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After
exploring various options, the Town Council of Groton,
CT, developed a residential waste transfer facility
that ably serves its residents.
By
Nancy M. Oram and Gary Schneider
Prior
to the promulgation of EPA Subtitle D landfill regulations,
the coastal town of Groton, CT, used three landfills
for the disposal of waste generated by its 40,000 residents
and commercial establishmentsone MSW landfill
and two for bulky waste items. Realizing it would not
comply with the 1993 deadlines established by these
new rules, the town entered into a long-term agreement
with the Southeastern Connecticut Regional Resource
Recovery Authority (SCRRRA) for the disposal of its
MSW at SCRRRA's nearby waste-to-energy facility. This
facility is 12 miles from the town's transfer station
and offers a reasonable tipping fee, representing the
lowest cost alternative for offsite disposal.
Groton closed
its MSW landfill and focused on reaching capacity and
closing the adjacent bulky-waste landfill, which occurred
in 1997. That left the town with one bulky-waste landfill
for the disposal of wastes not accepted at the SCRRRA
facility. Because the state wanted to close all unlined
landfills, the town signed a consent order with the
Connecticut Department of Environmental Protection (CTDEP)
to close its remaining landfill and come up with an
alternative means of handling its difficult-to-manage
(DTM) wastes, which include bulky waste, oversized MSW,
construction-and-demolition debris, appliances, propane
tanks, tires, scrap metal, brush and storm debris, batteries,
and waste oil.
A study was
done to define the waste items of concern, determine
current and future waste quantities, and evaluate long-term
options. All residential MSW was collected curbside
throughout the town, so the study focused on materials
that could not be or were not being collected curbside
and/or were not accepted at the waste-to-energy facility.
Six options were developed:
- No
action: This option consisted of the town no longer
providing a means for its residents to dispose of
their DTM wastes.
- Residential-only
transfer station: This option would provide a
disposal location for residential DTM wastes only.
- Truc-
haul transfer station for all town waste: This
facility would handle both residential and commercial
DTM waste generated within the town.
- Regional
truc- haul transfer station: This facility would
be similar to the prior option but would accept DTM
waste from the region surrounding the Groton area.
- Regional
rail-haul transfer station: This facility would
be similar to the prior option, but DTM waste would
be loaded into railcars and hauled out of town.
- New
landfill: This would entail construction of a
new landfill within the town, designed to handle the
residential and commercial DTM wastes for 20 years.
Since the
town wanted to continue providing DTM waste-disposal
service for its residents, the no-action alternative
was eliminated. A brief siting study was then done by
comparing available land with the siting requirements
for each type of facility. This analysis determined
that developing a new landfill was not feasible due
to lack of suitable land within the town. It also determined
that no town-owned parcels were available for the larger
amount of land needed to develop regional facilities
or a facility to handle both residential and commercial
DTM waste generated in the town. While purchase of a
private parcel was considered, land costs in southeastern
Connecticut precluded the feasibility of these options.
The Groton Town Council ultimately authorized development
of a residential DTM waste transfer station at its existing
residential drop-off facility, even though this was
not one of the lower-cost options.
The Site
The approximately
6-acre site of the existing facility was chosen to minimize
costs and expedite implementation. This site was advantageous
because it was already accepted by the residents, remote
from the nearest neighbors, and owned by the town. The
site included an existing equipment garage that was
worth salvaging and several other small structures that
were demolished prior to construction.
The following
site constraints had to be considered:
- Location
and ground elevation at the existing equipment garage
- Property
lines and required setbacks
- The adjacent
landfill, landfill gas flare, and SCRRRA recycling
facility
- Location
and elevation of existing entrance and exit access
roads
- Buffers
to Flanders Road required by the town planning commission
- Areas
required for stormwater control and onsite sewage
disposal
Habits of
the residential users of the old drop-off facility were
observed to optimize the new facility layout. Noted
concerns included:
- Insufficient
space for residents backing up trailers
- Unloading
delays
- Insufficient
number of dumping locations
Additionally,
residents bringing woodwaste, brush, leaves, and appliances
typically did not have other materials for disposal.
The town
wanted to add a building with an office from which the
facility manager could observe site operations, an employee
lunchroom, restrooms for the employees and the public,
and a drive-out basement for storage of consumer electronics
and fluorescent bulbs.
Also important
was ensuring that construction could be accomplished
while the facility remained open for residents' use.
Mike Picard, CDM associate, explains: "We needed
to plan the site layout to allow uninterrupted use of
the site as a residential drop-off facility while construction
was taking place."
