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Observations of Biogas Generation and Use in Ireland and Germany John Crawford Agenda Practice Introduction Engineering Drivers Conclusions Energy Context Introduction Increasing Interest for Dairy AD in NZ


  1. Observations of Biogas Generation and Use in Ireland and Germany John Crawford

  2. Agenda • Practice • Introduction • Engineering • Drivers • Conclusions • Energy Context

  3. Introduction • Increasing Interest for Dairy AD in NZ • Increasing herd size • Increasing interest in housing • Increasing problems with effluent disposal • Appears to be popular and successful in Europe – • Why? • Can we emulate that? • What drivers? • Scale – Also an interest for NZ municipals

  4. Drivers • Farm Waste Stream Management • EU Directive • Profit

  5. Drivers: Farm Waste Management • This is almost certainly the starting point for most of the farm based AD systems: • Desire for improved sustainability of the farming operation • Availability of nutrients • Transportability of nutrients • Odour management • Quantity of slurry

  6. Drivers: EU Directive & Profit • EU Directive 2009/23/EC • Requires member states to achieve 20% renewable electricity generation by year 2020 • Incentives introduced to actively encourage investment • Each State has its Own Incentives (or not) • Profit • Replacement of Retail energy. • Sale of energy. • Provision of heat energy to additional farm revenue enterprises. Gate fees • Fertilizer savings

  7. Energy Context • Historically low levels of electricity generation by renewable energy sources. • Approach to incentives varies • FIT and ROC or FIT • Seem to be available till 20% target is reached. Then made difficult or cut altogether. • Typically assured payments for 20 years • Grid operator must accept the energy – legislated – but doesn’t have to make it easy.

  8. Energy Context • Northern Ireland (UK 184 units, increasing) • ROC = £43.30 • 4 ROCs per MW.hr = £0.1732 / kW.hr, plus • Feed in Tariff = £0.05 / kW.hr, plus heat use incentive • Germany (8,000 units, static) • Sliding scale of € ct6 to € ct14 / kW.hr, plus • Various premium payments (size, feedstock, flexibility • Maximum € ct25 / kW.hr • Householder pays € ct20 + € ct6.5 /kW.hr as ‘Green energy support.

  9. Energy Context - Example • Northern Ireland • CAPEX £1.8M • 500 kWel, 91% overall availability • 400 cow herd, 6,500t @ 6%DS cattle slurry Annual Cost Annual Revenue Feedstock, 12,000t @ £50 £600k 500x91%x24x365x£(0.173+0.05) £889k Maintenance £60k Digestate Savings on Fertilizer £20k Labour & Admin £40k Gate Fees for waste acceptance £0 Depreciation or CR @5% £90k Dried Wood Chip Revenue £ ?? Interest @4% £72k Total Annual Cost £862k Total Annual Revenue £909k ++

  10. Practice • Robust, well engineered systems. • Trend is 250kW.el minimum economic and increments of 250kW.el. Some go lower, BUT … . • Cattle / Pig slurry used as the biological inoculum and a low grade energy source. • Alternative feedstocks (On & Off farm) provide the bulk of the energy yield: • Grass & Maize silage • Winter wheat • Beets • Chicken litter • Food & meat wastes (must be pasteurized)

  11. Engineering • Concrete or SS reactors • Three styles of Gas storage: • Double skin, pressurized bladder over headspace • Double skin, pressurized external balloon • Pressurized headspace under concrete roof • Common engines: • MVM Gas – Owned by Caterpillar • Jenbacher • Deutz • Scania • Leihberr

  12. Engineering • Mixing styles the key difference: • Submersible WW mixers (Williams) • External Recirculation & jets • Gas Mixing (Greenfinch) • Inclined shaft / Big blade (Weltec) • Mississippi Paddle Wheel (Hochreiter) • Common themes: • CHP • Stainless steel pipework • Centralised pumping and maceration • Instruments: Temp, Pressure, Gas analysis, Titration analyser. (Adequate, not excessive) • Digester treated like another herd of cows

  13. On the Farm • An extra FTE staff member to manage the digester: • Loading the feeder • Monitoring operation • Managing digestate • Legislative and Revenue administration, • Depending on feedstock, AD process measured as increasing N bioavailability by 18 – 24% over that of the feedstock. • Odour level from digestate is about 1/10 th that of raw animal slurry. • AD reduces the mass for disposal ~21%

  14. Conclusions • Digester treated like another herd of cows. • Economics of an electricity only enterprise questionable without the incentives. • Economics of a slurry only enterprise questionable. • Multiple Feedstock – Multiple Product – Better Outcome • Other revenue streams and farm operational drivers are the key to financial viability. • Small scale systems displacing retail energy purchase, using the heat and improving the feedstock fertilizer value may be feasible. Assessment each on its own merits. • In Feasibility study – look for a ‘Sweet Spot’ where the drivers overlap.

  15. Conclusions • For current New Zealand context: • We don’t yet have year round housing of cows (pigs yes). • Collect approx. 10% of slurry. • No incentives and low wholesale feed in tariffs. • Is wholesale electricity more valuable than milk produced from silage? • The digestate would be valuable. • Parallel, heat using enterprise may be the key as may upgrading biogas to methane and use as a biofuel. • Recommended Reading: • A Review of Anaerobic Digestion Plants on UK Farms, by Angela Bywater, for Royal Agricultural Society of England.

  16. Acknowledgements • Noel Gavigan, Bioenergy Association of Ireland (RoI) • Dr Peter Frost, Agri-Food and Biosciences Institute, Hillsborough Research Farm (NI) • Nigel Moore, CAFRE, Greenmount Agricultural College • Williams Industrial Services (NI) • Edina (RoI) • Weltec Biopower (Germany) • Blackiston-Houston Estates (NI) • Progressive Energy (NI) • McDonnell Farms / GreenGas (RoI) • Weichering Sudmann (Germany) • Suren Meyer (Germany) • Naturstrom Buschheide (Germany)

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