Livestock and Poultry Environmental Learning Center Webcast Series October 17, 2008

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Contribution of Manure Amendments to Soil Fertility and Carbon Sequestration Animal wastes contain inorganic N (NH 4 + NO 3 -N) and organic N: Inorganic N is plant available Organic N is mineralized by microorganisms before inorganic N can be released and used by plants Animal wastes increase plant available N in the season applied and add to pools of soil N and C that turnover in years or decades The timing, availability and amount of inorganic N released from animal wastes is influenced by: Soil properties like texture, mineralogy, ph, cation exchange capacity Land Management: tillage and cropping system Long-term application of animal wastes Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 1

The type and size of microbial communities that mineralize organic N or transform inorganic N are partly determined by soil type and management Nitrification NH 4 + N0 2 - N0 3 - Factors Affecting Nitrification Initial nitrifier population size Ideal 60% water filled pore space Availability of nutrient source- NH 4+ Anaerobic conditions with avail CO 2 Soil Type Optimum ph 7 to 8 Humic materials in soil & animal waste Inhibition of nitrification due to gaseous hydrocarbons (allelopathy) Soil properties 0-15-cm depth Texture Sand Silt Clay (%) silty clay loam 11 58 32 sandy loam 73 21 6.0 silty clay 19 41 40 Soil separates measured via particle size determination (pipette methods). Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 2

Soil properties 0-15-cm depth Texture SOC (%) Total N (%) CEC (cmol c kg -1 ) silty clay loam 3.5 0.25 31 sandy loam 0.58 0.06 10 silty clay 2.3 0.21 25 SOC = soil organic carbon sample 0-15-cm depth. Total N = total soil nitrogen sample 0-15-cm depth. Cation exchange capacity is (Ca + Mg + K + Na) from the Mehlich III extract. Dairy Slurry Manure Analysis Dairy slurry applications 39 ton acre -1, <17% solids, ph 7.2 were incorporated Total Nitrogen content 268 lb N acre -1 152 lb N NH 4+ -N acre -1 + 116 lb organic N acre -1 39 lb P acre -1 Effect of Dairy Slurry on Cumulative N across (NH 4+ + NO 3- )-N soil types silty clay loam silty clay sandy loam (NH 4 + + NO3 - )-N lb acre -1 160 140 120 100 80 60 40 20 0 0 7 14 21 28 Time Interval (days) Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 3

Soil Controls without Manure Table 7.Correlation among soil properties, carbon, nitrogen, and nitrification potentials unmanured managements. Nitrification Potentials Cumulative N mineralized (mg N kg soil d -1 ) 28 d, (kg N ha -1 ) Total C Total N C:N ph CEC Sand Silt Clay Day 0-0.01 0.71** 0.72** 0.40 0.65* 0.83*** -0.53 0.18 0.68* Day 7-0.02 0.67* 0.70** 0.34 0.60 0.82*** -0.57 0.22 0.69* Day 14-0.10 0.67* 0.69* 0.35 0.68* 0.84*** -0.52 0.16 0.69* Day 21-0.02 0.63* 0.67* 0.28 0.60 0.81** -0.54 0.16 0.70** Day 28-0.04 0.66* 0.70** 0.31 0.63* 0.82*** -0.57 0.21 0.70** *** Significant at P < 0.01. ** Significant at P < 0.05. * Significant at P < 0.10. Manured Soils Table 8.Correlation among soil properties, carbon, nitrogen, and nitrification potentials with application of dairy slurry. Nitrification Potentials Cumulative N mineralized (mg N kg soil d -1 ) 28 d, (kg N ha -1 ) Total C Total N C:N ph CEC Sand Silt Clay Day 0-0.04 0.72** 0.73* 0.40 0.74** 0.86*** -0.52 0.14 0.71** Day 7-0.32 0.76** 0.69* 0.63* 0.70** 0.54-0.34 0.33 0.19 Day 14-0.39 0.01 0.07-0.21 0.60 0.04 0.22-0.20-0.16 Day 21-0.34 0.22 0.13 0.15 0.91*** 0.40 0.23-0.31-0.04 Day 28-0.34 0.70** 0.62* 0.54 0.87*** 0.64* -0.23 0.11 0.27 *** Significant at P < 0.01. ** Significant at P < 0.05. * Significant at P < 0.10. Several years of animal waste applications will increase the soil organic matter content, total C and N Greater soil N will lead to increases in potentially mineralizable N, contributing to plant available N Seasonal additions of animal wastes sequester or maintain soil carbon Amendments containing significant amounts of humic material such as compost, add to C stocks and supply a limited amount of plant available N Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 4

The Living Field Lab (LFL) located in Kalamazoo MI was designed to compare the effects of Compost, crop rotations and cover crops on: the supply of inorganic N to row crops the size and mean residence time of C and N pools Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 5

Description of Experimental Units Experiment Living Field Lab (LFL) previously in alfalfa Management Agronomic Fertilizer Nitrogen fertilizer Compost Cropping System Continuous corn Rotation (Corn-corn-soybean-wheat) Compost Material A mixture of ~ 50% leaf material mainly oak and ~ 50% dairy manure Supplementing compost applications with cover crops and legume rotations added to seasonal and long-term nitrogen fertility Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 6

Crop Above and below-ground C inputs derived from crop residues and compost Carbon content of crop biomass ton acre -1 Fertilizer Compost Continuous Corn Total C Inputs 4 y 14 17 Rotation 4 y Total C Inputs 4 y 11 14 Crop Continuous Corn April July August 1 st Corn after 4 yr Rotation April July August Field Available (NH 4 + NO 3 )-N at 25 cm ppm i Fertilizer Compost 9.5 b 21 c 12 b 3.3 a 34 d 19 c 7.6 ab 6.8 ab 5.4 a 14 b 9.0 b 10 b Yields (ton acre -1 ) Crop Fertilizer Compost Continuous Corn Clover Cover Crop No Cover 1 st Corn after 4 yr Rotation Clover Cover Crop No Cover 2.8 2.2 3.0 3.3 2.5 2.0 2.9 3.1 Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 7

Effect of N Source and Crop Diversity on: the Mean Residence Time of C and N pools Compost applications increase the N associated with humic material increasing the pool of soil organic N & the mean residence time of the pool A larger organic N pool increases the nitrogen mineralization potential (NMP) 150-d N Incubation- N Pools after 4 yr of application Fertilizer Management Initial N N Min Mean Residence (NO 3 + NH 4 )-N Potential Time (% inorganic N (lb N acre -1 ) soil N -1 ) (Days) Nitrogen Fertilizer 0.6 14 149 Compost 0.8 23 206 Shifts in Total Soil Organic Carbon with 5 yr of Nutrient and Cropping Management (% total C in soil) Baseline out of Alfalfa 0.94a Nitrogen Fertilizer 1.15b Compost 1.39c Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 8

Impact: Increased Carbon Sequestration and Fertility Growers should design systems that increase cropping intensity and include application of organic amendments Such a system could improve farmer profitability, sequester carbon and aid in the maintenance of soil fertility Archived presentation available at: http://www.extension.org/pages/manure_impacts_on_soil 9