Alleviating Soil Acidity through Organic Matter Management. Malcolm E. Sumner, University of Georgia Marcos A Pavan IAPAR

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Transcription:

Alleviating Soil Acidity through Organic Matter Management Malcolm E. Sumner, University of Georgia Marcos A Pavan IAPAR

Introduction Most work on topsoil acidity amelioration Mechanical lime incorporation Little work on subsoil acidity amelioration Impractical to incorporate lime (cost) No-till systems present a challenge Little opportunity for mechanical mixing of lime

Introduction Top- and subsoil acidity Excess Al and Mn Deficient Ca Root extension and proliferation Require adequate Ca Limited by toxic levels of Al Poor root system Limited water and nutrient uptake Low yields

Approach Theoretical analysis of problem Experimental verification

Acidity in Conservation Tillage Systems Inability to mix amendments with soil Subsoils often already acid Ammoniacal fertilizers create acidity Can move down into subsoil Acidity problem essential same in top- and subsoil Cannot place lime at site of acidity Alternative strategies to move alkalinity into soil without disturbance

Brazilian Situation Most conservation tillage on Oxisols and Ultisols Variable charge soils Charge depends on ph and salt content Acidification causes Reduction in CEC and increase in AEC Lower ph, toxic Al & Mn, deficient Ca

CEC & AEC of Variable Charge Soils

Problem Requiring Solution Without disturbance To neutralize soluble Al To increase soluble Ca Throughout the profile

Brazilian Situation As ph decreases CEC decreases and AEC increases Al saturation increases and base saturation decreases Many Cerrado soils near ZPC Limited capacity to hold essential cations Mainly Al and H

Brazilian Situation Amelioration to depth involves Neutralization of Al and Mn Restoration of basic cations Organic matter builds up under no-till Decreases ZPC Increases CEC and reduces AEC Soil should be more resilient Can maintain ph at lower value?

Variable Charge Soils Acidity literature shows Lime does not move down profile Acidity chemistry well known Allows formulation of rules to predict lime behavior in profile

Rules for Lime Movement For surface applied lime to move Alkalinity (HCO 3-, OH - ) must move downward Mass flow If topsoil is sufficiently acid Al 3+, Mn 2+, H + can also move downward At ph 5.2-5.4, mass flow of alkalinity and acidity roughly balance

Rules for Lime Movement For alkalinity to move downward Topsoil ph must be > 5.4 Above ph 5.4 HCO 3-, OH - and CO 3 2- increase exponentially In variable charge soils Alkaline front retarded Alkalinity used up to increase CEC

Processes Involved Precipitation of Al 3+ and Mn 2+ 2Exch-Al 3+ + 3Ca(HCO 3 ) 2 3Exch-Ca 2+ + 2Al(OH) 3 + 6CO 2 Exch-Mn 2+ + Ca(HCO 3 ) 2 Exch-Ca 2+ + MnCO 3 + H 2 O + CO 2 Decrease in AEC Solid-OHH + Cl - + ½Ca(HCO 3 ) 2 Solid-OH + H 2 O + CO 2 + ½CaCl 2 Increase in CEC Solid-OH + ½Ca(HCO 3 ) 2 Solid-O - ½Ca 2+ + H 2 O + CO 2

Consequently Lime movement slower in variable than permanent charge soils Positively charge sites result in salt (CaCl 2 ) formation CaCl 2 moves down freely Reason for often observed rapid downward movement of Ca 2+ with no change in ph No lime movement without other factors

Factors Promoting Lime Movement Soil Fauna Acid Inputs Gypsum Organic Compounds

Soil Fauna Burrowing animals mix lime with soil Earthworms mix laterally and vertically Ants and termites mix mainly vertically Lime better distributed if mix with topsoil More soil fauna under conservation than conventional tillage Should be encouraged Avoid pesticides that impact fauna

Effect of Earthworms on Soil ph

Acid Inputs Ammoniacal fertilizers and legumes Appear to be deleterious Benefits under appropriate management Sufficient lime must be present in topsoil Crop must be actively growing Alkalinity transferred down Nitrification, lime dissolution, differential uptake of Ca 2+ and NO 3 -

Processes Involved Nitrification NH 4 X + 2O 2 HNO 3 + HX + H 2 O where X can be NO 3-, ½SO 4 2-, H 2 PO 4 - or HPO 4 2- Lime Dissolution CaCO 3 + 2HNO 3 Ca(NO 3 ) 2 + H 2 O + CO 2 Ca(NO 3 ) 2 free to move down

