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Variables for Forensic Evaluation of Degradation of Structural OSB Panels Experiencing “Wet” Service

May 15, 2004

4 • Interface August 2004
Abstract
At many construction projects, the exterior wall and roof
sheathing are comprised of oriented strandboard (OSB) panels produced
by more than one manufacturer or produced by one manufacturer
from more than one wood species. OSB typically consists
of wood strands from one of many tree species (commonly aspen)
that are hot-pressed, using one of two types of “binders,” into composite
panels. OSB panels, however, also are manufactured from
blended batches of wood strands from two or more tree species,
including blended mixtures of hardwood and softwood species.
Wood-rotting fungi of the class basidiomycetes are classified as
white rots and brown rots. In general terms, the brown rots preferentially
feed upon softwood and the white rots target the hardwoods;
however, some of the wood-rotting fungi have broadly
diverse appetites, while others may favor only one or a few host
species.
From the perspective of an invading fungus, wood is: a) structurally,
a natural subway of interconnected tubes; b) nutritionally,
a fast-food shop with limited choices; and c) environmentally, a
desert without running water (paraphrasing Dr. Steven Miller of the
University of Wyoming). The inadvertent introduction of water into
dry structural lumber or engineered wood sheathing can lead to
rapid fungal proliferation, if the wood meets the fungi’s nutritional
requirements. The wood can be expected to satisfy the nutritional
requirements of one or more of the different types of fungal spores
that have been hanging around waiting for wetter environs.
Lack of appropriate weather protection of engineered wood
sheathing during the initial construction process can be a key factor
determining the speed and severity of later biodeterioration
when the panels are re-wetted due to building envelope failures.
There is no readily available evidence to suggest that the use of
a particular binder or wood (of those tree species commonly used to
manufacture OSB) will provide greater overall resistance to the
numerous species of wood decay fungi that may attack the panels;
however, the authors document dramatic differences in the rate of
deterioration by a specific white-rot fungus of two different OSB
panels experiencing the same “wet” service.
The authors conclude that forensic evaluations of OSB sheathing
damage must consider the potential for significantly varying
rates of panel degradation due to differences in composition, even
if all of the inspected panels are from the same manufacturer. Also,
the rates of this structural degradation may have been further exacerbated
by pre-infection of the panels during the construction
process due to deficient weather protection.
OSB Structural Panels
OSB panels now comprise a majority of the structural sheathing
market in North America:
• “By 1973… plywood held a 99+ percent share of the U.S.
domestic structural panels market. At this point, lumber
had been totally displaced as a sheathing material.”
• “By 1983… waferboard shared the market with oriented
strandboard (OSB), and together the two products accounted
for 5.5 percent of the structural market in the United
States.”
• “By 1993… OSB… accounted for one-third of the structural
panels market.”
• “By 2000… North American production of OSB exceeded the
production of softwood plywood.”1
OSB structural panels are manufactured from thin wood
strands2 sliced from logs (in the direction of the wood grain) that are
then dried, mixed with wax and binders, placed into a form in multiple
layers, and hot-pressed into panels. Many tree species are
used to manufacture OSB panels; however, commonly used species
are southern pine, lodgepole pine, “aspen/poplar,”3 yellow poplar,4
sweetgum, and birch. The most commonly available OSB structural
panels are manufactured from the aspen/poplar species.
• “The raw material for the original waferboard product,
which was made from square wafers, was aspen. As this
industry expanded and OSB became the predominant product
manufactured, other species, such as southern pine,
white birch, red maple, sweetgum, and yellow-poplar were
found to be suitable raw materials as well. Small amounts
of some other hardwoods can also be used for OSB.”5
• “Following development with aspen, a variety of other
species have since been incorporated. Currently, mills can
use almost any low-to-medium-density species that is widely
available. Southern pine, spruce, birch, yellow poplar,
sweetgum, sassafras, beech, and others are incorporated
into OSB. Species of relatively high density, such as beech,
are often mixed with species of relatively low density, such
as aspen, to maintain acceptable board properties.”6
August 2004 Interface • 5
All OSB structural panels are manufactured to meet minimum
voluntary performance standards7 when tested for three basic performance
qualities: strength and stiffness, dimensional stability,
and bond durability. The uniformity of these manufacturing standards
has led many in the construction, repair, and consulting
industries to assume that each brand of identically dimensioned
OSB structural panel will provide the same general degree of both
structural and weather-resistive performance, including similar
levels of resistance to biodeteriorative attack by wood decay fungi.
