The purpose of this memo is to look at the issues of planning, sitting,
designing and operating composting facilities. It will be useful to the
decision-makers, managers and potential operators of the facility, as well as
to citizens who are interested in the composting process. The memo discusses
several approaches to composting and outlines the circumstances in which each
method should be considered.
The memo will discuss whether a composting operation should be designed
according to the need and resources of the community. For example, a municipal
composting effort can entail simply collecting yard trimmings on a seasonal basis
and using a simple “windrow and turn” technology to produce the compost, or it
can mean siting and designing a large facility that is capable of handling
several tons of mixed municipal solid waste.
BACKGROUND
Composting is considered to be a form of recycling. Like other
recycling efforts, the composting of yard trimming and solid waste can help the
municipality dispose of solid waste that can’t be sent to a landfill or incinerator.
Composting also yields a valuable product that can be used by farmers,
landscapers, horticulturists, government agencies, and property owners as a
soil amendment or mulch.
Composting is the
manipulation of the natural aerobic process of biological decomposition of
organic materials to increase the decomposition rate. This process is carried
out by successive microbial populations that function under increasing
temperatures to break down organic materials into carbon dioxide, water,
minerals, and stabilized organic matter. The
compost product improves the condition of soil reduces erosion, and help
suppress plant diseases. Simply piling up leaves and allowing them to
slowly decompose is not composting.
Since January 1993,
state law bans yard waste—leaves, grass clippings, garden debris, and twigs,
brush, and branches smaller than six inches in diameter—from landfills and most
incinerators. This law does not apply to stumps, roots or shrubs with intact
root balls, or incinerators which burn waste to recover energy.
The primary
motivation for composting wastes is the law that prevents landfilling in the
typical landfill. There are privately permitted landfills that may accept yard
waste, but require dumping fees. The City is currently landfilling at the old
Conservation Club, which is now the County Sheriff’s shooting range on CTH “V”
near E. Mills Drive. The site was permitted for landfilling in 2004 and the
city has used the site since then. The city previously hauled to a facility in
Waterloo and paid a dumping fee. The cost in labor, equipment, gas and fees was
substantial and hauling to the local site saved thousands of dollars. The
County site will fill up in a couple of years and the Council needs to consider
what options will be the best alternative for disposing of the yard waste
materials.
Neighborhood
composting facilities for grass, leaves, yard waste and food scraps which do
not exceed a volume of 50 cubic yards of compost at one time need no DNR license
or approval, provided the operation is nuisance free and certain performance standards
are met.
Community yard waste
compost facilities that handle between 50 and 20,000 cubic yards of material on
the site at one time are licensed by the Regional DNR office for that area.
These facilities must meet location, performance and reporting requirements set
by DNR administrative code. All yard waste compost facilities that exceed 50
cubic yards at one time must be licensed by the department, regardless of when
they opened for operation.
Yard waste compost
facilities that handle more than 20,000 cubic yards of waste at one time are
approved and licensed through the DNR central office and must meet the requirements
for such facilities set by DNR administrative code.
When considering any type of composting effort, councilmembers must
plan ahead to avoid potential obstacles that could hinder the operation. The
most common challenges are siting the facility, ensuring that the facility is
properly designed, mitigating and managing odor, controlling bioaerosols and
investing adequate capital to cover unforeseen costs. Councilmembers should
seek to understand and prepare for the challenges of potentially developing a
composting program.
Yard waste (i.e.,
leaves, grass clippings, and shrubbery and tree prunings) at one time comprised
an estimated 12 percent of the municipal solid waste (MSW) that was being
buried in America’s landfills. During the peak grass clipping and leaf
collection months of the spring and fall, that represented more than 50 percent
of the MSW stream in some locales. Local governments in Wisconsin are required to
enacted yard-waste disposal bans to increase the lifespan of landfills. Yard
wastes should not be landfilled because they are relatively clean,
biodegradable materials that can be recycled for soil improvement and other
agricultural uses. A further advantage of recycling yard wastes is that they
are easy to separate from the rest of the MSW stream at their point of origin.
Income from the sale
of the finished product and saving the cost of purchased compost are potential
financial incentives for setting up a composting operation. Considerable market
research is necessary before entering the compost sales business because supply
and demand is site specific.
