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Accelerated biodegradation of 2,4-D in legume rhizospheres: elucidation of the
mechanisms responsible
Liz Shaw
The rhizosphere
Distinctive soil-plant root environmentEnriched in organic carbon due to rhizodepositionAs much as 40% of carbon that is photosynthetically fixed is translocatedbelow ground
endo
rhiz
osph
ere
ecto
rhiz
osph
ere
rhiz
opla
ne
2
Rhizodeposit composition
O
CH2OH
H
HO
H
OH
H OH
HO
O
OH
O
NH2 C
CH3
H
COOH
OH
OH
N N OH O
HO
O
NH
OHO
OCH2OH
H
HO
O
OH
H OH
OCH2OH
H O
OH
H OH
OCH2OH
H H
OH
H OH
mucilage
sloughed border cells
‘Rhizosphere effect’
Time (d)0 10 20 30
Min
eral
isat
ion
(% in
itia
l)
0
20
40
60
80
non-plantedLoliumTrifolium
Enhanced biodegradation of 2,4-dichloro-phenoxyacetic acid in rhizosphere soil of red clover
Shaw & Burns (2005) Soil Biol. Biochem. 37, 995
O
ClCl
2,4-D
COOH
3
Summary of research reporting a ‘rhizosphereeffect’ on the biodegradation of pesticides
SoybeanDiphenolic ether: Acifluorfen
Zablotowicz et al., 1997
MaizeChloroacetanilide:Metolachlor and alachlor
Hoagland et al. 1997
Summer cypress, maize, pennisetum
Triazine:Atrazine and simazine
Kruger et al., 1997Marchand et al., 2002Pervovitch et al., 1996Piutti et al., 2002Singh et al., 2004
Red clover, daisy fleabane, barnyard grass, fall panicum, early goldenrod, chicory, timothy grass, green foxtail, sunflower
Phenoxyacetic acid:2,4-D and 2,4,5-T
Boyle and Shann, 1995Boyle and Shann, 1998
Plant speciesPesticideReference
research is descriptive, not mechanistic
Overall aim: to investigate mechanisms of Trifolium rhizosphere enhanced 2,4-D biodegradation
Time (d)0 10 20 30
Min
eral
isat
ion
(% in
itia
l)
0
20
40
60
80
non-plantedLoliumTrifolium
?
4
Overall aim: to investigate mechanisms of Trifolium rhizosphere enhanced 2,4-D biodegradation
Specific objectives:1. To investigate the impact of plant and soil properties on the
enhanced biodegradation2. To compare the number and diversity of 2,4-D degradative
microorganisms in Trifolium, Lolium and non-planted systems
Time (d)0 10 20 30
Min
eral
isat
ion
(% in
itia
l)
0
20
40
60
80
non-plantedLoliumTrifolium
Functional engineering of rhizosphere for benefit (i.e. rhizoremediation)
Time (d)0 10 20 30
Min
eral
isat
ion
(% in
itial
)
0
20
40
60
80
non-plantedLoliumTrifolium
Treatment of mineralization data
t1 = t0[(b-1)/(b+1)]1/b = time at maximum rateMaximum rate = (-a.b)/(4t1)
a = asymptote
Y = a[1+(t/t0)b]-1
time
at m
axim
um ra
te, t
1 (d
)
0
15
20
25
30
non-p
lanted
Loliu
m
Trifoliu
m
max
imum
rate
(d-1
)
0
2
4
6
8
10
a a
a a
b
b
5
The rhizosphere effect has legume specificity
non-p
lanted
Loliu
mHolc
us
Festuc
a
Helian
thus
Stellar
ia
Mysoti
s
Trifoliu
m
Medica
goLo
tus
Max
imum
rate
(d-1
)
0
5
10
15
20
25
non-p
lanted
Loliu
mHolc
us
Festuc
a
Helian
thus
Stellar
ia
Mysoti
s
Trifoliu
m
Medica
goLo
tus
Tim
e at
max
imum
rate
t 1 (d
)
0
5
10
15
20
25
30
non-planted controlLegumesDicotsMonocots
* * * * ** * * * *
Shaw and Burns (2005) Environ. Microbiol. 7, 191
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
Production of the active component is dependent on the presence of microorganisms
Shaw and Burns (2005) Environ. Microbiol. 7, 191.