• For most practical purposes, the first assumption is justified:
due to industry-wide implementation of the voluntary
performance standards in the manufacturing process, OSB
sheathing panels by various manufacturers can, at a basic
level, be considered structurally equivalent.
• However, the second assumption – equivalent OSB resistance
to biodeterioration when encountering “wet” service –
is demonstrably incorrect, as further discussed below.
Note: when properly installed as part of a properly designed and
maintained roofing or cladding system, neither OSB nor plywood
panels should be exposed to moisture extremes during the life of
the structure.
For a review of moisture exchange performance differences
between OSB and plywood panels, reference the authors’ article,
“Moisture Exchange Performance of OSB and Plywood Structural
Panels.”8
Wood Decay Fungi
The “wood decay fungi” (wood-rotting species of the class basidiomycetes)
affecting above grade structures in North America are
classified as white rots and brown rots. Wood decay fungi obtain
nourishment by digesting the cell walls of the wood element, resulting
in rapid and severe loss of structural properties.
• “The brown rots selectively attack the cellulose and hemicellulose
of the cell and modify the lignin…. Brown rots
cause dramatic strength loss in the early decay stages. Up
to two-thirds of the total wood substance may eventually be
consumed by brown rot fungi.”
“White-rot fungi have the ability to degrade both the lignin
and cellulosic components of the cell, although the lignin is
usually utilized at a somewhat faster rate. White rots may
change the color of wood only slightly but more often give it
a bleached or whitish color inherent to de-lignified cellulose.
These fungi typically erode the cell outward from the cell
lumen by decomposing successive layers of the cell wall,
much as a river erodes it bank. Thus, the cell wall becomes
progressively thinner, but the wood does not tend to shrink,
check, or collapse, as is often the case with brown rots.
White-rotted wood usually retains its shape, but may eventually
become a fibrous, spongy mass.”9
• “Infection by spores of ‘wood-rotting basidiomycetes’ [WRB] probably does not occur at wood moisture contents below
about 29%…. The mycelium and mycelial cords of WRB can
colonize wood below the fibre [sic] saturation point, possibly
down to 20% MC, provided they are growing from a substrate
at a higher moisture content.”
“Once WRB are established, the minimum moisture content
for decay to proceed is around 22-24%, so 20% is frequently
quoted as a maximum safe moisture content for wood.
…WRB can survive for up to nine years in wood at moisture
contents around 12%. If the wood wets up again, the decay
process can restart.”10
Note that the initial infection by the fungal spores requires an
initial spike of high moisture content (>28% MC), but subsequent
proliferation of the established fungi only requires that the wood
product is “wet” (>20% MC). This observation emphasizes the critical
importance of protecting the sheathing prior to cladding or roofing.
The authors have observed hundreds of construction projects
in which the engineered wood sheathing remains exposed to
inclement weather for weeks or months. Even if it is assumed that
this saturated sheathing remains sound and will properly dry when
the building is closed in, it is also reasonable to assume that some
fungal sporulation either has occurred when the sheathing was
exposed or will occur during the drying of the warmer, closed-in
roof and walls. By allowing the sheathing to become initially saturated
during construction, the builder has created a situation in
which even relatively small future increases in moisture content of
the dried panels can result in rapid biodeterioration and loss of
structural integrity.
The sapwood lumber of all tree species has no inherent resistance
to wood decay fungi. While the heartwood of some softwood
lumber species (e.g., Douglas fir, western larch, and a few of the
pine species) exhibit varying degrees of resistance to decay, the
heartwood of most species used to manufacture OSB – including
aspen, cottonwood, poplar, birch, and the remaining pines – has little
or no decay resistance. Further, note that many trees harvested
for OSB production are sufficiently young to have not produced a
significant percentage of heartwood. Similar lack of heartwood production
occurs with rapidly grown trees from commercial plantations.
