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Hi Jeff ~ This is a highly complex issue, with a lot of variables and uncertainties, so I hope that you will bear with me. At least four issues need to be covered: (1) gas generation and its disposition, (2) the acid phase of landfills, and (3) the impact of lignin on degradation under anaerobic conditions, (4) the value of the compost. First, the gas generation disposition. Dane County explored this issue when it did its initial study on diverting food from landfills. Our landfills recover methane gas and generate electricity, selling over $1 million in power a year and the question was about the effect of diverting food on electricity revenues. For over 10 years, we have not taken yard materials, so that was not an issue. What we found was that the situation varies considerable with the infrastructure of the gas collection system, but in our case, the environmental benefits of diversion are great. The issue hinges upon the relative time for materials to degrade, and is based on the concept of a half-life. The basic idea is -- just like radioactivity -- the decomposition of materials under either aerobic or anaerobic conditions are likely to follow a first order decay curve. The degradation under "average" conditions in a landfill according to a 1988 seminar presentation by Professor Bob Ham is that the half life of different materials are: food, garden debris 0.5 to 1.5 years paper, wood 5 to 25 years In a more recent study done for the Norwegian government, (Miljøkostnader ved avfallsbehandling [Environmental Costs from Solid Waste Management], ECON Senter for økonomisk analyse, December 2000), more detailed estimates of half lives of solid waste in landfills are provided on page 74 as: wet organics 2.8 years paper 8.4 years wood 10.5 years textiles 10.5 years For our existing landfill, we install the gas recovery system so that the openings in the pipes to recover the gas are only in the layers that are at least 5-7 years old. We do not want to draw oxygen through the surface of the landfill into the lower layers because this will change the landfill from an anaerobic to an aerobic situation and only under anaerobic conditions will methane be produced. Given the short half life of food and garden debris, much will start to degrade quickly and will do so aerobically, and then anaerobically. If the gas extraction system is only recovering gas from layers that are at least five years old, under the assumption of a half life of 1 year for food and grass clippings and other wet organics, less than 6% of the original material will typically be available, and we concluded for our system that the contribution of this gas to our recovery system was negligible. Instead, this gas would largely escape to the atmosphere and contribute to global warming. Thus, under our gas collection system configuration, diversion of food and garden debris is beneficial from a gas and environmental viewpoint. Of course, a bio-reactor may have an entirely different gas collection configuration, which would change the conclusions. Thus, the actual design must be known before a definitive conclusion can be reached. The acid phase of landfills. The degradation of solid waste in a landfill goes through a series of very distinct phases. To simplify things, one of the early stages is called the "acid phase", because at this stage (soon after aerobic decomposition has switched to anaerobic decomposition), the conditions in the landfill become very acidic, dissolving out heavy metals in a leachate flush. This is a condition that landfill operators would very much like to avoid if they can. The acids are basically caused by the decomposition of the materials in food and garden debris and grass clippings. After the acid phase, the landfill becomes basic and continues there for a long period of time. Wisconsin has a work group to look at how to achieve quicker stability of organics in landfills to reach the point where the organics would not be an environmental risk. In looking at rapid decomposition in landfills, three options are available -- (1) pump air into the landfill for the entire time, using an aerobic (i.e., composting) approach, (2) keep the air out, having the landfill operate as an anaerobic system, or (3) do a hybrid, pumping air into the site to get past the acid stage and then go anaerobic. It seems that the hybrid approach has a lot of advantages over the anaerobic approach because of the avoidance of the acid phase, but, it is more technically complex and costly, and reduces the methane generation and income from the degradable material. Thus, there are no clear winners. Viewed another way, there is no clear advantage to having the food and garden debris in the site, since it is these materials that produce the acid phase. Lignin and decomposition The third issue to highlight is the impact of lignin on anaerobic decomposition and whether a bio-reactor will work at all. There are many stories of old landfills being dug up and the waste layers dated by reading the dates from the newspapers. This is because lignin is extremely resistant to degradation in anaerobic conditions and newspapers have very high levels of lignin, on the order of 25-30%. A really good paper on the impact of lignin to inhibit degradation is found on the Internet at http://compost.css.cornell.edu/calc/lignin.html. Articles specifically on lignin and degradation in landfills by Ham, et. al., can be found in Environmental Science and Technology, 1995, pages 2305-2310 and the Journal of Environmental Engineering, December 1998, pages 1193-1202. What the research suggests is that bio-reactors -- being anaerobic systems -- are not going to achieve breakdown of the organics in newsprint and other high lignin materials, and thus are not going to achieve true organic stability. Thus, one of the major reasons for bio-reactors -- stability of the organics and less long term care -- is very questionable. Incidentally, the lignin issue also needs to be considered when calculating the potential methane generation from landfills. While the newsprint and other lignin-containing materials could theoretically produce methane, the actual methane generation is minimal from these substrates and thus the total potential generation must be correspondingly reduced. This will effect both the economics of the sites and as well as the calculations of efficiencies. The literature that I have seen on both methane potential and efficiencies, unfortunately, ignore this issue. The economics of composting In our area, we have found some interesting results vis-à-vis the economics issues. First, we have encouraged leaving grass clippings on the lawn and home composting of garden debris, food and leaves. This has saved our collection systems enormous amounts of money. On the other hand, we also operate three yard material composting sites (mainly for leaves) and find that there is extremely strong competition for our finished compost, with some landscapers wanting to buy our sites so that they can have all the compost. While in might be theoretically possible to recover compost from bio-reactors, I am not aware of any successful operations of this type. So, in closing, this is a very complex subject. And, while I know that these points do not completely answer your questions, I hope that they are of some value. Best wishes, John Reindl, Recycling Manager Dane County, WI > -----Original Message----- > From: Aluotto, Jeff [mailto:Jeff.Aluotto@no.address] > Sent: Monday, December 20, 2004 7:26 AM > To: 'greenyes@no.address' > Subject: [greenyes] Composting vs. Landfillling > > > I know this has been a frequent topic of discussion on this list, but I was > hoping someone might have some information I could use. With bioreactor > landfills (or landfills that attempt to pass for them) becoming more > commonplace, I believe that those of us putting public money into yardwaste > and organics composting programs will come under increased pressure to > justify the reasons for doing so. The argument is typically posed as "Why > spend thousands of dollars on collecting and composting yardwaste and other > organics, when the stuff is useful as a means of producing energy from > landfills and biodegrades quite easily?". > > Many organizations such as NRC have done a good job promoting > the financial > and environmental benefits of recycling. Does anyone have > any information > that does the same for composting? I know Peter has posted > some good info > on the relative inefficiency of gas collection systems - but > I was wondering > if anyone had any sort of life-cycle assessment on composting vs. > landfilling. > > Thanks! > > Jeff > > Jeffrey W. Aluotto > Manager, > Hamilton County Solid Waste District > 250 William Howard Taft > Cincinnati, OH 45219 > 513-946-7719 phone > 513-946-7779 fax > www.hcdoes.org > > > This e-mail message, including any attachments, is for the > sole use of > the intended recipient(s) and may contain private, > confidential and/or > privileged information. Any unauthorized review, use, disclosure or > distribution is prohibited. If you are not the intended recipient, > employee or agent responsible for delivering this message, please > contact the sender by reply e-mail and destroy all copies of the > original e-mail message. > > --------------------------------------------------------------------- > To unsubscribe, e-mail: greenyes-unsubscribe@no.address > For additional commands, e-mail: greenyes-help@no.address > |
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