Based on
these considerations, the site layout was divided into
two main areas: one where materials were generally stockpiled
for later processing or recycling, and one that included
a retaining wall for grade separation to allow residents
to directly deposit waste into containers. Construction
was staged, allowing half the site to be used as a temporary
drop-off facility while the retaining wall was being
built, and switching operations to the retaining wall
area while the stockpile area was finished.
Residents
dropping off woodwaste, brush, and leaves are kept separate
from other users in the new transfer station layout.
These wastes can be deposited by parallel parking to
the stockpile area (with three lanes of traffic available
to pass those dumping), limiting the amount of backing
required. Residents dumping bulky waste items or construction-and-demolition
debris can bypass the stockpile area, driving directly
to the retaining wall. A total of 14 dumping spaces
are provided at the retaining wall, allowing quicker
access to this area.
As residents
enter the new facility, they drive up an access road
with two curves (designed to reduce speeds) and approach
the attendant's shelter. The attendant directs the residents
to the stockpile area or the drop-off area at the retaining
wall depending on the type of waste to be disposed of.
The stockpile area has a road encircling it, allowing
the drop-off of woodwaste, appliances, leaves, brush
and yard debris, propane tanks, and tires. Residents
can gain access to the give-and-take shed and drop off
batteries, waste oil, and antifreeze in a three-sided
shed along this road encircling the stockpile area.
Residents disposing of scrap metal, oversized MSW, and
construction-and-demolition debris bypass the stockpile
area and deposit their items over the retaining wall.
To accommodate
the tub grinder and trucks hauling rolloffs and trailers,
a separate access road was constructed at the residential
entrance that goes straight into the site, allowing
vehicles with a large turning radius easier access.
These vehicles typically use the site on days that the
transfer station is closed to residents. A gate between
the building and the grassed area where the septic system
is located directs residential vehicles to the left
around the access road leading to the attendant's shelter
rather than directly into the site.
The Materials
During design
of the transfer station, the town inventoried the various
types of waste that were being delivered to the existing
drop-off station and landfill. These wastes were categorized
as materials that could be reused within the community
(such as woodwaste and yardwaste), materials that could
be recycled (such as waste oil and scrap metal), materials
that needed special handling (such as tires), and all
other materials that would require disposal.
The new facility
was designed to accept the materials listed below. The
town would also establish a small give-and-take center
where residents could leave reusable items for others
to take. The handling method for each of the materials
currently accepted at the DTM waste transfer facility
is discussed below.
Brush
and yardwaste are accepted in a lay-down area and
stockpiled. Once a sufficient quantity is collected
(enough to keep the tub grinder busy for at least two
days), a tub grinder that is owned and operated by SCRRRA
is brought to the site and the woodwaste is processed.
The material is ground twice, and the resulting mulch
is made available to the town departments and residents.
Leaves
and other compostable materials are collected at
the facility and stockpiled as well. Once a week (or
more often if required), the stockpiled leaves are brought
to the town's leaf composting facility by town staff.
Screened compost material is brought back to the site
and made available to town residents at no cost.
Pallets
are collected separately in an open-air stockpile area
and reused by the town and its residents.
Empty
propane tanks are stored in a remote area of the
transfer station. Once a wee,k the town removes the
valves (facility personnel have been trained in this
procedure), recycling the empty bottle with the general
scrap metal and recycling the brass valves separately.
Appliances
are deposited by residents directly on a paved pad.
Once a month, a specialized firm is contracted by the
town to remove any Freon. Once the appliances are certified
to be Freon-free, the town removes all capacitors and
they are loaded into a rolloff container for delivery
to a local scrap metal recycling facility.
Tires
are loaded into a 53-foot box trailer and delivered
to a tire-to-energy facility.
Consumer
electronics and fluorescent bulbs are deposited
in 1-cubic-yard gaylords, which are stored on-site until
enough containers are collected to fill a 40-foot-long
box trailer. The collected consumer electronics are
recycled; fluorescent bulbs are collected and handled
by a licensed waste hauler. Since CTDEP was considering
a ban on these materials being delivered to a waste-to-energy
facility, an area was included to collect these materials
at the DTM waste facility.
Waste
oil, oil filters, antifreeze, and automobile batteries
are collected in appropriate containers under a three-sided
concrete-block building and recycled by licensed facilities
within the state.
