Defining strategies and turning plans into practice Managing biowaste Enzo Favoino Scuola Agraria del Parco di Monza Chair, Working Group Biological Treatment ISWA Overview • • • • • The pivotal role of biowaste What’s going on in the EU A few facts & figures Sep collection, optimisation and results Tools and approaches 2 Scuola Agraria del Parco di Monza Contextual remarks: More than just waste management • Biodegradables represent the vast majority of MSW arisings (above all in S Europe) • Proper management often driven by strategies to reduce impacts of disposal – Landfill diversion targets (EU Landfill Directive) • Major contributor to GHGs from inappropriate management of MSW • Extended benefits: soils, farmlands, the environment – Climate Change (UNFCCC) – Desertification (UNCCD) – Biodiversity, fertility, resilience, prevention of floods, erosion (e.g. EU Soil Thematic Strategy) Strategic approaches to reduce impact of organics in landfills • Landfill diversion targets (Directive 99/31 EC) - Probably the most important driver for waste management in last decade in the EU (and elsewhere) • Landfill Bans (e.g. US, Brazil) - Garden waste only or organics as a whole - May be lacking some flexibility, anyway an important driver to consider for proper evolution of waste management systems ! - Requires proper definition of acceptance. Scuola Agraria del Parco di Monza MSW composition (EC, 2001) AU BE DK FIN FRA GER GRE IRL ITA YEAR (quantities) 1998 1997 1998 1997 1998 1998 1997 1998 1998 Total MSW (million tonnes) 4.85 4.69 2.93 2.51 49.1 3.9 2.06 26.9 Total (OECD) (1997 data, or latest year) 4.1 4.85 2.95 2.1 44.4 (38) 28.8 40.0 3.9 2.03 26.6 Kitchen and Yard Waste 29.2 34.9 37 40 29 29.9 47 27 33.6 24 13.4 21.6 18.9 36.8 16 32.5 5.0 28.5 22.8 1.4 2.8 1.9 I 2.6 0.8 8.2 9.4 7.2 6.8 5.1 3.7 4.5 2.3 3.2 2 2.8 5.4 9.2 3.2 4.5 4.5 4.5 11.4 4.8 2.6 1.7 0.9 17.8 26.0 12.4 31.5 15.5 19.2 Yard Waste Kitchen Waste Paper and card Paper Cardboard Timber Textiles Nappies Plastics Glass Metals Ferrous metals Non-ferrous metals Other 37.3 20 2.1 5.1 2.0 10.3 7.2 3.0 15.9 Some savings – just to give a touch • Replacement of mineral fertilisers 30-50 kg CO2eq/tonne • Biogas Production 100-150 kg CO2-eq/tonne • Peat replacement 300-400 kg CO2-eq/tonne • C sequestration 11 to 326 kg CO2-eq/tonne – EC Report “Soils and climate change” • Reduced N2O release + Improved Workability + Water retention + Replacement of pesticides….. “Climsoil” Report, EC 2009. "The report underlines the need to sequester carbon in soils. The technique is cost competitive and immediately available, requires no new or unproven technologies, and has a mitigation potential comparable to that of any other sector of the economy." http://ec.europa.eu/environment/soi l/review_en.htm Established separate collection and composting In implementation European biowaste at a glance: In beginning phase No activities 12 Mt 800 plants 3 Mt Potential organic Waste in EU15: 60 Mio. t / year 4 Mt 240 plants Sep. Collection in all municipalities . Article 22 bio-waste • Member States shall take measures, as appropriate, (…) to encourage: – (a) the separate collection of bio-waste with a view to the composting and digestion of bio-waste; – (b) the treatment of bio-waste in a way that fulfils a high level of environmental protection; – (c) the use of environmentally safe materials produced from bio-waste. • The Commission shall carry out an assessment on the management of bio-waste with a view to submitting a proposal if appropriate. The assessment shall examine the opportunity of – setting minimum requirements for bio-waste management and – quality criteria for compost and digestate (…) in order to guarantee a high level of protection for human health and the environment. Article 22 bio-waste • Member States shall take measures, as appropriate, (…) to encourage: – (a) the separate collection of bio-waste with a view to the composting and digestion of bio-waste; – (b) the treatment of bio-waste in a way that fulfils a high level of environmental protection; – (c) the use of environmentally safe materials produced from bio-waste. • The Commission shall carry out an assessment on the management of bio-waste with a view to submitting a proposal if appropriate. The assessment shall examine the opportunity of – setting minimum requirements for bio-waste management and – quality criteria for compost and digestate (…) in order to guarantee a high level of protection for human health and the environment. What does it take to get there ? “integrated” schemes, kerbside food waste + PAYT 80 % 70 % “integrated” schemes, kerbside food waste separation Road containers + kerbside (doorstep) doorstep) for a few dry recyclables (paper) paper) 50 % 40 % “added” systems, organics included trhough containers