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Phytoremediation
Introduction
 Remediation
 Conventional methods
 Alternative methods
 Bioremediation
 Phytoremediation
 Further classifications
 Rhizosphere
 Rhizoplane
EU: milliard
2,75-4,6 € /year
(Ernst &Young
2013)
Phytoremediation pros & cons
Pros
 Cost-efficiency
 „In situ”
 No/low amount of
secondary contaminants
 Soil structure, biological
function
 Biomass
 Metal recovery
(phytomining)
 Aesthetics (landscape)
Cons
 Timescale
 Concentration-dependency
 Restricted range of media
 Selection of species
 Continuous monitoring
 Treatment of biomass
Phytoextraction
Continuous phytoextraction I.
 Three strategies:
 Excluder
 Indicator
 Hyperaccumulator
 Mn, Zn (1%<)
 Cr, Cu, Ni, Pb (0.1%<)
 Cd (0.01%<)
Viola calaminaria (G.) Lej. Thlaspi alpestre (L.)
Silene dioica (L.) Alyssum bertolonii (Desv.)
Continuous phytoextraction II.
 Characteristics of hyperaccumulators
 Metal tolerance
 Translocation
 Detoxification with specific ligands
 Growing towards contamination (solution)
 Symbiosis (helps/hinders)
Pycnandra acuminata (Pierre ex Baill.) Swenson &
Munzinger
Induced phytoextraction
 Basics
 Mechanism
 Chelators
 EDTA (Pb, Cu, Zn)
 EGTA (Cd)
 S, NTA (Cd, Cu, Zn)
 (NH4)(NO3),
(NH4)2SO4 (137Cs)
 Citric-acid (U)
 Pros – Cons
Determination of phytoextraction
potential
 Bioaccumulation factor
BAF = Cshoot / Csoil
 Bioconcentration factor
BCF = Cplant part / Csoil
 Translocation factor
TF = Caboveground plant part / Croot
Phytofiltration
 Aquatic plants (absorption, adsorption, precipitation)
 Root + microorganisms
 Problems
 Concentration
 Size
 Development
 Water content
Lemna minor L.
Rhizofiltration
 Terrestrial plants
 Mechanism
 Root + microorganisms
 Precipitation (e.g. Pb – sunflower, Sarepta
mustard), adsorption, partitioning (Cd, U)
 Ideal species
Blastofiltration
 Seed, water, air (light)
 Primarily metals (adsorption/absorption)
 5-day-old Sarepta mustard plantlets
(Cd, Ni, Pb, Sr)
Brassica juncea L.
Phytovolatilization I.
 Plants + microorganisms
 Selenium
 Soil: Se2-, Se0, Se4+, Se6+
 Plant: SeO4
2-, SeO3
2-
 Dimethyl selenide
(e.g. cucumber)
 Dimethyl diselenide
 Forage, soil supplement
Astragalus bisulcatus (Hook.) A. Gray
Phytovolatilization II.
 Mercury (Hg)
 Mainly as Hg2+
 Hg0 (+), methylated (–)
 Members of Brassicaceae, tobacco
 Arsenic (As)
 Direct evidence (–)
 Bacteria and fungus
 Target: organic pollutants
 TCE - poplars
Phytostabilization I.
 Plants + soil amendments
 Ideally
 Sewage sludge
 Manure
 Industrial byproducts
 Phosphates
 Iron- and manganese oxides
 Organic matter
 Clay minerals
Phytostabilization II.
 Ideal species (short- and long term)
Agrostis stolonifera L. Populus alba L.
Phytodegradation I.
 Plants + microorganisms
 2 types:
 In planta
 log Kow 0,5 – 3
 + other factors
Myriophyllum spicatum L.
Phytodegradation II.
 Ex planta
 Exudates
 Enzymes
 Rhizosphere
Oryza sativa L.
Project I.
 Basket willow
 Meta-analysis
Salix viminalis L. Lovász-zug pond system
Project II.
Chenopodium album L. Tripleurospermum inodorum (L.)
Sch.Bip.
Laboratory work
 Soil
 pH
 Electrical conductivity
 Soil moisture
 Organic matter content
 CaCO3-content
 Liquid limit (soil plasticity
according to Arany)
 Elemental analyses (MP-
AES)
 Plant
 Cooling
 Drying
 Homogenizing
 Elemental analyses (MP-
AES)
Recommended literature
 Lone, ML., He, Z., Stoffella, PJ., Yang, X.
(2008): Phytoremediation of heavy metal polluted
soils and water: Progresses and perspectives.
Journal of Zheijang University Science B 9(3):
210–220.
 Pulford, ID., Watson, C. (2003):
Phytoremediation of heavy metal-contaminated
land by trees – a review. Environment
International 29(4): 529–540.