The give-and-take
center is adjacent to the waste oil area (within
the same building but separated by a block wall). Residents
are allowed to leave reusable items for others to take
and reuse. Larger items such as bicycles can be deposited
on a paved pad outside the building area.
Scrap
metal is deposited by residents over a retaining
wall directly into a rolloff container. Town employees
sort any unacceptable waste from the container using
a rubber-tired grapple. Once the container is full,
it is delivered to a local scrap-metal recycling facility.
Bulky
items such as furniture are deposited by residents
over a retaining wall onto a paved pad. The items are
size-reduced using the grapple and/or a rubber-tired
loader and are loaded into a rolloff container for delivery
to the SCRRRA waste-to-energy facility.
Construction
debris that can be size-reduced and sent to the
waste-to-energy facility is handled similarly to the
bulky items. Metal items are recycled in the scrap-metal
container, and other construction debris is deposited
by residents into a 2-cubic-yard container. This small
container is transferred to a 100-cubic-yard transfer
trailer, which is hauled to a Subtitle D landfill in
Massachusetts.
Demolition
debris is deposited directly by the residents in
the 2-cubic-yard containers discussed above.
Mobile
homes and boats are included as personal property
under Connecticut law, requiring the town to take possession
of and store these items for 15 days if they are abandoned.
The DTM waste transfer station includes an area where
these items can be stockpiled during this waiting period.
Once the waiting period has expired, the town has the
mobile homes inspected for asbestos (and has it removed
if found) and dismantles the mobile home or boat, recovering
and recycling as much material as possible. The remainder
is deposited in the 100-cubic-yard trailer and deposited
in the landfill. The dismantling occurs on days when
the transfer station is closed to the public. If these
items have any value, the mobile home park or boat yard
typically will keep them as payment for back fees.
The Approach
A design-build
(DB) approach was used to meet an ambitious construction
schedule and maximize the use of town forces for construction.
CDM performed
the vertical construction, such as the buildings and
retaining walls; installed the new water system; rehabilitated
the existing equipment garage (new roof, electrical
service, concrete floor, and paint); put in the site
security fencing; and installed new underground electrical
service. The town's Department of Public Works employees
performed horizontal construction, such as site work,
building and wall excavation, stormwater system installation
(including piping and a new detention basin), installation
of a new septic system, grading, paving, and landscaping.CDM
and town crews worked side-by-side to complete the project
within scheduleprior to the closure of Welles
Road Bulky Waste Landfill. Construction began in the
spring of 2002, and the facility was operational by
early September of the same year. The DB approach not
only expedited construction, but saved the town money
since detailed bidding documents were not required.
According to Gary Schneider, the Town of Groton's Public
Works Director, "Using a partnered DB approach,
we reduced approximately 10% of the facility's cost
and completed the project faster than if we had to conduct
a design-bid-build process."
The Facility
Since the
facility's completion, the DTM transfer station is more
efficient and user-friendly. The facility has been operational
for about two years now. It is open Thursday through
Sunday, serving an average of 600 residents a week.
The facility was immediately accepted by the town's
residents, traffic flow was eased and congestion reduced,
and waste that was previously landfilled is being successfully
diverted.
Operation
of this transfer station offers the residents of Groton
the ability to dispose of many items not commonly collected
curbside, while maximizing the reuse of items typically
disposed of in the wastestream. Potentially toxic or
dangerous materials are removed prior to disposal, and
recyclable or reusable materials are removed from the
waste, saving the town money in terms of their ultimate
disposal costs.
Gary Schneider
remarks, "Since the DTM transfer station's completion,
we have seen a remarkable increase in the amount of
materials that we are able to recycle. Currently, we
send approximately 25% of the materials to a waste-to-energy
facility and 11% to a landfill. The majority is recycled."
He adds, "Before this new facility was completed,
we sent almost all of the waste to the landfill. We
have reached our goal to reuse and recycle as much DTM
waste as possible."
The woodwaste
chipping operations have been particularly successful.
The town is able to control the content of what is chipped
and make the end product a usable commodity. Through
the use of the SCRRRA tub grinder, this material that
was previously landfilled is now beneficially used.
The facility
also maximizes the amount of materials that can be dropped
off by residents by being flexible. It can be adapted
to changing materials, seasonal variations in wastestreams,
and future regulatory requirements.
Difficult-to-manage
wastes in Groton, CT, are not difficult any more.
Nancy
M. Oram, P.E., is CDM project manager in Wethersfield,
CT, and Gary Schneider is Town of Groton (CT) public
works director.
MSW
- September/October 2004
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