Feasibility
Anaerobic digestion may not be suitable for all animal feeding operations. It's essential to ensure the feasibility of anaerobic digestion at your farm before committing to a system. Various technologies are available, including covered lagoons, plug flows, complete mixes, upflow sludge blankets, and fixed film reactors. Consult the selection guide for detailed information on these technologies and seek expert advice to determine the most appropriate technology for your operation. Once you establish that anaerobic digestion is technically and economically feasible, explore which types of anaerobic digester technologies best fit your site.
Biogas Handling
Methane concentrations between 6% and 15% mixed with air can be explosive. Since methane is lighter than air, it can accumulate under rooftops and in enclosed areas, making detection difficult due to its relative odorlessness. Extreme caution and special safety features are necessary when designing a digester system and storage tank, especially if the gas is compressed.
Corrosive Biogas
Biogas generated by anaerobic digesters contains highly corrosive hydrogen sulfide, which must be removed before feeding the biogas into a generator. Passing the biogas through iron particles is a simple, low-cost method for removing sulfides. The sulfides attach to the iron surfaces, removing them from the gas. The iron must be replaced every six to twelve months, depending on the size-to-gas-flow ratio.
Dry Wastes
Some collected animal wastes can have high solids content. Dairy operations are often considered suitable for anaerobic digestion technology, but waste management methods vary. Manure scraped from concrete floors or dry lots can have solids content as high as 90%. For wastes with more than 17% solids, substantial quantities of water may be required for anaerobic digestion, increasing operating costs. Clean water can absorb nutrients and pathogens, becoming a nuisance if added to an anaerobic digester. Dilution of waste with water is most practical when there is an available source of wastewater, such as from domestic or food processing uses.
High Inorganic Content
Manure collected from dry lots often contains high inorganic content, including rocks and soil particles, which cause major operational problems and must be removed before processing. This has been a prominent cause of failure in on-farm anaerobic digesters. Sand in bedding can also be problematic if it ends up in the waste supply. Removing rocks, soil, and sand typically involves adding water to the waste and allowing particles to settle, adding complexity, capital cost, and maintenance.
Co-Digestion
Combining animal feeding operation wastes with wastewater generated onsite or at nearby facilities can increase water content and methane production capacity, a process known as co-digestion. This practice is growing in popularity. However, the ability to combine manure with other wastes must be carefully evaluated before installation and operation of an anaerobic digester. Waste streams should remain consistent, as microorganisms in the digester are sensitive and can take up to three months to adjust and resume methane production when the waste source changes. Ensure that additional waste other than manure will be available daily throughout the year.
Handling End Products
Anaerobic digester effluent is a slurry containing 1% to 15% solids, depending on the waste fed into the system. This stabilized product is suitable for land application, being low in pathogens and high in nutrients. Processed material containing solids can be applied by a honey wagon, or solids can be separated for land application separate from liquids. When solids are separated, they can be composted and applied by a manure spreader. Solids separation combined with composting can result in a lower-weight product, reducing transportation costs compared to slurry for land application. The weight of processed slurry containing liquid and solids may be too expensive to transport over large distances. Using the nutrient-rich liquid component for irrigation, known as fertigation or chemigation, is regulated in most states. When fertigation systems are connected to a freshwater source, measures must be taken to avoid contamination, such as including a backflow preventer and shutoff valve. Fertigation systems must adhere to state and local regulations. If land application is not an option, find alternative methods for storage or on-site treatment.