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soil. Microflora such as algae and cyanobacteria have been reported to uptake DDT
residues from soil, with the predominant degradation product being DDE for algae
and DDD for the dinitrogen-fixating cyanobacteria (Megharaj et al. 1999, 2000).
Aquatic species not only uptake but also transform DDT, with the order of efficacy
being duckweed > elodea > parrot feather. The transformation was into DDD
(31%-48%) and some DDE (4.6%-7.9%) being formed after 6 d (Gao et al. 2000),
in contrast to upland plants, where the major metabolite is usually DDE.
Cl
Cl
Cl
Cl
Cl
DDT dehydrochlorinase
DDT 2,3-dioxygenase
1,1,1-Trichloro - 2,2 -
bis(4'-chlorophenyl) ethane
(DDT)
Cl
Cl
Cl
Cl
Cl
Cl
Cl
Cl
HO
Cl
H
H
1,1-Dichloro- 2,2 -
bis(4'-chlorophenyl) ethylene
(DDE)
OH
cis - 2,3-Dihydrodiol DDT
A
cis - 2,3-dihydrodiol
DDT dehydrogenase
DDE dehalogenase
Cl
Cl
Cl
Cl
H
Cl
Cl
Cl
HO
Cl
Cl
Cl
OH
Cl
HO
Cl
1-Chloro- 2, 2 - bis -
(4'-chlorophenyl) ethylene
(DDMU)
1,1-Dichloro- 2 - (dihydroxy- 4' -
chlorophenyl)- 2 - (4'-chlorophenyl)
ethylene
OH
2,3-Dihydroxy DDT
1,1-dichloro-2-(dihydroxy-4'-
chlorophenyl)-2-(4'-chlorophenyl)-
ethylene 1,2-dioxygenase
2,3-dihydroxy DDT
1,2 dioxygenase
6-oxo-2-hydroxy-7-
(4'-chlorophenyl)-3,8,8-
trichloroocta-2E, 4E, 7-
trienoate hydrolase
Cl
Cl
Cl
O
Cl
Cl
Cl
Cl
O
O
O
O
O
Cl
Cl
O
Cl
O
Cl
Cl
OH
OH
2-(4'-Chlorophenyl)-3,3-
dichloropropenoate
6-Oxo-2-hydroxy-7-
(4'-chlorophenyl)-3,8,8-
trichloroocta-2Z,4Z-,7-
trienoate
6-Oxo-2-hydroxy-7-
(4'-chlorophenyl)-3,8,8,8-
tetrachloroocta-2Z,4Z-
dienoate
D
B
E
O
O
O
CH 3
O
O
Cl
Cl
Cl
4-Chloroacetophenone
4-Chlorobenzoate
4-Chlorophenylacetate
C
O
4-Chlorobenzal dehyde
dehydrogenase
H
Cl
4-Chlorobenzaldehyde
Fig. 1 Proposed degradation pathways for aerobic degradation of DDT and DDE from the
UMBBD website (http://umbbd.msi.umn.edu/ddt/ddt_map.html). Reproduced from Ellis LBM,
Roe D, Wackett LP 2006, “The University of Minnesota Biocatalysis/Biodegradation Database: The
First Decade,” Nucleic Acids Research 34: D517-D521.
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