An environmental
benefit of composting rather than landfilling yard wastes is the reduction in
the amount of methane, a greenhouse gas, released into the atmosphere. When
organic materials decompose anaerobically in a landfill, they produce methane.
When they decompose aerobically through composting, they do not. EPA estimates
that increasing the national recycling rate to 35 percent from its current
level of 28 percent would reduce greenhouse gas emissions by another 9.8
million metric tons of carbon equivalent.
While there are
benefits to composting, waste-handling facilities (including yard-waste
composting operations) can raise public concerns. Nearby residents should be
alerted and educated early in the process of planning a yard waste composting facility.
Well-educated and informed citizens often become the most vocal supporters for
a composting facility.
ISSUES
When planning a
municipal yard waste composting program, the following areas need to be addressed:
quantity of material, equipment, material collection, facility siting,
staffing, public education, and marketing/end use.
1.
Quantity of Material: Determining the amount of yard waste
that will be available can be done through the use of established generation
rates or actual weight studies. Since yard waste does not occur at a constant
rate throughout the year, care must be taken in the analysis of collected data.
In most cases, existing generation rates should be adequate.
2.
Equipment: Equipment for a composting program must be
able to handle movement, turning, watering, screening, and monitoring of the
material. Specialized equipment is available for collection and windrow
turning, but is not necessary. The use of a screen does, however, create a uniform
sized material which helps in the marketing of the end product.
3.
Material Collection: Collection of yard wastes for a
municipal program can be separated into three categories: dropoff, curbside
pickup in bags or other containers, or bulk pickup where the leaves are
collected loose off the street. If bags are to be used for collection, it is
advantageous to use biodegradable plastic or paper. This type of bag can be
shredded and mixed into the compost while non-degradable plastic bags must be
removed prior to composting. Bulk collection requiring the material to be
scooped, raked, swept or vacuumed off the street, can be slow and may contain
contaminants from the street. The choice of collection methods should be
determined by cost, convenience, household participation rate, and the amount
and type of yard waste to be collected.
4.
Facility Siting: Land requirement will be dependent on the
volume of yard waste to be collected and the level of technology to be
employed. As the level of technology increases, the amount of land required for
processing decreases. In general, one acre of land can support 4,000 to 6,000
cubic yards of loose material. Criteria to be considered for a composting site
are: location, size accesibility, soil drainage, surface water, topography,
buffers, and security. It is important that the site be adequately sized to handle
all of the current and future material that will be received at the facility.
5.
Staffing: A staff that is dedicated and that
understands the material and the composting process is needed to ensure a
successful program. Of the staff's responsibilities, the areas of windrow
monitoring, recordkeeping, and quality control are the most important.
6.
Public Education: Education is a vital component of any
successful composting program. Education and promotional programs should start
as soon as the planning process is initiated. The information should answer
these basic questions: what, when, why, how and where. Information can be
distributed in a number of different manners with each targeting a different
audience. Education should not stop once the program has started, but be a
continuous process with updates and reminders to maintain interest and participation.
7.
Marketing/End Use: There are a number of uses for
compost. As a soil amendment, it improves the texture, porosity and water
holding capacity; it also increases the organic content of the soil. For mulch,
it is placed around plants to suppress weeds, modify soil temperature, and
conserve soil moisture. On slopes, it can be used for stabilization and reducing
soil erosion. In a greenhouse or nursery, it can be used as one of the
components of a potting soil mix.
The product can be
given away, sold, or traded to residents, landscapers, nurseries, greenhouses, and
local governments. It is usually distributed in bulk with pick up at the
composting site by the user. As with any product, the higher the quality, the
easier it is to market. Nurserymen and landscapers are more apt to reject a
product with extraneous material in it, so if they are to be a major outlet for
the compost, they should be contacted in the initial planning stages to ensure
that an acceptable product is produced.
CONCLUSION
Once the Council has
clearly defined the goals of its program, it will be easier to evaluate
available technologies and determine the role that composting will play in the
community’s overall management strategy. In addition to goal-setting is
important to evaluate the economic and technical feasibility of composting in
the context of other waste management techniques, such as landfilling and incineration,
to determine which alternatives are most suitable for the community The costs
and benefits of each option as well as relevant political and public opinion
considerations can be evaluated to ascertain which mix of solid waste
management approaches will best serve the community
Composting is good clean fun.
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