Processes Involved Differential Uptake of Ca 2+ and NO 3 - Roots excrete H + to take up Ca 2+ Roots excrete OH - to take up NO - 3 Roots take up more NO - 3 than Ca 2+ Root 4OH - Root 4NO - 3 + 2Ca(NO 3 ) 2 + Ca(OH) 2 + 2H 2 O Root 2H + Root Ca 2+ Lime [Ca(OH) 2 ] produced at point of uptake

Effect of N and Lime on Subsoil ph

Gypsum Surface applied gypsum ameliorates subsoil acidity Enhances soluble Ca 2+ and reduces toxic Al 3+ Allows better root profileration Allows better exploitation of subsoil water Translates into increased yields

Processes Involved Ion Pairing Al 3+ + CaSO 4 AlSO 4 + + Ca 2+ Self-liming Effect 2OH-[Fe,Al]-OH + CaSO 4 (HO-[Fe,Al]-SO 4- )2Ca 2 + Al 3+ + Ca(OH) 2 Al(OH) 3 + Ca 2+ Formation of Basic Aluminum Sulfates 3Al 3+ + K + + CaSO 4 + 3H 2 O KAl 3 (OH) 6 (SO 4 ) 2 + 3H + + Ca 2+ KAl 3 (OH) 6 (SO 4 ) 2 in soluble in ph range 4-5

Organic Compounds Literature shows that Short chain carboxylic acids detoxify Al 3+ Depends on relative positions of OH/COOH groups Root growth related to monomeric Al and not total Al in solution Lime + EDTA neutralized subsoil Al but lime alone does not Manure + lime neutralize subsoil Al Organic compounds transfer alkalinity

Movement of Organic Compounds Al complexation OM complexes and detoxifies Al Al-OM complexes can move downward Organic matter as lime Neutralizing value basic cation & N content ph and basic cation content is linear N content generates acidity Quality of OM is important Ligand exchange

Processes Involved Al Complexation Al 3+ + 3KOOC-R Al(OOC-R) 3 + 3K + Organic matter as lime Ca(OOC) 2 + ½O 2 CaCO 3 + CO 2 Ca(OOC) 2 + heat CaO + CO 2 CaO + CO 2 CaCO 3 Ca(C 6 H 11 O 7 ) 2.H 2 O + 11O 2 CaCO 3 + 11CO 2 +12H 2 O Ligand exchange 2[Fe,Al]-OH + Ca(OOC) 2 C 2 H 4 Ca(OH) 2 + [Fe,Al] 2 (OOC) 2 C 2 H 4

Leaves (200 t/ha) and ph of Cecil Soil (ph 4.0) Material N content Ca+Mg+K Final ph Cotton 26.9 2944 7.60 Peach 19.7 1859 7.12 Alfalfa 32.4 1653 6.84 Maize 10.0 958 5.44 Wheat 4.6 344 4.85

Effect of Basic Cation Content on Soil ph

Leaves and ph of Brazilian Soils (ph 4.0, 4.6, 4.4) Material Ca+Mg+K Average ph LV soil LR soil LE soil Radish 84.7 6.5 6.7 5.7 Soya 40.8 6.0 5.8 4.9 Wheat 5.4 4.3 5.2 4.3

Soluble cations and carbon Treat Total C Tot Cat. Sol. C Sol Cat. mmol c /kg mmol c /L 4% Radish 18.0 84.7 2.97 58.8 4% Soy 20.1 40.8 1.11 23.6 4% Wheat 22.5 5.4 0.29 3.0

Brazilian Results Ca ex + Mg ex (cmol kg -1 )

Brazilian Results

Brazilian Results W: wheat; S: soybean; L: blue lupin; O: black oat; M: maize

Brazilian Results

Conclusions Profile acidity can be reduced by Soil fauna incorporating lime and OM Differential uptake of Ca and NO 3 by roots Leaching of gypsum Leaching of bases with OM Brazilian results confirm last three mechanisms

Conclusions Reduced tillage systems Promote accumulation of OM Protect soil surface Provide soluble OM to carry bases into subsoil Quality of residue is of prime importance Cotton, tobacco, radish, lupin, soybean> wheat, millet, oats, rice, maize