Abstract

Capturing ammonia from anaerobically digested manure could simultaneously decrease the adverse effects of ammonia inhibition on biogas production, reduce reactive nitrogen (N) loss to the environment, and produce mineral N fertilizer as a by-product. In this study, gas permeable membranes (GPM) were used to capture ammonia from dairy manure and digestate by the diffusion of gaseous ammonia across the membrane where ammonia is captured by diluted acid, forming an aqueous ammonium salt. A lab-scale prototype using tubular expanded polytetrafluoroethylene (ePTFE) GPM was used to (1) characterize the effect of total ammonium nitrogen (TAN) concentration, temperature, and pH on the ammonia capture rate using GPM, and (2) to evaluate the performance of a GPM system in conditions similar to a mesophilic anaerobic digester. The GPM captured ammonia at a rate between 2.2 and 6.3% of gaseous ammonia in the donor solution per day. Capture rate was faster in anaerobic digestate than raw manure. The ammonia capture rate could be predicted using non-linear regression based on the factors of total ammonium nitrogen concentration, temperature, and pH. This use of membranes shows promise in reducing the deleterious impacts of ammonia on both the efficiency of biogas production and the release of reactive N to the environment.

Highlights

  • Ammonia (NH3 ) emissions from livestock manure are an important source of reactive nitrogen (N)release to the environment, impacting the health of humans and livestock, and resulting in N loss from the farm production cycle negatively affecting profitability

  • The objectives of this research were to test expanded polytetrafluoroethylene (ePTFE) gas permeable membranes (GPM) to (1) determine the optimal capture rate conditions considering total ammonium nitrogen (TAN) concentration, temperature, and pH, and (2) to mimic the conditions within a dairy manure anaerobic digester and in so doing, to evaluate whether it could be feasible to adopt within the anaerobic digestion (AD) reactor

  • Mass Reduction (MR)% is not equal to Mass Capture (MC)% because of production of TAN occurring in the donor solution from mineralized organic N concurrent with TAN removal

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Summary

Introduction

Ammonia (NH3 ) emissions from livestock manure are an important source of reactive nitrogen (N). Release to the environment, impacting the health of humans and livestock, and resulting in N loss from the farm production cycle negatively affecting profitability. Loss of ammonia decreases the fertilizer value of digestate. Nitrogen fertilizers are required for crop production, contributing to additional ammonia emissions and adding an economic burden to farmers. Ammonia emissions contribute to eutrophication of surface water bodies, soil acidification, and particulate matter formation [1]. Ammonia is a precursor to PM2.5 (particulate matter with an aerodynamic diameter of 2.5 μm or less), which has negative human health impacts [2]. Ammonia has a harmful impact on manure treatment processes, such as anaerobic digestion (AD). At high concentrations ammonia can inhibit the methane formation process

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