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Remediation-05.pdf

  • 2. Introduction  Remediation  Conventional methods  Alternative methods  Bioremediation  Phytoremediation  Further classifications  Rhizosphere  Rhizoplane
  • 3. EU: milliard 2,75-4,6 € /year (Ernst &Young 2013)
  • 4. Phytoremediation pros & cons Pros  Cost-efficiency  „In situ”  No/low amount of secondary contaminants  Soil structure, biological function  Biomass  Metal recovery (phytomining)  Aesthetics (landscape) Cons  Timescale  Concentration-dependency  Restricted range of media  Selection of species  Continuous monitoring  Treatment of biomass
  • 6. Continuous phytoextraction I.  Three strategies:  Excluder  Indicator  Hyperaccumulator  Mn, Zn (1%<)  Cr, Cu, Ni, Pb (0.1%<)  Cd (0.01%<)
  • 7. Viola calaminaria (G.) Lej. Thlaspi alpestre (L.) Silene dioica (L.) Alyssum bertolonii (Desv.)
  • 8. Continuous phytoextraction II.  Characteristics of hyperaccumulators  Metal tolerance  Translocation  Detoxification with specific ligands  Growing towards contamination (solution)  Symbiosis (helps/hinders)
  • 9. Pycnandra acuminata (Pierre ex Baill.) Swenson & Munzinger
  • 10. Induced phytoextraction  Basics  Mechanism  Chelators  EDTA (Pb, Cu, Zn)  EGTA (Cd)  S, NTA (Cd, Cu, Zn)  (NH4)(NO3), (NH4)2SO4 (137Cs)  Citric-acid (U)  Pros – Cons
  • 11. Determination of phytoextraction potential  Bioaccumulation factor BAF = Cshoot / Csoil  Bioconcentration factor BCF = Cplant part / Csoil  Translocation factor TF = Caboveground plant part / Croot
  • 12. Phytofiltration  Aquatic plants (absorption, adsorption, precipitation)  Root + microorganisms  Problems  Concentration  Size  Development  Water content Lemna minor L.
  • 13. Rhizofiltration  Terrestrial plants  Mechanism  Root + microorganisms  Precipitation (e.g. Pb – sunflower, Sarepta mustard), adsorption, partitioning (Cd, U)  Ideal species
  • 14.
  • 15. Blastofiltration  Seed, water, air (light)  Primarily metals (adsorption/absorption)  5-day-old Sarepta mustard plantlets (Cd, Ni, Pb, Sr) Brassica juncea L.
  • 16. Phytovolatilization I.  Plants + microorganisms  Selenium  Soil: Se2-, Se0, Se4+, Se6+  Plant: SeO4 2-, SeO3 2-  Dimethyl selenide (e.g. cucumber)  Dimethyl diselenide  Forage, soil supplement Astragalus bisulcatus (Hook.) A. Gray
  • 17. Phytovolatilization II.  Mercury (Hg)  Mainly as Hg2+  Hg0 (+), methylated (–)  Members of Brassicaceae, tobacco  Arsenic (As)  Direct evidence (–)  Bacteria and fungus  Target: organic pollutants  TCE - poplars
  • 18.
  • 19. Phytostabilization I.  Plants + soil amendments  Ideally  Sewage sludge  Manure  Industrial byproducts  Phosphates  Iron- and manganese oxides  Organic matter  Clay minerals
  • 20. Phytostabilization II.  Ideal species (short- and long term) Agrostis stolonifera L. Populus alba L.
  • 21. Phytodegradation I.  Plants + microorganisms  2 types:  In planta  log Kow 0,5 – 3  + other factors Myriophyllum spicatum L.
  • 22. Phytodegradation II.  Ex planta  Exudates  Enzymes  Rhizosphere Oryza sativa L.
  • 23. Project I.  Basket willow  Meta-analysis Salix viminalis L. Lovász-zug pond system
  • 24. Project II. Chenopodium album L. Tripleurospermum inodorum (L.) Sch.Bip.
  • 25. Laboratory work  Soil  pH  Electrical conductivity  Soil moisture  Organic matter content  CaCO3-content  Liquid limit (soil plasticity according to Arany)  Elemental analyses (MP- AES)  Plant  Cooling  Drying  Homogenizing  Elemental analyses (MP- AES)
  • 26. Recommended literature  Lone, ML., He, Z., Stoffella, PJ., Yang, X. (2008): Phytoremediation of heavy metal polluted soils and water: Progresses and perspectives. Journal of Zheijang University Science B 9(3): 210–220.  Pulford, ID., Watson, C. (2003): Phytoremediation of heavy metal-contaminated land by trees – a review. Environment International 29(4): 529–540.