• “When a tree or tree part is very young and growing vigorously,
it contains no heartwood. After a number of years,
however, heartwood typically begins to form near the center
of a stem. The most common age at which transformation
from heartwood occurs is reported to be fourteen to eighteen
years. …Some species, such as beech or European ash, may
not begin to form heartwood until reaching sixty to one hundred
years of age.”11
In general terms, brown-rot fungi preferentially attack softwoods
(e.g., Douglas fir, the true firs, larch, pine, and hemlock).
Likewise, in general terms, white-rot decay fungi preferentially
attack hardwoods (e.g., aspen, poplar, birch, and yellow poplar). A
1981 report identified 1,669 species that decay wood in forests or
wood in use in North America. Six percent (113) of these species
cause brown rots and 94 percent (1,556) cause white rots.12 It is
important to note that while some of the wood-rotting basidiomycetes
are very selective about what they eat (some will infest
only one tree species), others have a much broader appetite.
• “Brown-rot fungi commonly colonize softwoods, and whiterot
fungi commonly occur on hardwoods, but both brownand
white-rot fungi occasionally colonize both types of
wood.”13
• “Some fungi have a narrow host range, such as boletus
betulicola on betula spp., while others have a very broad
host range…”14
• “From a fungus point of view, wood is:
6 • Interface August 2004
a. structurally, a natural subway of interconnected tubes
b. nutritionally, a fast-food shop with limited choices
c. environmentally, a desert without running water.”15
Typical wood structural members are manufactured from softwood
species; thus, “brown-rot decay fungi have been the most
common agents of decay in buildings,”16 including the biodeterioration
of plywood sheathing.
Most commonly, OSB structural panels are manufactured from
hardwood species. It is the authors’ experience that white-rot decay
is the most prevalent form of fungal biodeterioration of OSB panels
in buildings; however, we also have observed severe brown-rot damage
of hardwood OSB sheathing.
• Where brown-rot deterioration of OSB sheathing is
observed, these fungi often are found to be expanding into
the panels from adjacent brown-rot decay occurring in softwood
structural members.
• Similarly, where white-rot deterioration of softwood lumber
or timbers is observed, the infestation commonly is found to
have originated in adjacent white-rot decay occurring in the
hardwood sheathing panels.
OSB Panel Manufacture – Type of Binder
In addition to the use of differing tree species and proprietary
variables in the hot-press manufacturing process, the other major
distinction between OSB brands is the type of synthetic “binder”
used to bond (with heat and pressure) the wood strands into a
structural mass. The two major types of binder materials are: phenolic
resins and methane di-isocyanate (“MDI”):
• “Phenolic resins are the most common binder used to manufacture
Oriented Strand Board (OSB), as well as plywood,
glass fibre [sic] insulation and other products. …Phenolics
are the oldest form of plastics. They have been used for a
variety of applications for over 100 years and as wood based
panel binders for over 60 years.”
“Liquid polymeric diphenyl methane di-isocyanate (MDI)
binders are an alternate binder system used by approximately
35% of the OSB mills (alone or in combination with
phenolics) and bring to wood composites the same advanced
polymer technology used in engineering thermoplastics and
polyurethanes.”17
Biodeterioration of OSB Sheathing –
Comparative Observations
Based upon the information provided above – that OSB panels
are manufactured from differing tree species and typically use one
of two different types of binders during the hot press manufacturing
process – it is reasonable to hypothesize that one or both of
these gross variables might significantly affect the potential risk for
biodeterioration if a panel becomes wet.
In other words, the forensic consultant investigating the causes
and extent of a building’s structural deterioration may find it useful
to consider the possibility that the observed conditions have
been selectively exacerbated by wood decay fungi that are targeting
only some of the closely similar sheathing.
Photo 1 – Overview of the work area.
Photo 2 – Hardwood OSB
sheathing with severe white-rot
decay is surrounded by
relatively undamaged hardwood
OSB. The dashed line traces the
upper limit of the migrating
water. Note that the white-rot
deterioration has spread upward
from the water line. (The
localized brown-rot decay at the
upper right is spreading from
underlying infestation of a
softwood-framing member.)
