Heavy Metals and Plants - a complicated relationship · Heavy Metals and Plants - a complicated...
Transcript of Heavy Metals and Plants - a complicated relationship · Heavy Metals and Plants - a complicated...
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Heavy Metals and Plants - a complicated relationshipHeavy metal toxicity and detoxification
Schwermetall-Hyperakkumulation im Wilden Westenmodified from:
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Dose-Response principle for heavy metals
inhi
bito
ry
Effe
ct
stim
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ory
Concentration
Exclusively toxic metal (e.g. mercury) Micronutrient (e.g. copper)
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Part I: Heavy metal toxicity
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A seemingly intact, natural creek ...However, the Elodea canadensisinside died from zinc stress that converted its chlorophyll to Zn-chlorophyll
Environmental relevance of heavy metal toxicity
Küpper H, Küpper F, Spiller M (1996) Journal of Experimental Botany 47 (295), 259-66
Zn-Fluosilicate
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1. Inhibition of root function
Why roots?
• In terrestrial plants the root is generelly the first organ that comes into contact with the heavy metals.
• In the case of heavy metals with typically low mobility, e.g. copper, also the highest metal accumulation is found in the roots
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Inhibition of root function
Mechanisms
• Competition in the uptake of less available essential micronutrients, which are sometimes transported by the same proteins
• Enhanced precipitation of essential micronutrients at the root surface
• Inhibition of transport proteins?
• Diverse relatively unspecific inhibitions of cytoplasmic enzymes
• Inhibition of cells division (relevance and mechanism unclear!)
• As a result of roots toxicity, roots tips and root hairs die off
From: Küpper H, Kochian LV, 2008,
unpublished
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2. GenotoxicityRelevance
Strongly DEPENDS on the metal applied:
• NOT relevant for copper and zinc toxicity, because other mechanisms (mainly photosynthesis inhibition) are MUCH more efficient
• VERY relavant for cadmium, because genotoxicity is very efficient, comparable e.g. to photosynthesis inhibition
• For lead, it is not very efficient, but other mechanisms are even less efficient because the metal is generally NOT very toxic for plants! Pb toxicity in general NOT environmentally relevant !
Also depends on the plant species!
From: Steinkellner H, et al., 1998, Env.Mol.Mutag. 31, 183-191
Micronucleus (MCN) formation
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Genotoxicity
Mechanisms: Point Mutations and Homologous recombinations
From: Kovalchuk O, Titov V, Hohn B, Kovalchuk I, 2001, Nature Biotechnol. 19, 568-72
Hom
olog
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reco
mbi
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ns: s
pots
per
pla
nt
Poin
t mut
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ns: s
pots
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pla
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Genotoxicity
Mechanisms: Mitotic aberrations induced by phenyl mercuric acetate (PMA)
From: Dash S, Panda KK, Panda BB, 1988, Mutation Research 203, 11-21
Micronucleus (MCN) formation
C-metaphase Tripolar anaphase
Star anaphaseAnaphase with a pair of lagging chromosomes
Micronucleus (MCN) formationAbnormal spindle
PMA concentration (ppm) PMA concentration (ppm)
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3. Oxidative Stress
Mechanisms generating reactive oxygen species during heavy metal stress
• Direct: catalysed by redox-active metal ions (Fe2+, Cu+), hydrogen peroxide is converted to reactive oxygen radicals via the Fenton-Reaction:
• Indirect: malfunktion of photosynthesis and respiration can generate reactive oxygen species. Therefore, even in vivo redox-inert metal ions like Zn2+ and Cd2+ can cause oxidative stress.
Relevance
• NOT clear: Studies with environmentally relevant realistic but still toxic heavy metal concentrations oft do NOT show oxidative stress! Almost all studies concluding that oxidative stress would be a major factor in heavy metal induced inhibition of plant metabolism were carried out using extremely high metal concentrations.
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Oxidative Stress
Mechanisms of damage caused by oxidative stress in plants
•Oxidative stress can lead to oxidation of lipids in membranes and thus make them leaky.This is a popular but debated mechanism.
