| Building
Deconstruction: Reuse and Recycling of Building Materials
Prepared
by:
Powell Center for Construction and Environment, University of
Florida
PO
Box 115703, Gainesvil\-le, Florida USA 32611-5703,
Tel: (352)-392-7502
On
behalf of:
Alachua
County Solid Waste Management Innovative Recycling
Project, August, 2000
Acknowledgements
The
Construction Site Supervisor for this project was
Mr. Kevin Ratkus. Data Collection was performed
by Mr. Sean McLendon and Mr. Bradley Guy. The Principal
Author of this report was Mr. Bradley Guy, including
materials prepared by Mr. Sean McLendon.
ABSTRACT
The
PCCE deconstructed six (6) houses during 1999-2000
to examine the cost-effectiveness of deconstruction
and salvage when compared to traditional demolition.
This research was funded through the Florida Department
of Environmental Protection (FDEP) Innovative Recycling
Projects grant program through Alachua County. The
one and two-story houses that were deconstructed
represent typical Southeastern US wood-framed residential
construction from 1900 to 1950. Regulatory issues
included the costs and implementation of environmental,
demolition, and historic permitting practices in
the Gainesville / Alachua County, Florida region,
and handling of lead-based paint (LBP) materials,
and asbestos containing materials (ACM). Worker
safety issues and technical issues included protection
from environmental and site hazards and a case-by-case
materials management process for each building.
Reuse and materials redistribution scenarios include
on-site and off-site redistribution and associated
costs and benefits. Over 500 pieces of salvaged
lumber were visually graded by the Southern Pine
Inspection Bureau, to understand the damage of
use and the deconstruction process on salvaged lumber
in reducing use in structural applications.
KEYWORDS:
deconstruction, selective dismantling, C&D wastes
management, building salvage, building materials
reuse.
Project
Background
From
August, 1999 to May, 2000 the Powell Center for Construction and Environment, University of Florida, with funding
from Alachua County Public Works Division and the
Florida Department of Environmental Protection (FDEP)
deconstructed six (6) wood-framed residential structures
in Gainesville, Florida. University students provided
labor on the first three buildings and Americorps*NCCC
members worked on the second three. Houses were
acquired mainly through word of mouth. Permitting
processes included issues of historic preservation,
demolition delay requirements, licensed contractor
requirements and environmental, safety and health
certifications for hazardous materials management,
utility disconnections, and septic tank removals.
Each house was tested for lead-based paint (LBP)
and asbestos containing material (ACM). All structures
were completely removed from the site, comparable
to a total demolition. Time and activity data was
collected for each worker and all associated costs
and estimated revenues from salvaged materials were
calculated. Each building was also estimated for
demolition in order to make a comparison with deconstruction
and salvage. There was considerable variety in the
buildings’ conditions, the location of the buildings,
and the efficiency of each deconstruction.
Buildings
Summary
The
structures ranged from approximately 1000 to 2000
SF and were both single and two-story. The oldest
structure was built in 1900 and the youngest built
in 1950. The typical construction was a raised wood
floor structure on brick and/or concrete piers,
light wood wall-framing, roof rafters, and interior
and exterior wood cladding and sheathing. Two structures
had plaster and lathe interior wall finishes. In
one case gypsum wallboard was applied directly over
the wood beadboard interior wall finish. One structure
also had two roof finishes, metal over asphalt shingles,
and two floor finishes, an oak floor laid directly
on top of a pine floor. All of the structures had
rot from water damage principally in kitchen or
bath floor areas, but also including wall areas
at leaks from the roof.
Table
One - Summary of Buildings
|
Building address #
|
2930
|
711
|
14
|
2812
|
901
|
3650
|
|
Built
|
1915
|
1945
|
1900
|
1900
|
1920’s
|
1950
|
|
Stories
|
1
|
2
|
2
|
1
|
1
|
1
|
|
Light
framed wood construct.
|
Y
/ CMU
|
Y
|
Y
|
Y
|
Y
|
Y
|
|
Size
(SF)
|
2,014
|
1,436
|
2,059
|
1,238
|
992
|
1,118
|
|
Urban
or rural-sized parcel
|
Rural
|
Urban
|
Urban
|
Rural
|
Rural
|
Rural
|
|
Additions
|
Y
|
Y
|
Y
|
Y
|
Y
|
Y
|
|
#
of additions
|
3
|
1
|
1
|
2
|
3
|
1
|
|
Internal
renovations
|
Y
|
N
|
Y
|
N
|
Y
|
N
|
|
Inhabitable
|
Y
|
N
|
Y
|
N
|
Y
|
Y
|
|
Require
major repair
|
N
|
Y
|
N
|
Y
|
N
|
N
|
| Asbestos
|
|
|
|
|
|
|
|
Exterior
wall finish
|
Y
|
N
|
N
|
N
|
N
|
N
|
|
Roofing
|
N
|
N
|
Y
|
N
|
N
|
N
|
|
Insulation
|
N
|
N
|
Y
|
N
|
N
|
N
|
|
Floor tile
|
Y
|
N
|
Y
|
N
|
N
|
Y
|
|
Drywall
|
N
|
N
|
Y
|
N
|
N
|
N
|
| Abatement
|
Y
|
N
|
Y
|
N
|
N
|
Y
|
| Lead-based
paint |
|
|
|
|
|
|
|
Interior
trim
|
N
|
N
|
Y
|
Y
|
N
|
N
|
|
Exterior
trim
|
Y
|
Y
|
N
|
Y
|
N
|
Y
|
| Interior
surfaces |
N
|
Y
|
N
|
N
|
Y
|
N
|
| Exterior
surfaces |
N
|
Y
|
Y
|
N
|
Y
|
Y
|
| Reason
for removal |
|
|
|
|
|
|
|
Redevelopment
site
|
Y
|
|
Y
|
Y
|
Y
|
|
|
Taxes
/ expense
|
|
|
|
|
|
Y
|
|
Safety
/ disuse
|
|
Y
|
|
|
|
|
|
Homeless
/ fire hazard
|
|
|
|
Y
|
|
|
All
of the structures had additions, and these were
typically for; 1) adding enclosed living space,
2) adding kitchen and bathroom facilities on older
structures, 3) enclosing an existing open porch
area. Four (4) out of six (6) could be made habitable,
and three (3) of six (6) had been recently occupied
prior to the building’s removal. One (1) house
had been occupied by homeless persons without
heating, kitchen, or bathroom facilities. Three
(3) of the six (6) structures were found to have
asbestos containing materials (ACM) requiring
abatement. Two
(2) of the structures contained only non-friable
asbestos which could have been “wet demolished”
by mechanical means but would have required the
entire demolition wastes load to be disposed off
in a hazardous materials landfill. Only one building
had LBP only on the inside, typically LBP was
found on exterior window and door trim, where
it was used in gloss and semi-gloss paint for
durability.
