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PROBLEM Reduced tillage on biosolids-amended land decreases runoff and erosion and increases infiltration and soil moisture. Little research has been conducted, however, on the effects of no-tillage on crop response nitrogen availability where biosolids were applied. INTRODUCTION Biosolids plant-available nitrogen (PAN) is composed of ammonium N and organic N. Insufficient PAN supply can reduce crop yield, while surplus PAN can lead to soil nitrate N leaching issues. Biosolids are traditionally incorporated into soil to prevent odors. Tillage increases organic N mineralization; no-tillage increases ammonia volatilization and also reduces risk of erosion and runoff. OBJECTIVE To compare the interactive effects of land-applied biosolids types and tillage practices on corn nitrogen availability in Coastal Plain agricultural soils. METHODS In 2009 and 2010, two study sites planted with corn (Zea mays L.) were laid out separately on an Orangeburg loamy sand (Fine-loamy, kaolinitic, thermic Typic Kandiudults), in Sussex County, VA. Experimental design: Split-Plot Design Main plot treatments: conventional tillage (CT) and no-tillage (NT). Sub-plot treatments: commercial fertilizers(0x, 0.5x, 1x, 1.5x agronomic N rate*), anaerobically digested biosolids (AD) and lime stabilized biosolids(LS) (1x N rate). Each treatment was replicated 4 times. *1x agronomic N rate= 120 kg ha -1 (2009) & 157 kg ha -1 (2010) Sampling and analysis: Pre-Sidedress Nitrate Test (PSNT) Biosolids Biosolids Year Year pH pH Organic C, g Organic C, g kg kg -1 -1 Organic N, Organic N, g kg g kg -1 -1 NH NH 4 -N, g kg -N, g kg - 1 LS 2009 12.4 546 29.3 1.1 2010 12.2 629 39.6 2.6 AD 2009 8.2 627 42.8 17.2 2010 8.3 635 55.1 21.4 In 2009, NO 3 level was higher in CT than in NT. All treatments in no-till had values below 450 ppm. Both biosolids maintained low levels of NO 3 , indicating that biosolids N availability was not excessive and was under control. Effects of Biosolids Types on Nitrogen Availability under Varying Tillage Practices Jinling Li ([email protected]), Gregory K. Evanylo and Xunzhong Zhang, Department of Crop and Soil Environmental Sciences, Virginia Tech Properties of land-applied biosolids in 2009 and 2010. Tillag Tillag e e Soil Soil C, C, g kg g kg -1 -1 Soil Soil N, N, g kg g kg -1 -1 CT 3.92 0.36 NT 4.38 0.39 In 2009, both tillage and fertility treatment significantly influenced end-of- season soil C and N. Soil organic C and total N were higher in NT than in CT, and AD was higher than LS. Biosolids could Tillage effects on soil C and N Fertility effects on soil C and N In 2010, all treatments had values above 450 ppm; LS had value over 2000 ppm. In this situation, much nitrate-N accumulated at the bottom of stalks and could not be utilized by plants. AD was lower than CONCLUSION AND PERSPECTIVE Both biosolids types maintained higher N availability than commercial fertilizers at 1x N rate. The differences between LS and AD biosolids were possibly due to the varying proportions of inorganic N and organic N. Biosolids N availability could be influenced by tillage practices, as no-till apparently slowed down the mineralization of biosolids organic N, and incorporation of biosolids into soil could reduce ammonia volatilization. Biosolids types did not show much organic C sequestration over the first growing season. The evident increasing of biosolids C sequestration would possibly be indicated by the future three-year studies. Fertilit Fertilit y y Soil Soil C, C, g kg g kg -1 -1 Soil Soil N, N, g kg g kg -1 -1 0xN 3.90 a 0.34a 0.5xN 3.79 a 0.34a 1xN 3.88 a 0.35a 1.5xN 4.14 ab 0.37a b LS (1xN) 4.40 bc 0.40b c AD (1xN) 4.81 c 0.43c RESULTS AND DISCUSSION In 2009, due to frequent and sufficient rainfall events, moisture was not a limiting factor. Plants could take up enough N for growth and biosolids maintained higher N levels than fertilizers. In 2010, hot and dry weather reduced organic N mineralization and increased ammonia volatilization rates. Plant uptake N decreased relatively and biosolids showed lower N levels than commercial fertilizer treatments. Grain Yield In 2009, both biosolids maintained higher level of NO 3 than fertilizers. AD was higher than LS. In 2009, both biosolids maintained higher ear leaf N than fertilizers. LS was higher than AD. In 2009, both biosolids maintained higher grain yields than fertilizers. LS was higher than AD. In 2010, both biosolids maintained lower level of NO 3 than fertilizers. AD was lower than LS. In 2010, both biosolids maintained lower ear leaf N than fertilizers. LS was higher than AD. Grain yield in 2010 was lower than in 2009. Both biosolids maintained higher yields than fertilizers. Ear Leaf TKN Biosolids Application PSN T CSNT Lime Stabilized Biosolids Grain Yield Soil C & N Analysis Anaerobically Digested Biosolids
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PROBLEM

Mar 18, 2016

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Effects of Biosolids Types on Nitrogen Availability under Varying Tillage Practices. Jinling Li ( [email protected] ), Gregory K. Evanylo and Xunzhong Zhang, Department of Crop and Soil Environmental Sciences, Virginia Tech. PROBLEM - PowerPoint PPT Presentation
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Page 1: PROBLEM

PROBLEMReduced tillage on biosolids-amended land decreases runoff and erosion and increases infiltration and soil moisture. Little research has been conducted, however, on the effects of no-tillage on crop response nitrogen availability where biosolids were applied.

