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Solid Wood Packing Material as a
Pathway for Nonindigenous Species

Eric
Allen
In the past decade, solid wood
packing material (SWPM) has become recognized as a major pathway for
the introduction of woodborne nonindigenous species. Infested SWPM
has been implicated as the source for several recently discovered
exotic pests, notably the pine shoot beetle (Tomicus piniperda)
in eastern North America, the Asian longhorned beetle (Anoplophora
glabripennis) in New York and Chicago, and the pine wood
nematode (Bursaphelenchus xylophilus) in Portugal. With the
increased movement of trade goods around the world in recent years,
the problems associated with SWPM have become a global issue that
will require global-scale solutions. This paper will describe the
nature of SWPM, why it poses a risk, the magnitude of the risk, and
what steps might be taken to reduce the risk.
What is solid wood packing
material?
The USDA APHIS defines
solid wood packing material as “wood packing materials other than
loose wood packing materials used or for use with cargo to prevent
damage, including, but not limited to, dunnage, crating, pallets,
packing blocks, drums, cases and skids” (USDA, 1998 http://www.aphis.usda.gov/oa/alb/interimalb.html)
(Fig. 1). Manufactured wood products, such as plywood, particle
board, or oriented strand board, are not considered a risk.
 |
Figure 1. Solid wood
packing: pallets and crates |
Why is solid wood packing material
a problem?
The properties of the wood
commonly used as packing material contribute to the hazard. SWPM is
typically made from rough-sawn, low-quality wood or by-products of
milling that are not acceptable as higher lumber grades. The wood
may include bark or wane from the outside of the stem, insect grub
holes, and fungal decay or stain. Such low-value wood is generally
green, untreated by heat or chemicals, and may remain a favorable
substrate for living organisms, particularly insects and fungi. In
addition to problems related to these physical characteristics, SWPM
pose other concerns. Except for the direct trade of packing
materials, they are not a commodity and are difficult to monitor
during quarantine inspection procedures. Even when high-risk packing
is identified in a shipment, the inspection process is complicated
by limited access to visible surfaces (most surfaces are not facing
the inspector or the cargo is buried deep in a container) and the
cryptic nature of many wood-inhabiting organisms (little or no sign
of their presence is evident at the surface). Latent fungal
infections or insect larvae (e.g. the wood-wasp Sirex) are
virtually impossible to detect through inspection of outer wood
surfaces. Packing materials may also be repaired, reused, and moved
from country to country before they are disposed of. This furthers
the likelihood of unintentional movement of infested wood or wood
that is reinfested in transit. Disposal methods may also add risk.
In Canada, wooden cable spools carrying cable for forestry use have
been left in forest settings-potentially moving wood-inhabiting
pests directly to the forest (Fig. 2).
 |
Figure 2. Infested wire
rope cable spools |
What is the magnitude of the SWPM
problem?
Although quarantine
interception records have provided an indication of the kinds of
pests moving with solid wood packing materials, only recently have
studies quantified the risk associated with known volumes of packing
wood. A 1997 Canadian Forest Service audit of 50 Chinese wire rope
spools revealed that 24% of the spools examined still contained live
wood borers, while a total of 31% of the spools had some evidence of
past wood borer activity. Six species of longhorned wood borers (Cerambycidae),
including Monochamus alternatus, Hesperophanes (=Trichoferus)
campestris, Ceresium flavipes, Psacothea hilaris,
Megopis sinica, and Rhagium inquisitor and one species
of Anobiidae, Ptilineurus sp., were reared from these spools.
There was often no visible external evidence of the presence of live
wood borers in these spools: only 63% exhibited external signs of
wood borer activity, while all were found to have some evidence of
past insect activity when disassembled (Allen et al., 1997 http://www.pfc.cfs.nrcan.gc.ca/health/exotics.htm).
In a subsequent study in July 1998,
live beetles were found associated with shipments of granite from
Norway. Green spruce bolts had been used to brace large granite
blocks inside shipping containers (Figs. 3 and 4). More than 2,500
adult insects representing more than 40 species of bark beetles,
wood borers, and their associated parasitoids, predators, and
scavengers, such as well as bluestain fungi and nematodes were
recovered from 29 log bolts (Table 1). At least three species of
Scolytidae of quarantine significance, Pityogenes chalcographus,
Polygraphus poligraphus and Ips typographus, were
recovered from these bolts.
 |
 |
| Figure 3. Unloading
imported granite blocks. |
Figure 4. Green Norway
spruce bolt bracing granite blocks. |
Table 1. Bark
and wood-boring beetles and wasps reared from intercepted spruce
bolts from Norway used as dunnage.
|
Family and Species |
No. of Individuals |
|
Scolytidae |
|
|
Pityophthorus micrographus |
942 |
|
Pityogenes chalcographus |
284 |
|
Polygraphus poligraphus |
207 |
|
Ips typographus |
27 |
|
Crypturgus hispidulus |
16 |
|
Pityophthorus pityographus |
1 |
|
Cerambycidae |
|
|
Tetropium fuscum |
44 |
|
Callidium coriaceum |
3 |
|
Molorchus minor |
1 |
|
Pogonocherus fasciculatus |
1 |
|
Semanotus undatus |
1 |
|
Anobiidae |
|
|
Anobium
sp. |
10 |
|
Ernobius explanatus |
4 |
|
Curculionidae |
|
|
Rhyncholus
sp. |
1 |
|
Melandryidae |
|
|
Serropalpus barbatus |
7 |
|
Siricidae |
|
|
Sirex juvencus |
21 |
What steps might be taken to reduce
the risk?
With the heightened
awareness of SWPM as a significant pathway for invasive species, a
global effort has been initiated to develop international standards
for the treatment and regulation of SWPM. Although such an
initiative will result in added costs to shipping and packing
industries, it is clear that the phytosanitary benefits of such a
program be worthwhile. This type of approach, in conjunction with
enhanced surveillance, using improved detection tools and inspection
methods will greatly reduce the negative impacts of nonindigenous
species.
Further Reading
Allen, E.A.,
Humble, L. M., Dawson, J. L. M., and Bell, J.D. 1997. Exotic
interceptions from wooden dunnage and packing material. North
American Plant Protection Organization Bull. No. 15, Abstracts of
the 21st annual meeting and colloquium on quarantine security.
Seattle, WA Oct 20-24, 1997. http://www.pfc.cfs.nrcan.gc.ca/health/exotics.htm
(accessed Jan 12, 2001)
USDA 1998. Solid wood packing
material from China; Interim Rule 7 CFR Parts 319 and 354 http://www.aphis.usda.gov/oa/alb/interimalb.html
(accessed Jan 12, 2001)
USDA 2000. Draft pest risk
assessment for importation of solid wood packing materials into the
United States. Primary contact: J. Pasek, USDA APHIS Raleigh NC. |