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Georgia Forestry Commission
Forest Health Fact Sheet
FOREST PEST
MANAGEMENT
GEORGIA FORESTRY COMMISSION
SOUTHERN PINE BEETLE
CONTROL TECHNIQUES
Southern pine beetle (SPB) caused timber losses
can be reduced through the use of one or more recommended direct-control tactics. SPB control, to be most effective, should be a year-round activity Major efforts should be made from late spring through fall to control actively spreading infestations. Winter and early spring treatment is also important to reduce the
potential for spot growth as well as new spot development later in the spring and summer. Although infesta-
tions are concentrated in fewer trees for longer periods of time during the colder months, the spots are harder
to detect from the air because of slower crown discol-
oration.
DEFINITIONS
The techniques used for SPB control are based on biological and cost effectiveness. Furthermore, they refleci the reality of SPB outbreaks and focus on the achievable goal of controlling spot growth. Four techniques or methods are used to control SPB spot growth.
A brief definition of each follows:
-- 1. Cut and remove felling and removal of infested
trees and a buffer of adjacent, uninfested, green trees. (Figure 1) This technique reduces the number of bee-
tles available to attack new trees.
-- 2. Cut and leave felling of infested trees and a buffer
of adjacent, uninfested, green, trees toward the center of the spot. This technique disrupts pheromone production and beetle attack-
behavior.
-- 3. Cut and hand spray felling, limbing and
bucking infested trees into manageable lengths and hand spraying with Lindane or Dursban (Chlorpynfos). This technique destroys beetle broods before and during emergence.
-- 4. Pile and bum felling, piling and burning
infested trees to destroy beetle broods before
RtCEIVEb
they emerge.
2 DEC. 1 1994
DUCUMENTS
,
August). When cut and remove is
used, only infested trees should be cut; trees vacated by the SPB should remain standing. Uninfested trees within a 200-foot red-cockaded
woodpecker buffer should not be
cut unless absolutely necessary to
prevent the SPB from infesting
cavity trees.
Fig. 1 . The buffer stnp should be at least the width of the tallest trees in the spot, and should encom-
pass the active head.
CUT AND REMOVE
General Forest Area Cut and remove is the prompt
removal of infested trees. Removal of infested trees and an adequate buffer strip prevents spots from spreading. The inclusion of a buffer ensures the removal of freshlyattacked pines that were overlooked or became infested after the spot was first evaluated and marked. SPB infested trees must be promptly
removed to achieve maximum effec-
tiveness: stopping additional spot spread. Because both the beetles
and their associated pheromone source are removed from the site,
the potential for spot spread is minimized.
Managers and owners usually prefer cut and remove over the other control options because infested trees are removed from the forest and used, giving the landowner
some financial return. However,
removal of individual spots is not always practical because of inaccessibility insufficient volume, poor lum-
ber or pulpwood markets, and
environmental considerations. In addition, cut and remove often takes longer to implement than alternative tactics. Despite these limitations, cut
and remove, when properly and
promptly applied, remains the most practical and economical control tactic for treating most large, rapidlygrowing infestations.
Near Red-Cockaded Woodpecker Colony Sites
Cut and remove can be disruptive to the red-cockaded woodpecker and should not be used during the red-cockaded woodpecker breeding season (from March 1 until the young have fledged, approximately July-
CUT AND LEAVE
General Forest Area Cut and leave involves felling
infested trees and a buffer strip of uninfested trees so that the crowns point toward the center of the spot. This treatment disrupts spot growth and causes emerging adult beetles to disperse into the surrounding forest. It is usually recommended for spots with 100 infested trees or less.
Cut and leave is practical, relatively inexpensive, and requires
a minimum of labor, equipment,
and training. The procedure can be applied soon after spots are
detected. Freshly-attacked trees are
sometimes difficult to detect during
the early stages of attack. Therefore,
the major disadvantage is that a
buffer strip of green, uninfested
trees must be felled around each
spot to assure that freshly-attacked trees are included in the treatment.
In the general forest area, many
landowners, are reluctant to sacrifice this buffer if the trees cannot be salvaged.
Expanding spots involving more than 100 active trees are more difficult to stop with cut and leave. Breakouts are more likely to occur for spots exceeding 100 active trees.