August 2004 Interface • 7
The accompanying photos were taken by ERD in December
2002, at a condominium complex in Seattle, Washington, during a
joint research project with the Forest Products Laboratory to study
potential forensic uses of the “immunodiagnostic wood decay”
(“IWD”) test18 developed by microbiologist Carol Clausen.
• The full results of the joint IWD study are published at
http://www.fpl.fs.fed.us/pubs.htm: (C.A. Clausen, L.
Haughton, and C. Murphy, “Evaluating Wood-Based
Composites for Incipient Fungal Decay with the
Immunodiagnostic Wood Decay Test.”)
Photo 1 shows an overview of the work area. In Photo 2, note the
severe white-rot deterioration at one of the sections of hardwood
OSB sheathing, while the surrounding hardwood OSB sections are
relatively undamaged except for some localized brown-rot damage
at the upper right corner. (The observed brown-rot decay has
spread from an infested softwood-framing member behind the
hardwood sheathing.)
The dramatic differences between the hardwood OSB panels are
further highlighted in Photo 3. Note the water staining across the
face of the otherwise undamaged middle section, tracing the route
taken by the migrating moisture that promoted the severe white-rot
damage at the OSB section at the right. Further, note that this
moisture also has resulted in severe white-rot damage at the OSB
section at the far left. Both damaged OSB sections are by the same
manufacturer.
The severity of the white-rot deterioration at the left and right
sections is advanced. As the panels became saturated and spongy,
the fungi were able to spread vertically above the visible path of
water flow denoted by the water stain. In striking contrast, the middle
OSB section remains sound, firm, and undamaged.
• “The stain pattern from water infiltration that crossed three
sheets of OSB revealed extensive damage to only two of the
sheets. The middle sheet of OSB was not damaged.”19
Field inspection of mill stamps identified two manufacturers for
the inspected OSB panels, which were manufactured in Minnesota
and British Columbia.
• “Removal of the sheathing and subsequent analysis, including
identification of “mill stamps” on the back of the panels,
showed that two different types of OSB were installed at this
area during construction. Inspection confirmed both types
of OSB panels had been installed prior to siding installation
and final inspection of the structure.”20
The undamaged OSB sections were the panels manufactured in
Minnesota.
Further evaluation at the Forest Products Laboratory, supported
by review of online technical publications by the manufacturers,
identified two major differences between the two panels: a) the
British Columbia panels were found to be comprised of aspen (populus
sp.) wood strands with an MDI binder; b) the Minnesota panels
were comprised of birch (betula sp.) wood strands with a
phenolic resin binder.
Unfortunately, the specific wood decay fungus could not be
identified:
• “The visible decay fungus was not culturable from the
mycelial sample …”
• “Wood can be too decayed to recover a culture of viable fun-
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gus or to give positive IWD results. In cases of advanced
decay, where all wood components are utilized, growth of
the decay fungus eventually stops …”21
Moisture readings with a Delmhorst meter, confirmed by laboratory
testing, revealed moisture content levels typically less than
17% (13-15% for the damaged panels and 15-17% for the undamaged
panels), indicating no recent conditions of water infiltration to
the currently dry sheathing. The lack of viable decay fungi indicated
a lengthy period had elapsed since the panels had last been wet.
This situation likely was exacerbated by a dearth of appropriate
food remaining within the ravaged panels, despite the mass of wood
strands available in the adjacent undamaged panels.
• “The condominium complex was constructed in 1997. The
winter of 1998-99 was the wettest on record for Seattle, with
34 inches of rain recorded between November 1 and
February 28 (source: National Weather Service – Seattle). A
forensic building envelope investigation discovered extensive
decay in this complex in 1999.”22
• Records for the 12-month period prior to the 2002 sampling
indicate the total rainfall recorded in Seattle was 32 inches,
more than 5 inches below normal. The summer months that
preceded the sampling were the driest on record for Seattle,
with less than 2 inches of rain recorded in a four-month
period. Further, recorded rainfall during the year 2000 was
more than 8 inches below normal, with the winter of 2000-
2001 recorded as the second driest on record.23
Summary Discussion
The OSB panels were installed at the same period of construction,
as evidenced by the overlying steel strap seen in Photo 2. It is
possible that the damaged panels had been infected with the whiterot
fungi prior to installation, but the almost total absence of whiterot
damage at the adjacent OSB sheathing is strong evidence that
the OSB panels from Minnesota were highly resistant to this particular
wood decay fungus.