INTRODUCTION Biosolids plant-available nitrogen (PAN) is composed of ammonium N and organic N. Insufficient PAN supply can reduce crop yield, while surplus PAN can lead to soil nitrate N leaching issues. Biosolids are traditionally incorporated into soil to prevent odors. Tillage increases organic N mineralization; no-tillage increases ammonia volatilization and also reduces risk of erosion and runoff.

OBJECTIVETo compare the interactive effects of land-applied biosolids types and tillage practices on corn nitrogen availability in Coastal Plain agricultural soils.

METHODSIn 2009 and 2010, two study sites planted with corn (Zea mays L.) were laid out separately on an Orangeburg loamy sand (Fine-loamy, kaolinitic, thermic Typic Kandiudults), in Sussex County, VA.

• Experimental design: Split-Plot Design Main plot treatments: conventional tillage (CT) and no-tillage (NT). Sub-plot treatments: commercial fertilizers(0x, 0.5x, 1x, 1.5x agronomic N rate*),

anaerobically digested biosolids (AD) and lime stabilized biosolids(LS) (1x N

rate). Each treatment was replicated 4 times.

*1x agronomic N rate= 120 kg ha-1 (2009) & 157 kg ha-1 (2010)

• Sampling and analysis: Pre-Sidedress Nitrate Test (PSNT) Corn Ear Leaf total Kjeldahl Nitrogen (ELN) Corn grain yield End-of-season Corn Nitrate Test (CSNT) End-of-season soil organic C and total N

BiosolidsBiosolids YearYear pHpH Organic C, g kgOrganic C, g kg-1-1 Organic N, g kgOrganic N, g kg-1-1 NHNH44-N, g kg-N, g kg-1-1

LS 2009 12.4 546 29.3 1.1

2010 12.2 629 39.6 2.6

AD 2009 8.2 627 42.8 17.2

2010 8.3 635 55.1 21.4

In 2009, NO3 level was higher in CT than in NT. All treatments in no-till had values below 450 ppm. Both biosolids maintained low levels of NO3, indicating that biosolids N availability was not excessive and was under control.

Effects of Biosolids Types on Nitrogen Availability under Varying Tillage PracticesJinling Li ([email protected]), Gregory K. Evanylo and Xunzhong Zhang, Department of Crop and Soil Environmental Sciences, Virginia Tech

Properties of land-applied biosolids in 2009 and 2010.

TillageTillage Soil C,Soil C, g kgg kg-1-1

Soil N,Soil N, g kgg kg-1-1

CT 3.92 0.36

NT 4.38 0.39

In 2009, both tillage and fertility treatment significantly influenced end-of-season soil C and N. Soil organic C and total N were higher in NT than in CT, and AD was higher than LS. Biosolids could sequester more organic C and N.

Tillage effects on soil C and N Fertility effects on soil C and N

In 2010, all treatments had values above 450 ppm; LS had value over 2000 ppm. In this situation, much nitrate-N accumulated at the bottom of stalks and could not be utilized by plants. AD was lower than LS.

CONCLUSION AND PERSPECTIVE Both biosolids types maintained higher N availability than commercial fertilizers at 1x N rate. The differences between LS and AD biosolids were possibly due to the varying proportions of inorganic N and organic N. Biosolids N availability could be influenced by tillage practices, as no-till apparently slowed down the mineralization of biosolids organic N, and incorporation of biosolids into soil could reduce ammonia volatilization. Biosolids types did not show much organic C sequestration over the first growing season. The evident increasing of biosolids C sequestration would possibly be indicated by the future three-year studies.

FertilityFertility Soil C, Soil C, g kgg kg-1-1

Soil N, Soil N, g kgg kg-1-1

0xN 3.90a 0.34a

0.5xN 3.79a 0.34a

1xN 3.88a 0.35a

1.5xN 4.14ab 0.37ab

LS (1xN) 4.40bc 0.40bc

AD (1xN) 4.81c 0.43c

RESULTS AND DISCUSSION In 2009, due to frequent and sufficient rainfall events, moisture was not a limiting factor. Plants could take up enough N for growth and biosolids maintained higher N levels than fertilizers. In 2010, hot and dry weather reduced organic N mineralization and increased ammonia volatilization rates. Plant uptake N decreased relatively and biosolids showed lower N levels than commercial fertilizer treatments.

Grain Yield

In 2009, both biosolids maintained higher level of NO3 than fertilizers. AD was higher than LS.

In 2009, both biosolids maintained higher ear leaf N than fertilizers. LS was higher than AD.

In 2009, both biosolids maintained higher grain yields than fertilizers. LS was higher than AD.

In 2010, both biosolids maintained lower level of NO3 than fertilizers. AD was lower than LS.

In 2010, both biosolids maintained lower ear leaf N than fertilizers. LS was higher than AD.

Grain yield in 2010 was lower than in 2009. Both biosolids maintained higher yields than fertilizers.

Ear Leaf TKN

Biosolids Application

PSNT

CSNT

Lime Stabilized Biosolids

Grain Yield

Soil C & N Analysis

Anaerobically Digested Biosolids