on the road 20 % “added” systems, containers on the road for dry recyclables Development of source separation of biowaste in the EU • Obligations for biowaste management – NL: compulsory schemes for separate collection – AUT: obligation upon households to either take part in separate collection or to compost in the backyard – GER: KrW-AbfG separate collection widely diffused – Catalunya (Spain): ley 6/95 compulsory for all Municipalities with a pop. > 5000 (recently extended to cover all Municipalities) – SK (Act 24/04): Garden Waste to be separately collected by 2006; biowaste by 2010 • Targets – SWE: 35% composting target – ITA, UK: recycling targets acting as drivers Separate collection of biowaste facts and findings • Kerbside (doorstep) schemes basically showing same results everywhere • Schemes may be optimised – Increased captures – Best quality – cost optimisation (no increase of costs for collection) • Best performing schemes based on labour-intensive strategies (kerbside collection, hand pick-up) – Less CAP.EX., creation of jobs • Collection at high-rise buildings also POSSIBLE and widely implemented 2n d se 98 m .' 00 00 99 99 m .' em .' se ts d 1s 2n 97 98 m .' em .' se ts d 1s 2n 96 97 m .' em .' se ts d 1s 2n em .' 95 96 m .' em .' se ts d 1s 2n 94 95 m .' em .' se ts d 1s 2n m .' 94 93 93 m .' em .' se ts d 1s 2n se 35 ts d em .' 92 40 1s 2n ts 92 m .' em .' se ts d 1s 2n 1s % recycling A remarkable, long-lasting effect 55 50 45 Kerbside biowaste collection implemented 30 25 20 15 10 5 0 Time Best Recycling Municipalities, pop < 10,000 inhabitants 9 Scuola Agraria del Parco di Monza Province capitals (larger towns, with high-rise buildings) 10 Scuola Agraria del Parco di Monza Quality of biowaste: not a matter of size of towns ! Collection at the doorstep 11127 12720 9652 34849 4713 30800 7824,192308 5971 11177 19230 16112 4332 23890 20028 92 90 88 119187 44748 50121 Containers on the road 6832 6893 9062 6152 6274 26475 150.000 Population 100.000 7161 50.000 86 84 82 80 75650 10493 0 Purity 100 98 96 94 Scuola Agraria del Parco di Monza Turin • Pop. 909,000 • Separate collection = 42% • 404,000 inhabitants with collection at the doorstep (“kerbside”) - Waste separation in neighbourhoods with kerbside, incl. food waste = 59% - Waste separation in neighbourhoods without kerbside (road containers, 3,2 m3) = 25% 11 Scuola Agraria del Parco di Monza Waste “management” in Italy ? 3 Scuola Agraria del Parco di Monza The “new” European Map – Economist 2010 * 7 Scuola Agraria del Parco di Monza Salerno • 150,000 inhabitants • Pilot project covering 30,000 inhab., July 2008 • Extension in 5 steps, completed in September 2009 • Separate collection= 75 % • Organics 50% ! Florianopolis october 28, 2010 Patrizia Lo Sciuto Slide by Enzo Favoino 14 Scuola Agraria del Parco di Monza Optimising logistics, making management sustainable (and cost-effective) Scuola Agraria del Parco di Monza “bespoke” food waste collection: Food waste in residual waste Municipality Altivole Arcade Breda di Piave Casale sul Sile Castello di Godego Cessalto Conegliano Cornuda Giavera del Montello % Food waste 7,82 8,24 7,61 9,42 8,05 6,30 9,40 7,19 6,88 Scuola Agraria del Parco di Monza Cost optimisation (Lombardy, 1500 Municipalities) Euro/person Cost of collection (green bars) and cost of treatment/disposal (blue bars) Scuola Agraria del Parco di Monza TOOLS AND STRATEGIES TO CUT COSTS Tool Details Reducing pick-up time Hand pick-up of small receptacles much faster than mechanical loading Reduced frequency for collection of “Residuals” Effective systems to collect biowaste make its percentage in Residuals less than 15 % Use of bulk lorries instead of packer trucks Bulk density of food waste is much higher (0.7kg/dm3) than garden waste Low-tech, modular approaches (particularly suited for small districts, pilot areas, small islands) Anaerobic Digestion • Turns biogenic C into a substitute fuel – wider benefits (renewable energy AND soil improvers) • Not dependent on availability of bulking materials (e.g. metropolitan areas, lack of gardens) • Unit investment and operational cost usually higher than composting (in spite of revenues from energy production, even if Renewable Energy is subsidised) • Less independent from economies of scale • Cost for the management of wastewaters – requires good integration of waste management and management of wastewater Summary remarks • Separate collection of biowaste a PROVEN strategy • Similar schemes deliver similar results everywhere – MAKE IT HAPPEN ! • intensive collection of food waste may deliver – – – High separate collection rates high diversion of BMW savings on cost of managing waste Thanks for your attention Enzo Favoino [email protected] +39 335 35.54.46 Scuola Agraria del Parco di Monza, Monza, Italy