Mass and Nutrient Losses During the Composting Of Dairy Manure Amended with Sawdust or Straw

Composting has become an increasingly popular manure management method for dairy farmers. However, the design of composting systems for farmers has been hindered by the limited amount of information on the quantities and volumes of compost produced relative to farm size and manure generated, and the impact of amendments on water, dry matter, volume and nitrogen losses during the composting process. Amendment type can affect the free air space, decomposition rate, temperature, C:N ratio and oxygen levels during composting. Amendments also initially increase the amount of material that must be handled. A better understanding of amendment effects should help farmers optimize, and potentially reduce costs associated with composting. In this study, freestall dairy manure (83% moisture) was amended with either hardwood sawdust or straw and composted for 110-155 days in turned windrows in four replicated trials that began on different dates. Initial C:N ratios of the windrows ranged from 25:1 to 50:1 due to variations in the source and N-content of the manure. Results showed that starting windrow volume for straw amended composts was 2.1 to 2.6 times greater than for sawdust amendment. Straw amended composts had low initial bulk densities with high free air space values of 75-93%. This led to lower temperatures and near ambient interstitial oxygen concentrations during composting. While all sawdust-amended composts self-heated to temperatures >55°C within 10 days, maintained these levels for more than 60 days and met EPA and USDA pathogen reduction guidelines, only two of the four straw amended windrows reached 55°C and none met the guidelines. In addition, sawdust amendment resulted in much lower windrow oxygen concentrations (< 5%) during the first 60 days. Both types of compost were stable after 100 days as indicated by CO2 evolution rates <0.5 mg CO2-C/g VS/d. Both types of amendments also led to extensive manure volume and weight reductions even after the weight of the added amendments were considered. However, moisture management proved critical in attaining reductions in manure weight during composting. Straw amendment resulted in greater volume decreases than sawdust amendment due to greater changes in bulk density and free air space. Through composting, farmers can reduce the volume and weights of material to be hauled by 50 to 80% based on equivalent nitrogen values of the stabilized compost as compared to unamended, uncomposted dairy manure. The initial total manure nitrogen lost during composting ranged from 7% to 38%. P and K losses were from 14 to 39% and from 1 to 38%, respectively. There was a significant negative correlation between C:N ratio and nitrogen loss (R2=0.78) and carbon loss (R2=0.86) during composting. An initial C:N ratio of greater than 40 is recommended to minimize nitrogen loss during dairy manure composting with sawdust or straw amendments.

[1]  Steven J. Hoff,et al.  AIR QUALITY AND EMISSIONS FROM LIVESTOCK AND POULTRY PRODUCTION/WASTE MANAGEMENT SYSTEMS , 2006 .

[2]  R. Haug The Practical Handbook of Compost Engineering , 1993 .

[3]  K. Ekinci Evaluation of decomposition rate, airflow rate and ammonia control of short paper fiber with broiler litter and additives – alum and sulfuric acid , 1997 .

[4]  H. Kirchmann,et al.  Treatment of solid animal manures: identification of low NH3 emission practices , 1998, Nutrient Cycling in Agroecosystems.

[5]  K. Ekinci,et al.  Composting Short Paper Fiber With Broiler Litter And Additives , 2002 .

[6]  Warren A. Dick,et al.  Maturity indices for composted dairy and pig manures , 2004 .

[7]  P. Wang,et al.  Assessment of the Reliability of a Commercial Maturity Test Kit for Composted Manures , 2003 .

[8]  A W Jongbloed,et al.  Environmental concerns about animal manure. , 1998, Journal of animal science.

[9]  D. Lairon,et al.  A Five Year Study on Nitrate Leaching under Crops Fertilised with Mineral and Organic Fertilisers in Lysimeters , 1995 .

[10]  M. Mizuochi,et al.  Measurements of N2O and CH4 from the aerated composting of food waste. , 2000, The Science of the total environment.

[11]  H. Hoitink,et al.  BIOCONTROL WITHIN THE CONTEXT OF SOIL MICROBIAL COMMUNITIES: A Substrate-Dependent Phenomenon. , 1999, Annual review of phytopathology.

[12]  S. Barrington,et al.  Effect of carbon source on compost nitrogen and carbon losses. , 2002, Bioresource technology.

[13]  T. Misselbrook,et al.  Environmental Impacts of Cattle Manure Composting , 2002 .

[14]  T. Dewes Ammonia emissions during the initial phase of microbial degradation of solid and liquid cattle manure , 1999 .

[15]  B. Faucette Dynamic partnership yields high quality compost , 2002 .

[16]  M. Honeyman,et al.  Effect of Windrow Turning and Seasonal Temperatures on Composting of Hog Manure from Hoop Structures , 2000 .

[17]  John E. Gilley,et al.  Nutrient, Carbon, and Mass Loss during Composting of Beef Cattle Feedlot Manure , 1997 .

[18]  J. Kim,et al.  A new method for conservation of nitrogen in aerobic composting processes. , 2001, Bioresource technology.

[19]  G. Bollen Factors involved in inactivation of plant pathogens during composting of crop residues. , 1993 .

[20]  T. L. Richard,et al.  Carbon, nutrient, and mass loss during composting , 2002, Nutrient Cycling in Agroecosystems.

[21]  D. Y. Han,et al.  Suppression of Plant Diseases by Composts , 1997 .

[22]  Robert Rynk,et al.  On-Farm Composting Handbook , 1992 .

[23]  J. Lopez-Real,et al.  A Preliminary Comparative Study of Three Manure Composting Systems and their Influence on Process Parameters and Methane Emissions , 1996 .

[24]  B. Hamelers,et al.  Passively Aerated Composting of Straw-Rich Pig Manure: Effect of Compost Bed Porosity , 2002 .

[25]  Harry A. J. Hoitink,et al.  Basis for the control of soilborne plant pathogens with composts , 1986 .

[26]  Wayne H. Thompson,et al.  Test methods for the examination of composting and compost , 1998 .

[27]  F. Michel,et al.  Effect of Oxygenation Level on Yard Trimmings Composting Rate, Odor Production, And Compost Quality In Bench-Scale Reactors , 1998 .

[28]  B. Fraser,et al.  The Effects of Process Control Strategies on Composting Rate and Odor Emission , 2000 .

[29]  M. Kenny,et al.  Practical applications of on-farm composting technology , 1995 .

[30]  S. Traina,et al.  Particulate Organic Matter Composition and Pythium Damping‐Off of Cucumber , 2001 .

[31]  H. Hoitink,et al.  Science and Engineering of Composting , 1993 .

[32]  Larry J. Forney,et al.  Effects of Turning Frequency, Leaves to Grass Mix Ratio and Windrow vs. Pile Configuration on the Composting of Yard Trimmings , 1996 .

[33]  J. Wohlt,et al.  Chemical and physical properties of processed newspaper compared to wheat straw and wood shavings as animal bedding. , 2000, Journal of dairy science.

[34]  J. Matsuda,et al.  High Rapid Composting of Dairy Cattle Manure with Crop and Forest Residues , 1983 .