78 6.26
3.57 6.80 2.79 6.36
3.45 6.72 2.75 6.33
4.27 7.42 2.87 6.92 3.72 7.20 2.52 7.08
4.32 7.43 2.91 6.92
4.20 7.39 2.83 6.91 4.55 7.30 3.24 6.91
4.25 7.41 2.85 6.92
5.46
5.35
6.38
6.11
6.24
6.29
6.22
6.23
6.34
6.27
6.15 5.37
6.14 5.42
7.15
7.01
7.16 5.51
7.13 5.48
7.13 5.54
7.21 5.64
6.90 5.54
6.85 5.55
6.87 5.51
6.93 5.65
7.03 5.63
6.95 5.53
7.09 5.54
7.05 5.52
7.88 5.52
7.88 5.54
7.87 5.50
7.88 5.51
5.08 5.17
5.12 5.09
5.37
5.39
5.36
5.36
5.38
5.39
5.48
5.41
5.52
5.51
2149
168. 1239
169. 1246
170. 1247
171. 1248
172. 1249
173. 1267
174. 1268
175. 1269
176. 1278
177. 1279
178. 1289
179. 1368
180. 1369
181. 1378
182. 1379
183. 1469
184. 1478
185. 2378
186. 12346
187. 12347
188. 12367
189. 12368
190. 12378
191. 12467 5.14 7.99 3.16 7.40 8.55
192. 12468 4.98 7.67 3.33 7.21 8.27
193. 12469 5.41 7.86 3.56 7.30 8.34
194. 12478 4.80 7.86 2.96 7.36 8.51
195. 13467 5.30 8.04 3.28 7.42 8.55
196. 13468 4.90 7.67 3.25 7.22 8.29
197. 14678 5.26 7.99 3.29 7.39 8.51
198. 23467 5.42 8.29 3.15 7.56 8.77
199. 23468 5.10 7.92 3.19 7.36 8.49
200; 123467 5.87 8.70 3.19 7.97 9.36
4.70 7.58 3.14 6.98
4.46 7.33 3.15 6.84
4.01 7: 17 2.85 6.79
4.13 7.19 2.95 6.79
4.51 7.35 3.17 6.85
4.31 7.57 2.76 7.01
4.19 7.26 2.95 6.83
4.62 7.49 3.15 6.93
4.36 7.55 2.83 6.99
4.45 7.39 3.08 6.88
4.89 7.78 3.13 7.09
3.84 6.91 2.94 6.64 4.24 7.08 3.15 7.13
4.34 7.14 3.22 6.74
4.08 7.20 2.90 6.80
4.26 7.04 3.23 6.68
4.76 7.36 3.42 6.83
4.24 7.31 2.96 6.85
4.24 7.47 2.79 6.96 3.93 7.45 2.48
5.28 8.05 3.25 7.43
4.82 7.92 2.91 7.39 5.37 7.73 3.65 7.44
4.99 8.13 2.89 7.50
4.76 7.80 2.98 7.32
4.92 8.11 2.83 7.50
7.92 5.65
7.74 5.65
7.71 5.50
7.70 5.55
7.75 5.66
8.02 5.48
7.75 5.55
7.85 5.65
7.99 5.51
7.80 5.62
8.07 5.66
7.50 5.53
7.58 5.67
7.72 5.52
7.51 5.67
7.68 5.78
7.78 5.55
7.95 5.48 7.68 5.24
8.57 5.52
8.57 5.37
8.72
8.46
8.72
5.36
5.39
5.34 5.27
5.48
5.54
5.67
5.38
5.53
5.51
5.54
5.48
5.49
5.21
2150
201. 123468
202. 123469
203. 123478
204. 123678
5.59
6.10
5.41 5.57
5.48
205. 124678 5.70
206. 124679 5.85
207. 134678 5.75
208. 134679 5.97
209. 234678 5.86
210. 1234678
211. 1234679
212. 12346789
6.23 6.22
6.47
6.87 6. 73
8.35 3.26
8.52 3.60
8.59 2.84 8.37 3.20
8.65 2.84
8.49 3.23
8.32 3.55
8.51 3.25
8.35 3.64
8.79 3.08
9.17 3.08 8.86 3.36
8.97 3.51
9.60 3.29 9.85 2.88
7.77
7.83
7.94 7. 79
7.98
7.85 9.19
7.73 8.99
7.86 9.20
7.73 8.98
8.02 9.45
8.40 10.00 8.20 10.95
8.25 9.75
8.75 10.50 8.60 10.96
9.09
9.11
9.37
9.42
5.23
5.39
5.07 5.01
5.08 4.94
5.23
5.36
5.24
5.41
5.18 4.93
4.79 4.68
4.95
4.39 4.13
PCDFiD -0.91- 3.43- 1.67- 3.68- 3.45- 3.68- All 6.87 9.64 3.64 8.75 10.50 5.78
N 23 23 23 15 12 24
<de+ 0.39 0.25 0.31 0.19 0.34 0.18
r 0.98 0.98 0.71 0.99 0.95 0.87
* Given are a serial number of each compound and the substitution pattern of the PCDF/D congener. a Experimental data from Ref. l), corrected or averaged by 10) with 11). b Experimental data from Ref. l), corrected and averaged by 12), 16) and 13). ’ Inferred from P and S by the relationship log H = log P -log S +6, the factor of 6 accounting for proper treatment of units. d Experimental data from Ref. 14). e Experimental data from Ref. 5). f Experimental data from Ref. 15).