• Oxidation of proteins
From: en.wikipedia.org
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0 1 2 3 4 5 6 7 8 9 10 11 12
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photosynthesis
net p
hoto
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days of heavy metal stress
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fluor
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fluorescence
Küpper H, Küpper F, Spiller M (1996) Journal of Experimental Botany 47 (295), 259-66
Environmental relevance of heavy metal induced inhibition of photosynthesis:
Elodea stressed by 0.2 µM (= 0.013 ppm) Cu2+
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2 H2O O2 + 4 H+
P700*
P700
A0 A1
4. Targets of heavy-metal induced damageto the photosynthetic apparatus
P680*
P680
PheoQA QB
WSC 4 e-
EChlChlPQ FeS/
Rieske
PC
electron transport
Antenna Chl-proteincomplexes,
main protein:LHCII4 h·ν
excitation energy transfer
ChlChl
Chl
heavy metals
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Macroscopically visible symptoms of heavy metal damageto photosynthetic systems
Sun reactionIn high irradiance, only a small fraction of the total Chl is accessible to heavy metal Chl formation, and direct damage to the PS II core occurs instead. The bulk of the pigments bleaches, in parallel to the destruction of the photosynthetic apparatus.
Shade ReactionUnder low irradiance conditions that include a dark phase, the majority of antenna (LHC II) chlorophylls is accessible to heavy metal Chlformation by substitution of the natural central ion of Chl, Mg2+. If stable heavy metal Chls (e.g. Cu-Chl) are formed, plants remain green even when they are dead.
Küpper H, Küpper F, Spiller M (1998) Photosynthesis Research 58, 125-33
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Why are heavy metal chlorophylls unsuitable for photosynthesis?
• shift of absorbance/fluorescence bands --> less energy transfer
• unstable singlet excited state --> “black holes“ for excitons
• different structure --> proteins denature
• do not readily perform charge separation when in reaction centre.
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UV/VIS absorbance spectroscopySpectra of Elodea canadensis extracts
Küpper H, Küpper F, Spiller M (1996) Journal of Experimental Botany 47 (295), 259-66
In vivo UV/VIS absorbance spectroscopy
Küpper H, Küpper F, Spiller M (1998) Photosynthesis Research 58, 125-33
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Brown algaEctocarpus siliculosus:
Chl a/c-LHC always accessible to Mg-substitution
--> always shade reaction
Red algaAntithamnion plumula:Phycobilisomes: no Chl--> always sun reaction
Küpper H, Šetlík I, Spiller M, Küpper FC, Prášil O (2002) Journal of Phycology 38(3), 429-441
UV/VIS -spectroscopy: non-Chlorophyta
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Photosynthesis activity: Sun- vs. Shade-reaction
0
20
40
60
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Mg-subst.: % of control
x10
Fv / F
m:
% of controlGPOR:
% of control
shade reaction sun reaction
Fm
: % of control
Küpper H, Šetlík I, Spiller M, Küpper FC, Prášil O (2002) Journal of Phycology 38(3), 429-441
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µ y
fluor
esce
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fluorescence
Küpper H, Küpper F, Spiller M (1996) Journal of Experimental Botany 47 (295), 259-66
Comparison of gas exchange and steady state fluorescence in Elodea stressed by 0.2 µM Cu2+ during shade reaction
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Static fluorescence microscopy of metal-stressed Elodea
red (650-700nm) chlorophyll fluorescence
transmittant light observation
1 µM Cu2+ control 100 µM Zn2+
Küpper H, Küpper F, Spiller M (1998) Photosynthesis Research 58, 125-33
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Inhibition of PSI vs. PSII
Küpper H, Küpper F, Spiller M (1998) Photosynthesis Research 58, 125-33
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In vivo thermoluminescence measurements
--> Heavy metal stress does not lead to a shift in the QA band of thermoluminescence, but only to a lowering of amplitude, i.e. a decrease of the number of active PSII--> QA site is not the primary site of
heavy metal action under physiological conditions
Küpper H, Šetlík I, Spiller M, Küpper FC, Prášil O (2002) Journal of Phycology 38(3), 429-441
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Cd-acclimation in the Zn-/Cd-hyperaccumulator T. caerulescens
Küpper H, Aravind P, Leitenmaier B, Trtilek M, Šetlík I (2007) New Phytol., 10.1111/j.1469-8137.2007.02139.x.