t 1 (d
)
020
30
40
50a
b
max
imum
rate
(d-1
)
0
2
4
6
a
b
non-
amen
ded
a
a
gnot
obio
tic-
grow
n ro
ots
non-
ster
ile-
grow
n ro
ots
non-
amen
ded
gnot
obio
tic-
grow
n ro
ots
non-
ster
ile-
grow
n ro
ots
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
6
The production of the rhizodeposit component that stimulates 2,4-D mineralization:
Has specificity to legumesIs dependent on presence of microorganismsIs dependent on plant age
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
The production of the rhizodeposit component that stimulates 2,4-D mineralization:
Has specificity to legumesIs dependent on presence of microorganisms
Implies plant-microbe signallingIs dependent on plant age
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
7
Rhizodeposit composition
O
CH2OH
H
HO
H
OH
H OH
HO
O
OH
O
NH2 C
CH3
H
COOH
OH
OH
N N OH O
HO
O
NH
OHO
OCH2OH
H
HO
O
OH
H OH
OCH2OH
H O
OH
H OH
OCH2OH
H H
OH
H OH
mucilage
sloughed border cells
flavonoids
MODULES – REMEDIATION and SOIL MICROBIOLOGY & BIOTECHNOLOGY
Role of flavonoids: nod factor inducers
E.g. 7,4’-dihydroxyflavone
from Broughton et al. (2003) Plant and Soil 252, 129
OHO
OH
O
8
The mechanism?The stimulatory rhizodeposit (isoflavonoid?) component is acting as:
A significant additional growth substrate for 2,4-D degradersAn inducer of 2,4-D catabolism
Is the stimulatory rhizodeposit enhancing 2,4-D mineralization by acting as a growth substrate?
If this was the case, would expect:Increased numbers of 2,4-D degraders in the rhizosphere of Trifolium compared to Lolium or non-planted pristine soilRhizosphere-dependent shift in diversity of 2,4-D degrading microorganisms
9
104
105
106
107
Plant age (d)0 25 60 116
Log
(Med
ian
MP
N g
-1)
1
10
100Non-plantedLoliumTrifolium
1.7 LoD
After 2,4-D(+ve control)
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
No effect of plant species or plant age on numbers of 2,4-D degraders
Shaw and Burns (2004) Appl. Env. Microbiol. 70, 4766
3 6 8 2 5 9 4 7 1 10 15 20 18 14 19 21 11 13 12 16 17 22
0.67
1
Mat
chin
g si
mila
rity
mea
sure
nn n ll lt tt t NN NN LLL LT TTT
N,n = non-plantedL,l = LoliumT,t = Trifoliumn,l,t = before 2,4-DN,L,T = after 2,4-D
No effect of plant species on 2,4-D degrader diversity: Hierarchical cluster analysis of SSCP profiles: tfdAα from soil
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
Shaw and Burns (2004) Appl. Env. Microbiol. 70, 4766
10
The mechanism?The stimulatory rhizodeposit component is acting as:
A significant additional growth substrate for 2,4-D degradersAn inducer of 2,4-D catabolism ?
Suggested mechanism for the role of flavonoids as inducers in enhanced 2,4-D mineralization (1)
O
O
HO
OH
OH
OH
O
O
HO
OH
OH
O
A C
B
HO
OH
OH
OH
A C
OHHO
OH
B
OH
A
A
OH
C
OH
B
O
O
B
OH
Quercetin
Naringenin
Phloroglucinol 3,4-Dihydroxy cinnamic acid
11
OH
OH
O
O
OH
OH
OH
OH
CHO
OH
OH
COOH
Cl
Cl OH
Cl
COO-COO-
COO-
3,4-dihydoxycinnamic acid
3,4-dihydoxystyrene
Cl Cl
O
O
O
B-carboxymucanate
2,4-dichloromuconate
Cl
HO
OH
protocatechuicaldehyde
COO-COO-Cl
Cl
2,4-dichlorophenol
2,4-D
protocatechuicacid
3,5-dichlorocatechol
TCA cycle TCA cycle
Suggested mechanism for the role of flavonoids as inducers in enhanced 2,4-D mineralization (2)
TfdA can accept hydroxy cinnamicacids as substrates1
1 Dunning Hotopp and Hausinger, 2001 J. Mol. Catal. B 15: 155
2,4-D pathway in W. eutropha JMP134 pJP41 kb
A S R DII CII EII FII BII K T C D E F B
OH COOHCOOH
OH
Cl
Cl Cl
ClOCH2COOH
Cl
Cl
OH
Cl
Cl
tfdA tfdC(II)tfdB(II)
tfdR gene product activates expression and the effectormolecule for TfdR is 2,4-dichloro-cis,cis-muconate.
12
OH
OH
O
O
OH
OH
OH
OH
CHO
OH
OH
COOH
Cl
Cl OH
Cl
COO-COO-
COO-
3,4-dihydoxycinnamic acid
3,4-dihydoxystyrene
Cl Cl
O
O
O
B-carboxymucanate
2,4-dichloromuconate
Cl
HO
OH
protocatechuicaldehyde
COO-COO-Cl
Cl
2,4-dichlorophenol
2,4-D
protocatechuicacid
3,5-dichlorocatechol
TCA cycle TCA cycle
Suggested mechanism for the role of flavonoids in enhanced 2,4-D mineralization (2)
Involvement of flavonoids as inducers requires further testing ?