Two
(2) of the six (6) buildings were on property
slated for immediate commercial or multi-family
redevelopment, two (2) were on property slated
for long-term redevelopment, and two (2) buildings
were on land not slated for redevelopment. The
latter two (2) structures may have been left vacant
for an indeterminate length of time if they had
not been used for this project. During the course
of the project, one building verbally committed
to the deconstruction project, on a site slated
for commercial redevelopment, was demolished.
In addition, two candidate buildings, on sites
slated for redevelopment, were moved. One structure
that was considered for the project was considered
too dilapidated for a reasonable deconstruction
and another was passed over due to scheduling
conflicts and was subsequently partially renovated
by the owner. The average size of the six structures
was 1,476 SF.
Based
upon literature review and anecdotal information,
this sample of structures would appear to be representative
of residential demolitions in the United States.
Also, approximately 94% of all residential buildings
built each year in the US are light wood-framed
construction (NAHB, 1994).
Data
Collection
On-site
labor was documented by recording each worker’s
activities on a 15-minute time increment.
There have been several well-documented
deconstruction pilot projects in the US with this
detail of data collection, most notably the Fort
Ord Pilot Deconstruction project conducted by
the Fort Ord Reuse Authority (Cook, 1997) and the Riverdale Pilot Deconstruction
Project conducted by the National Association
of Home Builders Research Center
(NAHBRC, 1997). These projects provided
models for creating the data collection process.
Data is divided into two categories; the deconstruction
of the structure and the processing of the salvaged
materials. The cost of a traditional demolition
was calculated for each structure, including disposal
costs. Salvage revenues were estimated using a
percentage (25-50%) of retail prices from local
building materials suppliers and the experience
of a former used building materials store owner/operator
in Gainesville, Florida. Disposal costs were estimated
by weight and costs data provided by the wastes
haulers for the project.
Worker
labor activities were sub-divided into categories
by the location in, or component of, the building
in order to calculate the costs of deconstructing
a particular component of the building, and the
costs to salvage a unit of a particular material.
The latter information was used to assign a unit
cost of extraction and processing that could be
compared to the pricing units for materials, i.e.
number, linear feet, or board foot of material.
Labor productivity data was collected in the following
task categories:
(S)
upervision
Directing
and planning the flow of work on the job site.
(Decon)
struction
Labor
involved in the initial removal of materials from
the structure. Any manual or mechanical procedure
required to remove materials for salvage, either
the direct handling of a material or removing
other materials to gain aPCCEss to the salvage
material.
(Demo) lition
The
hand or mechanical removal of building materials
for direct disposal.
(P)
rocessing
Preparing
materials for redistribution in reusable form.
Denailing is the most typical processing
activity.
(N)
on-production
No
work is being performed. Includes breaks and the
unloading and clean-up of daily tools, but excludes
lunch.
(C)
lean-up / (Dis) posal
Sweeping
and/or removing debris or demolition materials
from a work area and/or disposal into a roll-off
container.
L)
oading/unloading
Loading
or unloading materials from the site onto a truck
for transport and at the final storage area.
The
largest percentage of time on any deconstruction
was the deconstruction activity, an average of
26% of total time. The next greatest percentage
of time was spent in processing materials at an
average of 21%. Disposal and cleaning required an average of
17% of total time. Demolition required an average
of ~12% of total time. The house with the largest
percentage of time spent for deconstruction was
the house at 901 SR 301 (47.8%). This house was
being removed for redevelopment and had a very
short time frame for the deconstruction. It was
also located on a major highway in the corner
of a shopping center site, and materials were
redistributed by placing them neatly in separate
piles at the site and posting “Free Materials”
signs to encourage passersby to remove the materials
themselves. All of the materials were removed
within one day after the completion of the deconstruction.
Table
Two - Sample Data Sheet
|
Location:
|
|
|
|
Completed by:
|
|
Date:
|
|
Worker
|
#1
|
#2
|
#3
|
#4
|
#5
|
#6
|
#7
|
|
7:30
|
|
|
|
|
|
|
|
|
Activity
|
|
|
|
|
|
|
|
|
Room
|
|
|
|
|
|
|
|
|
Location
|
|
|
|
|
|
|
|
|
Material
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Activity
|
Supervise
|
Decon
|
Process
|
Demo
|
|
|
|
|
|
S
|
Dec
|
P
|
Dem
|
|
|
|
|
|
Clean/Disposal
|
Non-Prod
|
Load
|
|
|
|
|
|
C/Dis
|
|
N
|
L
|
|
|
|
|
|
|
|
|
|
| |