0.00.10.20.30.40.50.60.70.8
dark acclimated light acclimated at the end of the recovery period
control palisade mesophyll
F v/ F
m
; Φ
PSII =
(Fm'-F
t')/ F
m' spongy mesophyll
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NP
Q =
(Fm-F
m')/
Fm
Mrz Mai Jul Sep Nov0.00.10.20.30.40.50.60.70.8
Sat
urat
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= (F
p-F 0
)/(F m
-F0)
DateMrz Mai Jul Sep Nov
10 µM Cd2+
palisade mesophyll spongy mesophyll
Mrz Mai Jul Sep NovDate
Mrz Mai Jul Sep Nov
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Cd-stress in the Zn-/Cd-hyperaccumulator T. caerulescens: Spectral changes of PSII activity parameters
Küpper H, Aravind P, Leitenmaier B, Trtilek M, Šetlík I (2007) New Phytol., 10.1111/j.1469-8137.2007.02139.x.
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NIR-luminescence study of excitation energy transfer between chlorophyll derivatives and singlet oxygen
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Chl a derivatives Chl b derivativeseffi
cien
cy o
f sin
glet
oxy
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prod
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n/ %
of M
g-C
hl a
Mg2+ H+ (=pheophytin) Cu2+ Zn2+
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lifet
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of C
hl tr
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g-C
hl a
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Chl a derivatives Chl b derivatives
Mg2+ H+ (=pheophytin) Cu2+ Zn2+
lifet
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of s
ingl
et o
xyge
n/ %
of M
g-C
hl a
--> Hms-Chls have lower or equal quantum yields of singlet oxygen (1O2) production, but always lower yields of 1O2quenching compared to Mg-Chl. Phe has the most efficient 1O2 production and least efficient quenching. --> Hms-Chl formation may indirectly lead to oxidative stress.
Küpper H, Dedic R, Svoboda A, Hála J, Kroneck PMH (2002) Biochim Biophys Act 1572, 107-113
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Part II: Heavy detoxification
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1. Heavy metal detoxification with strong ligands
Phytochelatins
• Bind Cd2+ with very high affinity, but other heavy metal ions with low affinity
• Specially for Cd2+-binding synthesized by phytochelatin-synthase
• They are the main Cd-resistance mechanism in most plants (excepthyperaccumulators) and many animals
• Phytochelatin synthase becomes activated by (e.g. via Cd-binding) blocked thiols ofglutathion and similar peptides
• Phytochelatins bind Cd2+ in the cytoplasm, then the complex is sequestered in the vacuole.
• In the vacuole large phytochelatin-Cd-aggregates are formed
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Metallothionins
• MTs of type I und II bind Cu+ with high affinity andseem to be involved in its detoxification.
• BUT: Main role of MTs in plants seems to be metal-distribution during the normal (non-stressed)metabolism
Glutathion
• Also glutathione itself, the building block of phytochelatins, can bind and thus detoxify heavy metals - the in vivo relevance is questionable
1. Heavy metal detoxification with strong ligands
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Free Amino acids
• Like during metal transport under normal physiological conditions, free amino acids(mainly histidine+nicotianamine) seem to play a role in the detoxification of heavy metals.
Other Ligands
• Diverse Proteins
• Anthocyanins: seem to be involved in Brassicacae in molybdemum binding(detoxification or storage?)
• Cell wall
• Some algae release unidentified thiol-ligands during Cu-stress
1. Heavy metal detoxification with strong ligands
NicotianamineHistidine
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Speciation of cadmium and copper in the Cu-sensitive CdZn-hyperaccumulator T. caerulescens
Analysed by XAS of frozen-hydrated tissues
Cd: Küpper H, Mijovilovich A, Meyer-Klaucke W, Kroneck PMH (2003) Plant Physiology 134 (2), 748-757Cu: Mijovilovich A, Meyer-Klaucke W, Kroneck PMH, Küpper H - unpublished
Cu-K-edge EXAFS
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2. Resistance mechanisms against oxidative stress
• Enhanced expression of enzymes that detoxify reactive oxygen species (superoxide dismutase+catalase. Problem: inhibition of Zn-uptake ( SOD) during Cd-Stress.
