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Model assessment of reductive dechlorination as a remediation technology for contaminant sources in fractured clay: Modeling tool
Table B.1 - Reported values of kinetics parameters for dechlorination
Kinetics coefficients |
|
Units |
Symbol |
Bagley 1998 |
Christ 2007 |
Chu 2004 |
Clapp 2004 |
Cupples 2004a |
Cupples 2004b |
Fennell 1998 |
Friis 2007 |
Garant 1998 |
Haston 1999 |
Lee 2004 |
Yu 2004 |
|
|
|
- |
Victoria, TX |
- |
- |
Bacterium VS |
VS mixed |
VS highly enriched |
KB-1/VC |
Finellas |
Mixed culture |
KB-1TM |
- |
Victoria, TX |
Victoria, TX |
PM |
EM |
µ |
d-1 |
µPCE |
0.006 |
0.316 |
0.277 |
2.395 |
- |
- |
- |
- |
- |
0.264 |
- |
0.128c |
0.016c |
3.001 |
0.08 |
0.074 |
µTCE |
0.021 |
4.29 |
0.277 |
2.506 |
- |
0.35 |
0.35 |
0.33 |
0.49 |
0.441 |
3.42 |
0.077c |
0.013c |
3.001 |
0.744 |
0.75 |
µDCE |
0.015 |
0.563 |
- |
0.766 |
0.4 |
0.46 |
- |
0.44 |
0.43 |
0.441 |
0.16 |
0.048c |
0.003c |
0.394 |
0.132 |
0.083 |
µVC |
0.013 |
0.563 |
- |
0.737 |
0.4 |
0.49 |
- |
0.42 |
0.28 |
0.441 |
0.52 |
0.055c |
0.003c |
0.394 |
0.015 |
0.048 |
K |
µmol.L-1 |
KPCE |
0.06 |
0.2 |
1 |
0.88 |
- |
- |
- |
- |
- |
0.54 |
- |
70.7 |
0.11 |
0.2 |
3.86 |
1.63 |
KTCE |
1.4 |
1.4 |
10 |
1.15 |
- |
9 |
12.4 |
10 |
10 |
0.54 |
10b |
17.4 |
1.4 |
0.05 |
2.76 |
1.8 |
KDCE |
3.4 |
3.3 |
- |
2.28 |
3.3 |
3.3 |
0.54 |
3.3b |
11.9 |
3.3 |
3.3 |
1.9 |
1.76 |
KVC |
2.7 – 400 |
2.6 |
- |
325 |
2.2 |
2.6 |
290 |
2.2b |
3.83 |
2.6 |
2.6 |
602 |
62.6 |
Y |
mgbiomass.µmol-1 |
- |
0.0027 |
0.017 |
0.0061 |
0.0058 |
0.0082a |
0.0083a |
0.0031a |
- |
- |
- |
0.0082d |
0.01e |
0.01e |
a calculated assuming 1.6*10-14g/cell [Cupples et al., 2003]
b from [Haston and McCarty, 1999]
c calculated assuming Y=8.2*10-3mgbiomass.µmol-1
d from [Cupples et al., 2003]
e calculated assuming 0.6 g protein/g biomass [Cupples et al., 2003]
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Version 1.0 July 2009, © Danish Environmental Protection Agency
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