The two major variables between the OSB brands were wood
species (aspen vs. birch) and the binder (methane di-isocyanate vs.
Photo 3 – Undamaged center panel is sandwiched by two white-rotted panels. (The dashed line traces the upper limit of the migrating
water.)
August 2004 Interface • 9
phenolic resin). It is reasonable to assume that one or both of these
variables caused the Minnesota panel to be deemed inedible by this
particular specie of white-rotting basidiomycetes.
• Another potential variable, not explored in the joint ERDFPL
forensic analysis reported above, is the differing
amounts of wax added to the binder during the proprietary
manufacturing processes.24 The potential effects of this
added wax to the moisture exchange performance of wet
OSB sheathing are discussed in “‘Moisture Exchange’
Performance of OSB and Plywood Structural Panels.”25
These observations should not be construed as evidence that
birch OSB sheathing manufactured with a phenolic resin binder
can be expected to provide superior overall resistance to wood
decay fungi; however, it is clear that under certain project-specific
conditions, significantly varying decay-resistance performance will
be afforded by some types of OSB panels. Further, the extent and
severity of the deterioration may be exacerbated by the builder’s
failure to properly weather-protect the panels prior to closing in the
roof and walls.
This ex post facto information comes too late to benefit project
design teams, but can be useful in various ways to forensic consultants
evaluating building failures.
• For example, the two accompanying photos confirm that
even a relatively small26 amount of infiltrating water from
one localized flashing failure can result in rapid total
destruction of affected sheathing panels.
• Conversely, note that forensic sampling of only the middle
OSB section could have led to a mistaken conclusion that
the only results of the localized water infiltration had been
simple water staining of the dry sheathing.
It should also be noted that the observed damage is strong evidence
of the rapid rate of biodeterioration of structural wood products
that can occur given the right conditions. Conditions of severe
sheathing decay were observed throughout the project during the
1999 survey, only two years after construction. Given the near total
bio-destruction of the dry OSB panels depicted in the photos, it
must be assumed that:
a. This damage also occurred primarily during the 1998-1999
period immediately following the project’s construction that
included Seattle’s wettest winter on record; and
b. Within the first year after project completion, the aspen OSB
panels already had experienced significant and accelerating
loss of structural integrity and performance. This one-year
timeframe for structural failure can be an important factor
in subsequent insurance claims analyses.
In summary, the building envelope consultant’s forensic analysis
always must extend beyond a single point in time to evaluate the
entirety of the possible conditions that could have led to the current
problems. Clearly, a factor that may require consideration is the
potential for significantly varying rates of panel degradation due to
differences in the OSB composition, even if all of the inspected panels
are from the same manufacturer. Rates of structural degradation
can be further exacerbated if panels have been pre-infected
during the construction process due to deficient weather protection.

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10 • Interface August 2004
References
1. J.L. Bowyer, R. Shmulsky, and J.G Haygreen, Forest
Products and Wood Science – An Introduction (Fourth
Edition), Iowa State Press, Ames, Iowa, 2003.
2. E.g., “Typical strand size is 4.5 to 6 inches long, 0.5 inches
wide, and 0.023 to 0.027 inches thick (USDA 1999).” –
Mackes, K. and Lynch, D., “The Effect of Aspen Wood
Characteristics and Properties on Utilization,” USDA Forest
Service Proceedings RMRS-P-18, 2001. www.fs.fed.us/
rm/pubs/rmrs_p018/rmrs_p018_429_440.pdf.
3. Various species belonging to the genus populus of the willow
family (salicaceae). The poplar species native to North
America is divided into three main groups: the cottonwoods,
the aspens, and the balsam poplars.
4. Liriodendron tulipifera – not a true poplar.
5. Wood Handbook – Wood As An Engineering Material, Gen.
Tech. Rep. FPL-GTR-113. Madison, WI, U.S. Department of
Agriculture, Forest Service, Forest Products Laboratory,
1999. Chapter 10, p13.
6. Bowyer, Shmulsky, and Haygreen.
7. E.g., PS2-92 Performance Standard for Wood-base
Structural-use Panels, National Institute of Standards and
Technology, U.S. Department of Commerce, Gaithersburg,
MD, 1992. www.apawood.org/pdfs/managed/S350D.pdf.