• Synthesis of non-enzyme-antioxidants, e.g. ascorbate and glutathione
• Changes in the cell membranes to make them more resistant against the attack ofreactive oxygen species:- Lipids with less unsaturated bonds- Exchange of phosphatidyl-choline against phosphytidyl-ethanolamine as lipid-“head“- Diminished proportion of lipids and enhanced proportion of stabilising proteins in themembrane
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3. Heavy metal detoxification by compartmentation
Mechanisms
• Generelly: aktive transport processes against the concentration gradienttransport proteins involved.
• Exclusion from cells:- observed in brown algae- in roots
• Sequestration in the vacuole: - plant-specific mechanism (animals+bacteria usually don‘t have vacuoles...)- very efficient, because the vacuole does not contain sensitive enzymes- saves the investment into the synthesis of strong ligands like phytochelatins- main mechanism in hyperaccumulators
• Sequestration in least sensitive tissues, e.g. the epidermis instead of the photosynthetically active mesophyll
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Compartmentation of metals in leavesZn/Cd/Ni accumulation in epidermal vacuoles
of Thlaspi and Alyssum species
Zn Mg P S Cl K0
2
4
6
8mature leaves
mM
/ mM
Ca
Zn Mg P S Cl K0
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8 young leaves
mM
/ mM
Ca
upper epidermis upper mesophylllower mesophyll lower epidermis
Concentrations of elements in leaf tissues Thlaspi caerulescens
Zn K α line scan and dot map of a T. caerulescens leaf
Ni K α line scan and dot map of a A. bertolonii leaf
Zn: Küpper H, Zhao F, McGrath SP (1999) Plant Physiol 119, 305-11Ni: Küpper H, Lombi E, Zhao FJ, Wieshammer G, McGrath SP (2001) J Exp Bot 52 (365), 2291-2300
vacuole
epidermis
mesophyllupper lower
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From: Colangelo EP, Guerinot ML, 2006, CurrOpinPlantBiol9:322-330
Mechanisms of Metal Uptake in plantsRoot uptake
example: iron and zinc transport in Brassicaceae
root uptake
intracellular distribution
4 main familiesP-type ATPases (P1B-type = CPX ATPases)Cation Diffusion Facilitators (CDF-transporters)ZRT-/IRT-like proteins (ZIP-transporters)Natural resistance associated macrophage proteins (Nramp-transporters)
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From: Williams LE, Mills RF, 2005, TrendsPlantSci10, 491-502
Mechanisms of Metal Uptake+Compartmentation in Plants (I)CPx-type (=P1B-type) ATPases
Likely Functions (suggested by expression studies)
translocation into the root xylem, that means out of root cells ( e.g. HMA4)xylem unloading in shootsintracellular metal sequestration e.g. in
the vacuole (putative!)transport into the chloroplast, inside
the chloroplast into the thylakoidstransport into the Golgi apparatus
From: Argüello JM et al., 2007, Biometals, DOI 10.1007/s10534-006-9055-6
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From: Williams LE, Mills RF,2005,
TrendsPlantSci 10,491-502
Mechanisms of Metal Uptake+Compartmentation in Plants (I)CPx-type (=P1B-type) ATPases
Sequence characteristics predicted structure(only A, P, and N-domain crystallised from bacterial proteins)
CPx-motif in 6th predicted transmembrane helix ( Name!)Variable number of transmembrane helicesMANY histidines and cysteines in sequence ( e.g. 58 Cys in TcHMA4)Putative metal binding domain at N-terminus (in cytosol?)Histidine repeat at C-terminus (in cytosol?)
