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Model assessment of reductive dechlorination as a remediation technology for contaminant sources in fractured clay: Modeling tool
Table B.2 - Reported values of inhibition coefficients
Competitive inhibition coefficient in µmol.L-1 |
|
Christ
2007 |
Chu 2004 |
Cupples
2004a |
Cupples 2004b |
Friis 2007 |
Garant
1998 |
Lee 2004 |
Yu 2004b |
Yu 2005b |
Culture |
Victoria,
TXa |
- |
Bacterium
VS |
VS mixed |
VS highly
enriched |
KB-1/VC |
Pinellas |
KB-1TM |
c |
Victoria,
TX |
PM |
EM |
PM |
EM |
K,iPCE |
0.2 |
912 |
- |
- |
- |
- |
- |
- |
70.7 |
0.2 |
3.86 |
1.63 |
3.9 |
1.6 |
K,iTCE |
no inhib |
724 |
- |
8.6 |
6.8 |
10 |
10.5 |
11 |
17.4 |
0.05 |
2.76 |
1.8 |
2.8 |
1.8 |
K,iDCE |
2.6 |
600 |
3.6 |
3.6 |
3.6 |
3.6 |
3.6 |
2.2 |
11.9 |
3.3 |
1.9 |
1.76 |
1.9 |
1.8 |
K,iVC |
250 |
- |
7.8 |
7.8 |
7.8 |
7.8 |
7.8 |
no inhib |
383 |
2.6 |
602 |
62.6 |
602 |
62.6 |
a from [Lee et al., 2004]
b inhibition constants are equal to half-velocity constants
c from [Tandoi et al., 1994]
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Version 1.0 July 2009, © Danish Environmental Protection Agency
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