8. L. Haughton and C. Murphy, “‘Moisture Exchange’
Performance of OSB and Plywood Structural Panels,”
Interface (Vol. XXI, No. 6), Roof Consultants Institute,
Raleigh, NC, June 2003.
9. Bowyer, Shmulsky, and Haygreen.
10. Morris, P.I., “Understanding Biodeterioration of Wood in
Structures,” Forintek Canada Corp. / Canadian Wood
Council, http://www.durable-wood.com/pdfs/biodeterioration.
pdf.
11. Bowyer, Shmulsky, and Haygreen.
12. S. Miller, “Basidiomycota,” University of Wyoming, 2001.
http://w3.uwyo.edu/~fungi/Basidios2001.pdf.
13 Wood Handbook – Wood As An Engineering Material, Gen.
Tech. Rep. FPL-GTR-113. Madison, WI, U.S. Department of
Agriculture, Forest Service, Forest Products Laboratory,
1999. Chapter 13.
14 S. Miller, Basidiomycota, University of Wyoming, 2001.
http://w3.uwyo.edu/~fungi/Basidios2001.pdf
15 Ibid.
16 Carll, C.G. and Highley, T.L., “Decay of Wood and Wood-
Based Products Above Ground in Buildings,” Journal of
Testing and Evaluation, Vol. 27, No. 2, March 1999, pp. 150-
158. http://www.fpl.fs.fed.us/documnts/pdf1999/
carll99a.pdf.
17 “Binders and Waxes in OSB,” Structural Board Association,
2002. www.osbguide.com/pdfs/TB114.pdf.
18 www.fpl.fs.fed.us/documnts/techline/II-3.pdf.
19 C.A. Clausen, L. Haughton, and C. Murphy, “Evaluating
Wood-Based Composites for Incipient Fungal Decay with the
Immunodiagnostic Wood Decay Test.” General Technical
Report FPL-GTR-142, Forest Products Laboratory, U.S.
Department of Agriculture, Madison, WI, 2004.
http://www.fpl.fs.fed.us/pubs.htm.
20 Ibid.
21 Ibid.
22 Ibid.
23 Source: National Weather Service – Seattle
24 “Binders and Waxes in OSB,” Structural Board Association,
2002. www.osbguide.com/pdfs/TB114.pdf
25 L. Haughton and C. Murphy.
26 As evidenced by the total lack of damage to some of the OSB
panels that had been wetted by the infiltrating water.
Colin Murphy, RRC, FRCI,
founded Trinity Group
Fastening Systems in 1981. In
1986, he established Trinity
Engineering, providing laboratory
testing and forensic
and material analyses of roof
and building envelope components
and systems. The firm,
now known as Exterior
Research & Design, LLC, is
based in Seattle, WA, and has
an office in Waterbury, CT.
Colin joined RCI in 1986 and became an RRC in 1993.
In 1996, he was honored with the Richard M. Horowitz
award for excellence in technical writing for Interface. In
1998, RCI granted Colin the Herbert Busching, Jr.
Award for significant contributions to the general betterment
of the roof consulting industry. In 2001, Colin was
made a Fellow of RCI. Colin is currently chairman of
RCI’s Manual of Practice Committee.
Lonnie Haughton is a senior
associate of Exterior Research
& Design, commuting to
ERD’s Seattle office from his
home in Mill Valley, CA, where
he resides with his wife and
teenage son. He has a graduate
diploma in business
administration from the
Edinburgh Business School of
Heriot-Watt University in
Edinburgh, Scotland. With a
background in project management, Lonnie first worked
alongside ERD in 1996 at a hotel repair project in Alaska
and then joined the ERD team in 1998. His current
responsibilities at ERD are centered on report production
and analyses of compliance of the “as-built’” construction
with industry standards and the code. He is
certified by the International Code Council as a
Residential Building Inspector and a Commercial
Building Inspector.
ABOUT THE AUTHOR
COLIN MURPHY,
RRC, FRCI
LONNIE HAUGHTON