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Purification and Characterisation of a Zn/Cd transporting P1Btype ATPase from natural abundance in the Zn/Cd
hyperaccumulator Thlaspi caerulescens
From: Aravind P, Leitenmaier B, Yang M, Welte W, Kochian LV, Kroneck PMH, Küpper H (2007) BBRC 364, 51-56
Preliminary characterisation resultspost-translational modification (splitting) possibleregulation by substrate inhibitionhigher activity with Zn with Cd, but higher affinity for Cd than for Zn
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In almost all measured cells, a bright cytoplasmatic ring appeared first after start adding Cd to the medium.
A cell that was incubated with Cdover night is completely filled withCd, which means that the transportinto the vacuole took place
The transport into the vacuole is the time-limiting step in metal uptake!
Leitenmaier B, Küpper H, (2008) unpublished
Cd-transport into protoplasts isolated from the hyperaccumulator plant Thlaspi caerulescens
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From:Guerinot ML, 2000, BBA 1465, 190-8
Mechanisms of Metal Uptake+Compartmentation in Plants (II)ZIP-transporters
Structure predicted by sequence• usually 8 transmembrane helices, one long
variable region, predicted to be in the cytoplasm• 309-476 amino acids
Characteristics revelaed by yeast expression studies
• High affinity and saturable kinetics for selected metal (e.g. Zn in ZNT1)
• Lower affinity uptake for related metals (e.g. Cd in ZNT1)
From:Pence NS et al., 2000, PNAS 97, 4956-60
Likely Functions (suggested by expression studies)
• uptake of metals into cells over the cytoplasmatic membrane
• abundant in all eucaryotes, incl. humans, plants and fungi
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Fe deficiency (left) and iron replete conditions (right)
From:Connolly et al., 2002, PlantCell 14, 1347-57
Mechanisms of Metal Uptake+Compartmentation in Plants (II)Transcriptional regulation of ZIP transporters
Expression patternexpressed in most plants mainly under metal deficient conditionsin metal hyperaccumulators rather
strong expression at all metal levelsexpression mainly in metabolically
active cells, not metal storage cells
From:Küpper H, Seib LO, Sivaguru M, Hoekenga OA, Kochian LV, 2007 The Plant Journal 50(1), 159-187
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Compartmentation of elements in leaves:Correlation between metals in
the mesophyll ofArabidospis halleri
0 2 4 6 8 100
5
10
15
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25
data pointsregression line (R = 0.79; P < 0.0001) 95% confidence limits
Mg
/ mM
Cd / mM0 20 40 60
0
2
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6
8
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data points regression line (R = 0.94; P < 0.0001) 95% confidence limits
Cd
/ mM
Zn / mM
Küpper H, Lombi E, Zhao FJ, McGrath SP (2000) Planta 212, 75-84
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Cd-stress in the Zn-/Cd-hyperaccumulator T. caerulescens: distribution of photosystem II activity parameters
Cellular Fv/Fm distribution in a control plant
Distribution of Fv/Fm in a Cd-stressed plant
Küpper H, Aravind P, Leitenmaier B, Trtilek M, Šetlík I (2007) New Phytol., 10.1111/j.1469-8137.2007.02139.x.
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Proposed mechanism of emergency defenceagainst heavy metal stress
Normal: sequestration in epidermal storage cells
Acclimated: enhancedsequestration in epidermal storage cells
Stressed: additional sequestration in selected mesophyll cells
vvv
Küpper H, Aravind P, Leitenmaier B, Trtilek M, Šetlík I (2007) New Phytol., 10.1111/j.1469-8137.2007.02139.x.
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4. Root-specific resistance mechanisms
Strategies
• Reduction of the unspecific permeability of the root for unwanted heavy metals:expression of peroxidases enhances lignification
• Active (ATP-dependent) discharge by efflux-pumps ( CPx ATPases!): was shown forCu in Silene vulgaris and for diverse metals in bacteria.
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5. Further Resistance-Mechanisms
• Reduction by reductases, e.g. Hg2+ --> Hg0, Cu2+ --> Cu+
• Precipitation of insoluble sulfides outside the cell (on the cell wall)
• Methylation, e.g. of arsenic