Newsletter and Technical Publications
<Municipal Solid Waste Management>
Regional Overviews and Information Sources
Asia
2.2 Topic c: Composting
East Asia/Pacific
Backyard composting is a longstanding tradition in countries like Australia,
Japan, and New Zealand, especially in rural towns. Now it is being promoted by
local governments, with inexpensive compost bins being made available, along
with "how-to" leaflets and demonstrations. Garden and park waste are
also being composted by solid waste authorities to reduce wastes for landfilling.
A large portion of the household organic wastes in Asia is eaten by animals
or fed to pets. In cities like Hong Kong, Bangkok, Manila, Cebu, and most cities
and towns of China and Vietnam, pig and poultry farmers routinely collect food
wastes from households and restaurants for animal feed. In some small Chinese
cities, pigs are released on garbage dumps to reduce organic wastes. However,
pig keeping itself often leads to pollution of streams and rivers and has been
banned, for example, in Singapore.
Almost all the large cities of the developing countries in the region in the
past installed imported mechanical composting plants (for instance, built six).
Most are now defunct and the remaining ones are not operating at full capacity
(e.g., Bangkok, Hanoi, Shanghai, and Tokyo). The reasons why centralized
mechanical MSW composting plants are not functioning effectively, are
underutilized, or are closed down include: (a) high operating and maintenance
costs compared to open landfilling (including foreign exchange costs for
replacement parts of imported plants); (b) the cost of compost is higher than
commercial fertilizers (both cost to purchase, and labor cost to apply to the
fields); (c) incomplete separation of materials such as plastic and glass,
making the compost poor for agriculture application; and (d) poor operation and
maintenance of the facilities.
The forced-air plant in Hanoi is typical in operating at only 20% capacity.
The city has not even been able to persuade farmers to take the product free, as
it is too contaminated with plastics. Instead, it is used on city parks.
The traditional open-air windrow process is used in some countries,
especially China. In many Chinese cities and towns, there are no garbage dumps,
the wastes being delivered directly by collection vehicles to peri-urban farms.
The farmers are instructed to compost the waste in windrows or pits for a
prescribed period of time, but they often do not do this if they are in urgent
need of the organics. It is difficult for the authorities to monitor the
farmers' practices. The compost is also increasingly contaminated with plastics
and broken glass.
It is a common practice for farmers to go to garbage dumps and remove compost
in China and Myanmar. The Beijing Sanitation Department is facilitating this
practice by supplying sifting machines at the main dump site. Both Ho Chi Minh
City and Medan are allowing the mining of compost from dump sites for fees. With
recent rapid increases in industrialization, these practices will require
greater scrutiny unless there is effective control of toxic substances in the
waste stream.
Small-scale, neighborhood composting is being promoted through research and
pilot projects, especially in Java. There have been experiments for over a
decade, and now some small private enterprises have been established in Jakarta
that are supplying compost to estate gardens and golf courses. In Bandung there
is a type of box windrow composting at one garbage dump.
Co-composting with sludge from municipal sewage treatment plants is gaining
acceptance at least in cities of industrialized countries where lands are
available. High operation and maintenance and transportation costs, along with
incomplete separation of waste materials, are major constraints for the adoption
of co-composting.
There are many technical and aesthetic problems to be solved in the
composting of MSW. As one small example, an important, privately run
vermiculture experiment in Indonesia failed when toxics in the MSW killed the
earthworms.
Basic training and education of workers in technical, health, and safety
aspects is essential. With better understanding of the process, improved
processes, and public education, composting should increase at least in cities
where sites and skilled manpower are available, and markets can be developed.
The cost of compost, whether used as fertilizer or soil conditioner, is still
problematic when compared to costs of synthetic fertilizer/soil conditioner, and
this has become a major factor for decision makers.
Composting can be viable, especially for smaller cities with intensive
agricultural areas near cities. Many international agencies and environmental
consulting firms are offering Asian cities technology for composting as the
process is increasingly gaining importance in all parts of the world. An issue
here is whether the equipment offered is appropriate for the wastes of that
particular place.