Conclusions
A complete set of 212 values for each of the six partition constants was calculated, filling a
substantial gap in the availability of data. The inaccuracy of these values is close the inaccuracy of the
experimental data used for derivation. This meant that distinguishing between isomers is only partly possible.
Accurate theoretical (model) relationships were calculated between calculated n-octanol-water partition
coefficients, aqueous solubility, sediment-water partition constants and bioconcentration factors. Some
additional comments were given respect to the use of calculated data for specific partition constants.
2151
References
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
D. Mackay, W.Y. Shiu and K.C. Ma, Illustrated Handbook of Physical-Chemical Properties and
Environmental Fate of Organic Chemicals, Volume II. Lewis Publishers, Chelsea, U.S.A (1992).
H.A.J. Govers, Calculation of Partition Constants for a Series of Organic Compounds via a Novel
Solubility-parameter-based Method. J. Chem. Sot. Faraday Trans., 89, 3751-3759 (1993).
H.A.J. Govers and P. de Voogt, Gas Chromatographyic Derivation of the Solubility of
Polychlorinated Biphenyls with the Inclusion of Cis-Trans and Optical Isomerism and Orientational
Disorder. SAR and QSAR In Environ. Res., 3, 3 15-324 (1995).
A.G. van Haelst, Environmental Chemistry of Tetrachlorobenzyltoluenes. Ph.D. Thesis, University
of Amsterdam, Amsterdam ( 1996).
H. Loonen, Bioavailability of chlorinated dioxins and furans in the Aquatic Environment. Ph.D.
Thesis, University of Amsterdam, Amsterdam (1994).
H.A.J. Govers, F.W.M. van der Wielen and K. Olie, Derivation of solubility parameters of
chlorinated dibenzofurans and dibenzo[p]dioxins from gas chromtographic retention parameters via
SOFA. J. Chromatogr. A., 715, 267-278 (1995).
D.R. Lide (editor), Handbook of Chemistry and Physics, CRC Press, Boca Raton (1991).
Y-P. Chiou and W.J. Weber, Jr., Estimating the Effects of Dispersed Organic Polymers on the
Sorption of Contaminants by Natural Solids. 1. A Predictive Thermodynamic Humic Substance-
Organic Solute Interaction Model. Environ. Sci. Technol., 23, 978-984 (1989).
H.A.J. Govers, H. Loonen and J.R. Parsons, Nonlinear dependence of bioconcentration factors on
n-octanol-water partition coefficients of chlorinated dibenzofurans and dibenzo-p-dioxins. SAR and
QSAR in Environ. Res., 5, 63-78 (1996).
B.F. Rordorf, Prediction of vapor pressures, boiling points and enthalpies of fusion for twenty-nine
halogenated dibenzo-p-dioxins and fifty-five dibenzofurans by a vapor pressure correlation method.
Chemosphere 18, 783-788 (1989).
B.D. Eitzer and R.A. Hites, Vapor Pressure of Chlorinated Dioxins and Dibenzofurans. Environ. Sci.
Technol., 22, 1362-1364 (1988).
K.J. Friesen and G.R.B. Webster, Temperature Dependence of the Aqueous Solubilities of Highly
Chlorinated Dibenzo-p-Dioxins. Environ. Sci. Technol., 24, 97- 10 1 (1990).
K.J. Friesen, J. Vilk and D.C.G. Muir, Aqueous solubilities of selected 2,3,7,8_substituted
polychlorinated dibenzofurans (PCDFs). Chemosphere 20, 27-32 (1990).
L.P. Burkhard and D.W. Kuehl, N-octanol/water partiton coefficient by reverse phase liquid
chromatography/mass spectrometry for eight tetrachlorinated planar molecules. Chemosphere 15,163-
167 (1986).
2152
15. H. Loonen, M. Tonkes, J. Parsons and H.A.J. Govers, Bioconcentration of polychlorinated dibenzo-p-
dioxins and polychlorinated dibenzofwans in guppies after aqueous exposure to a complex
PCDDIPCDF mixture: Relationship with molecular structure. Aquat. Toxicol., 30, 153-169 (1994).
16. W.J. Doucette and A.W. A&en, Aqueous Solubility of Selected Biphenyl, Furan, and Dioxin
Congeners. Chemosphere 17, 243-252 (1988).