Further research to investigate the role of isoflavonoids and inducers
Establish the role of isoflavonoidsSpiking experiments with commercially available isoflavonoidsUse of legume mutants (e.g. Medicago truncatula) deficient in isoflavonoid biosynthesis
Establish whether rhizodeposits (isoflavonoids) act as inducers of the 2,4-D pathway
Use of transcriptional fusions to quantify gene expression in model bacterial strains
13
Arrangement of tfd genes in plasmid pEST4011 of Achromobacter xylosoxidans subsp. dentrificansEST4002
From Vedler et al. (2004) J. Bacteriol. 186, 7161.
tfdA tfdK tfdB tfdE tfdC tfdR iaaH tfdD
Role of plant-microbe interactions in the evolution of xenobiotic catabolic pathways
Arrangement of tfd genes in plasmid pEST4011 of Achromobacter xylosoxidans subsp. dentrificansEST4002
From Vedler et al. (2004) J. Bacteriol. 186, 7161.
tfdA tfdK tfdB tfdE tfdC tfdR iaaH tfdD
Indole acetamide hydrolase(Bradyrhizobium japonicum USDA110)
Role of plant-microbe interactions in the evolution of xenobiotic catabolic pathways
14
Thank you
HERBICBIOREM
15
tfd A, B, and C primer sets
tfdC(Calvaca et al. (1999) FEMS Micro. Ecol. 29, 45. )
Bacillus B11JMP 228 (pEMT8)RASCJMP134-ve
OH COOHCOOH
OH
Cl
Cl Cl
Cl
tfdB(This study)
OH
Cl
Cl Cl
Cl
OH
OHJMP228 (pEMT8)Bacillus B11RASCJMP134-ve
tfdA(Vallaeys et al. (1998) FEMsMicrob. Ecol. 20, 163.)
OCH2COOH
Cl
Cl
OH
Cl
Cl
RASCJMP134-ve
1000 bp 100 bp
Used these primer sets to PCR amplify from DNA extracted directly from soil or from 2,4-D degrading enrichment cultures
NO PRODUCTS
tfdA-like genes in 2,4-D-degrading bacteria belonging to the BANA cluster in α-ProteobacteriaItoh et al. (2002) AEM 68, 3449.
Bacillus B11
RASC
RD5-C2
HW13
-ve
100 bp ladder
Japanese upland soil α-Proteobacterial isolate RD5-C2 tfdAα gene 56-60% homologous to canonical tfdA genesDesigned primers from alignments of tfdAα genes in RD5-C2, HW13, BTH and HWK12
16
N L T N L T N L T N L T N L T N L T N L T N L T
A
B
Before 2,4-D After 2,4-D
PCR amplification (A) and subsequent SSCP analysis (B) of tfdAα genes in Sourhope soil before and after 2,4-D application
2,4-dichlorophenoxyacetic acid canonical pathway in β-Proteobacteria Wautersia eutropha JMP134 pJP4
tfdA encodes 2,4-D/α-ketoglutarate dioxygenase
tfdA
O
ClCl
2,4-D
OH
ClCl
2,4-dichlorophenol
OH
ClCl
3,5-dichlorocatechol
OH
COOHCOOH
ClCl
2,4-dichloromuconate
COOH
TCA cycle
17
The mycorrhizosphererh
izos
pher
e
Hypho-sphere
dead/dyinghyphae
root
hyphosphere
Addition of chopped Trifolium roots enhances 2,4-D mineralization
non-a
mende
d
roots
100 m
g
autoc
laved
roots
100 m
g
roots
200 m
g
max
imum
rate
(d-1
)
0123456
non-a
mende
d
roots
100 m
g
autoc
laved
roots
100 m
g
roots
200 m
g
t 1 (d
)
02025303540 a
b bb
b
a
bb
18
Specific objectives:1. To investigate the impact of plant and soil properties on the enhanced biodegradation2. To compare the number and diversity of 2,4-D degradativemicroorganisms in Trifolium, Lolium and non-planted systems
0 12 25 60 116
Max
imum
rate
(d-1
)
4
5
6
7
8
9
10
11
12
Plant age at rhizosphere harvest (d)
0 12 25 60 116
Tim
e at
max
imum
rate
(t1)
12
14
16
18
20
22
24
non-plantedLoliumTrifolium
Shaw and Burns (2004) Appl. Env. Microbiol. 70, 4766
The rhizosphere effect depends on plant species and plant age
Flavonoids of leguminous plants: a tentative identity for the stimulatory rhizodeposit?
From: Aoki et al. (2000) J. Plant Res. 113, 475
19
Role of flavonoids (2): phytoalexinsE.g. medicarpin produced by Medicago spp.
Data from Blount et al. (1992) Plant Pathol. 41, 333.
OHO
O
H
H
OCH3
Medicarpin (mM)
0.10 0.25 0.50
% d
iffe
renc
e in
rad
ial g
rowt
h-100
-80
-60
-40
-20
0
Antifungal activity of medicarpin on Nectria haematococca
Initial mineralisation kinetics are linear
Time (days)
0 2 4 6 8 10 12 14 16
% m
iner
alis
atio
n
0.0
0.5
1.0
1.5
2.0
2.5
3.0
Non-plantedLinear regression