Biogas technology is well known in smaller towns in rural areas in China
through government policies of comprehensive utilization of wastes. However,
these biogas digesters use human and animal feces as the main feedstock. Some
agricultural wastes may be added. The number of biogas digesters in rural towns
is declining with the breakup of communes. Household-level digesters have not
proved practical. The potential remains for anaerobic digestion of wastes, but
organizational problems need to be overcome.
South and West Asia
Since the organic fraction of the waste stream is high in most places, there
is considerable interest in composting of MSW in the region, and a long history
of experiments with composting. Large-scale centralized composting (as distinct
from neighborhood composting) has had little success; pure anaerobic digestion
has been tried rarely and only in pilot projects in the region.
In the 1960s many mechanical compost plants were constructed, often promoted
by foreign firms. In India, the central government gave grants to eight cities
to install plants (of foreign design, with imported parts) and the principal
cities in the northern and central countries of the region built similar plants.
Almost all of these are now not operating or are producing at a fraction of
capacity, because they were unsuitable for the local wastes, parts and skilled
operators were not available, and/or the product was too expensive or not good
enough to secure markets.
Although one of New Delhi's plants has been closed, another is still
operating. The compost is absorbed by the city's parks department, an example of
how city procurement policies can help the marketing problem. In Kathmandu, the
compost from a municipal plant was in high demand by local farmers in the late
1980s and early 1990s, and the plant continued with a simple windrow system
after the machinery broke down. It was forced to close recently when residents
of new housing estates protested.
Recently, however, private firms, alone or in public-private partnership,
have revived centralized composting in a few places. Bangalore's windrow compost
plant is reported to be cost-effective since privatization, although there are
now NIMBY ("Not In My Back Yard") pressures at the site. There are
experiments with new techniques for producing compost by processing partly
decomposed wastes at dump sites (being done by a private company subsidized by
the Bombay and Ahmedabad municipal corporations).
In some middle- and high-income economies, private firms are also reported to
be operating effectively and are and able to market the compost locally or to
other countries. In Sharjah, UAE, a compost plant is run by the municipality;
there are, however, marketing constraints. In Israel, the Ministry of
Environment reports that 20,000 metric tons of organics are converted into
compost annually. Analysis of the compost from some plants in these areas,
however, has shown high levels of contaminants, especially from nickel-cadmium
batteries.
Backyard composting is casually practiced in areas where there are home
gardens, the bulk of the input material being yard waste. This practice has been
strongly discouraged by city health officers (for instance in Bangalore) after
complaints about rodents. Consequently, backyard composting has declined in the
past twenty years.
In the past decade, several projects have been initiated for small-scale,
neighborhood-level composting. In Bangalore, the Waste Wise Project of the
Mythri Foundation and the Centre for Environmental Education are both combining
worm culture with composting on a small scale on land provided in local parks by
the City. Bangalore University is giving advice on worm culture. Pilot research
and development projects for the region are included in the current UNCHS
project on small-scale digestion and composting of MSW.
The natural process of decomposition at waste disposal sites is commonly
exploited by farmers and sometimes by the municipal corporations in cities and
towns of the Indian subcontinent. Farmers go to dumps to remove compost, thus
extending the life of the dumps. The Corporation of Calcutta leases out dump
land at the city's main dump for vegetable farms. Small dumps near squatter
settlements are regularly farmed. There are no studies of possible health risks
from these practices.
The subcontinent has wide experience with anaerobic digestion of cattle dung,
and it was assumed that similar digesters could be adapted to ferment MSW, but
producing animal-dung-like slurries from urban organic waste proved
energy-intensive and the product was poor. A major problem with anaerobic
digestion is that MSW used as feedstock tends to float. A number of design
changes have to be achieved to produce small-scale digesters. Research is being
done in Bangalore at the Indian Institute of Science, but there are no reports
of successful large-scale anaerobic digestion.
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