Lecture Notes - University of Bristol
Transcription
Lecture Notes - University of Bristol
Environmental Geochemistry DM Sherman, University of Bristol Organic Geochemistry DM Sherman, Environmental Geochemistry University of Bristol Composition of Living Matter Proteins Carbohydrates Lipids Lignin Vascular plants 7 50 10 33 Phytoplankton 23 66 11 0 Diatoms 29 63 8 0 Zooplankton 60 22 18 0 Page 1 Environmental Geochemistry DM Sherman, University of Bristol Molecular Components of Biomass Lipids Carbohydrates and Polysaccharides Molecular Components of Biomass Lignin Page 2 Environmental Geochemistry DM Sherman, University of Bristol Hydrolysis Products of Biomass Fatty Acids (Hydrophyllic Acids) Sugars Amino Acids Biological Breakdown of Biomolecules Amino Acids Hydrolysis Fatty Acids Sugars Respiration CO2 Humic/Fulvic Acids Proteins Lipids Fermentation Carbohydrates Extremely anaerobic conditions Lignin Acetate Alcohols Methanogenesis CH4 Page 3 Environmental Geochemistry DM Sherman, University of Bristol Abiotic Breakdown Products of Biomass Fulvic Acids Abiotic Breakdown Products of Biomass Humic Acid Page 4 Environmental Geochemistry DM Sherman, University of Bristol Complexation of Metals by Humic/Fulvic Acids Some metals (Cu, Hg) are complexed by HA and FA. This may play a role in oreforming processes. Organic Carbon in Terrestrial Aquatic systems Page 5 Environmental Geochemistry DM Sherman, University of Bristol Nature of Humic/Fulvic Acids and Humin • Major form of organic matter in soils and freshwater. • Origins are still not fully understood but main hypothesis is that humic/fulvic acids are derived from the breakdown of lignin. • Humic Acid = soluble at high pH only • Fulvic Acid = soluble over all pH values • Humin = not soluble at any pH Organic Carbon in Aquatic systems Page 6 Environmental Geochemistry DM Sherman, University of Bristol Organic Carbon in Sediments • Sediments contain < 1% organic C. • Nearly all DOC and POC in the water column is oxidized by respiration. • For organic C to accumulate in sediments, the flux of POC must be high and the redox conditions must be anaerobic. Diagenesis and Kerogen Formation • Hydrolysis of complex organics • Functional groups are removed. • Double bonds are hydrogenated to give saturated hydrocarbons • Aromatic compounds increase relative to aliphatic • Condensation of molecular fragments to complex macromolecules • End product is kerogen a mixture of complex organic compounds that dominate organic matter in sediments. Page 7 Environmental Geochemistry DM Sherman, University of Bristol Catagenesis of Kerogen to Oil and Gas Diagenesis: methanogens produce methane. Organic matter converted to kerogen. Catagenesis: breakdown of kerogen Metagenesis: breakdown of oil into gas + graphite Methane Hydrates At the pressures and temperatures of the ocean bottom, biogenic methane is trapped as clathrates. Page 8 Environmental Geochemistry DM Sherman, University of Bristol Methane Hydrates The stability field of methane hydrates is limited to shallow sediment depths. Methane is an extremely potent greenhouse gas and release from sediments could greatly accelerate global warming. Carbon Isotopic Fractionation Page 9 Environmental Geochemistry DM Sherman, University of Bristol Carbon Isotopic Fractionation Pollution by Organic Compounds Page 10 Environmental Geochemistry DM Sherman, University of Bristol Organic Pollutants: BTEX Compounds Biodegradation of Organics (Cont.)" C6H6 + 7.5 O2 ! 6CO2 + 3H2O + ! 6CO2 + 18H2O + 15Mn2+ C6H6 + 6NO3- + H+ ! 6CO2 + 3N2 +6H2O C6H6 + 30 FeOOH + 60 H + ! 6CO2 + 48 H2O + 30Fe2+ Decreasing Eh C6H6 + 15MnO2 + 30H C6H6 + 3.75SO42- + 7.5H+ ! 6CO2 + 3.75H2S + 3H2O C6H6 + 4.5H2O ! 2.25CO2 + 3.75CH4 Page 11 Environmental Geochemistry DM Sherman, University of Bristol Spatial Distribution of electron acceptors after biodegradation progresses in soil PAH (Polycyclic Aromatic Hydrocarbons) in Creosote" OH phenol OH CH3 napthalene Benzo-[a]-pyrene cresol anthracene Creosote is a common wood preservative but is now banned because it contains PAHs (carcinogenic). These are slow to degrade in soil. Page 12 Environmental Geochemistry DM Sherman, University of Bristol Synthetic Chlorohydrocarbons" Organohalide Breakdown by Methanogens" (1) CCl2=CCl2 (PCE) + H2 ! CCl2=CClH (TCE)+ HCl (2) CCl2=CClH (TCE) + H2 ! CCl2=CH2 (DCE) + HCl (3) CCl2=CH2 (DCE) + H2 ! CH2=CHCl (VC) + HCl Breakdown of vinyl chloride (CH2=CHCl) requires aerobic conditions: CH2=CHCl (VC) + 5/2O2 ! 2CO2 + H2O + HCl Page 13 Environmental Geochemistry DM Sherman, University of Bristol Summary: Abiotic Breakdown of Biomolecules Lignin, Carbohydrates, Proteins, Lipids Fulvic, Humic acids, Humin Kerogen Hydrocarbons Methane Graphite Page 14