Gaseous emissions and modification of slurry composition during storage and after field application: Effect of slurry additives and mechanical separation.

The aim of the study was to evaluate the impact of slurry treatment by additives (EU200® (EU200), Bio-buster® (BB), JASS® and sulphuric acid (H2SO4)) and mechanical separation on the physical-chemical characteristics, gaseous emissions (NH3, CH4, CO2 and N2O) during anaerobic storage at ∼20 °C (experiment 1) and NH3 losses after field application (experiment 2). The treatments studied in experiment 1 were: whole slurry (WS), WS+H2SO4 to a pH of 6.0, WS+EU200 and WS+BB. Treatments for experiment 2 were: WS, slurry liquid fraction (LF), composted solid fraction (CSF), LFs treated with BB (LFB), JASS® (LFJ), H2SO4 to a pH of 5.5 (LFA) and soil only (control). The results showed an inhibition of the degradation of organic materials (cellulose, hemicellulose, dry matter organic matter and total carbon) in the WS+H2SO4 relative to the WS. When compared to the WS, the WS+H2SO4 increased electrical conductivity, ammonium (NH4+) and sulphur (S) concentrations whilst reducing slurry pH after storage. The WS+H2SO4 reduced NH3 volatilization by 69% relative to the WS but had no effect on emissions of CH4, CO2 and N2O during storage. Biological additive treatments (WS+EU200 and WS+BB) had no impact on slurry characteristics and gaseous emissions relative to the WS during storage. After field application, the cumulative NH3 lost in the LF was almost 50% lower than the WS. The losses in the LFA were reduced by 92% relative to the LF. The LFB and LFJ had no impact on NH3 losses relative to the LF. A significant effect of treatment on NH4+ concentration was found at the top soil layer (0-5 cm) after NH3 measurements with higher concentrations in the LF treatments relative to the WS. Overall, the use of the above biological additives to decrease pollutant gases and to modify slurry characteristics are questionable. Reducing slurry dry matter through mechanical separation can mitigate NH3 losses after field application. Slurry acidification can increase the fertilizer value (NH4+ and S) of slurry whilst mitigating the environmental impacts through a decrease in NH3 losses during storage and after application.

Greenhouse gas emissions and soil properties following amendment with manure-derived biochars: Influence of pyrolysis temperature and feedstock type.

Manure-derived biochars can offer a potential option for the stabilization of manure, while mitigating climate change through carbon sequestration and the attenuation of nitrous oxide emission. A laboratory incubation study was conducted to assess the effects of four different manure-derived biochars produced from different feedstocks (poultry litter and swine manure) at different temperatures (400 or 600 °C). A commonly available standard wood chip biochar, produced at a greater temperature (1000 °C), and non-amended treatments were used as references. Two different soils (sandy and silt-loam) were amended with 2% (w/w) biochar on a dry soil weight basis (corresponding to 20 Mg ha(-1)), with the soil moisture being adjusted to 75% saturation level. After a pre-incubation period (21 days), 170 kg N ha(-1) of NH4NO3 fertilizer was added. Measurements of CO2, N2O, CH4 emissions and soil N mineralisation were carried out on different days during the 85 days of incubation. The net C mineralization and N2O emissions from both soils amended with poultry litter biochar at 400 °C were significantly greater than the other biochar treatments. Nitrate availability was greater in both soils in which the manure-derived biochar was used instead of the standard biochar. All of the biochars increased the pH of the silt-loam, sub-acid soil, but failed to improve the cation exchange capacities (CEC) in either soil. Total C and N, P, K and Mg (except Ca) were significantly increased in the manure-derived biochar amended soils, compared to the Control, and were positively correlated to the biochar nutrient contents. This study indicates that the soil application of biochar engenders effects that can vary considerably according to the biochar properties, as determined on the basis of the feedstock types and process conditions. Low-temperature biochar production from manure represents a possible way of producing a soil amendment that can stabilize C while supplying a significant quantity of nutrients.