Nevertheless, cut and leave
remains useful mainly because of
-- another beneficial effect when a
buffer strip is included, it usually
stops the expansion of a spot. The
biological rationale for spot
disruption by cut and leave is based on the way individual spots expand dunng the summer. Continuous spot growth requires at least three factors: emerging beetles, nearby pine trees, and a source of secondary attractants. Felling the most recently attacked trees eliminates the attractant source. The felled buffer strip eliminates nearby unattacked pines, and beetles emerging from the infested trees tend to disperse in the absence of
attractants.
The fate of beetles that are not killed or removed mechanically has been partially explained by SPB population dynamics research. This research has determined that longrange beetle dispersal normally
occurs when temperature
-- conditions are favorable from
November through March. Very little dispersal occurs dunng the warmer months because of the weakened physiological condition
-- of the beetles the stored fat from
which the beetles draw energy for
flight is lowest during this period.
Near Red-Cockaded Woodpecker Sites
Cut and leave is the preferred technique for controlling spots near red-cockaded woodpecker colony sites during the birds' breeding season. The effectiveness of this
method is greatest from May to
October, which generally coincides with the red-cockaded breeding sea-
son. After the breeding season and during the winter months the more effective cut-and-remove method can be used. Trees vacated by the SPB will not be cut. Uninfested trees within a 200-foot red cockaded woodpecker colony buffer zone will not be cut unless absolutely necessary to prevent the SPB from infest-
ing cavity trees.
CUT AND HAND SPRAY
General Forest Area Cut and hand spray is the felling,
limbing and bucking of infested trees into manageable lengths and hand spraying with an insecticide.
Insecticides may be used to control
the SPB in individual trees or small groups of trees. Registered insecticides, Lindane and Dursban
(Chlorpyrifos), are available for this
purpose. Although chemical control is costly and raises some environ-
mental concerns, it may be the best
alternative in urban forests, highvalue recreational areas and, to a limited degree, in commercial
forests when other methods cannot
be used. Because of high costs and
environmental concerns, no large-
scale chemical bark beetle control projects are likely to be undertaken in the South. Nevertheless, a need remains for a fast-acting, effective
tactic to reduce SPB concentrations. To date, only insecticide sprays can
assure this level of protection. In
commercial forests, insecticides are useful for treating small spots during the winter, spots inaccessible to heavy equipment, and or breakouts.
The use of insecticides in forests
will be limited because of high costs, the need to fell and spray all
surfaces of infested trees, safety
precautions, and toxicity to non-tar-
get organisms.
Near Red-Cockaded Woodpecker Colony Sites
This method can be used when
alternative methods are outside their effective period (cut and leave during March and April) or not
feasible, or when a biological
evaluation determines that foraging
habitat loss due to control must be minimized. In no case will any standing trees be sprayed.
PILE AND BURN
General Forest Area Pile and burn refers to the felling,
piling, and burning of infested trees. This technique is one of the oldest SPB control methods, and also is
one of the most effective when
properly done. However, because of high costs and environmental constraints, the practice has been used sparingly in recent years. The bark must be completely burned to achieve control. Vacated trees need not be cut, piled, and burned. For practical reasons, both infested and vacated trees are usually piled and burned to clear the site for regeneration. Because burning can cause wildfires, this technique should be restricted to periods of low fire danger. Also, federal and state air pollution laws must be
followed.
The biological rationale for pile and burn is comparable to that for
cut and remove and cut and hand
-- spray the beetles are destroyed if
the infested bark is completely burned. This practice has been largely abandoned, however, because of the labor and logistical problems involved. In most cases, heavy equipment must be used to pile the trees. In wet areas, burning felled trees becomes extremely difficult. In dry areas, the procedure increases the chances of wildfire, and burning must be restricted to
days when fire danger is low.
Near Red-Cockaded Woodpecker Colony Sites
This method will not be used in or near active red-cockaded wood-
pecker colonies.
BIOLOGICAL CONTROL
Several species of parasitic and predacious insects feed on southern pine beetles. Their ability to keep the southern pine beetle under control
depends on many factors. The insect
most famous for its ability to devour
southern pine beetles is the checkered beetle. (Figure 2) Regardless of the control technique, older killed trees should be left standing where
feasible to protect as many checkered
beetles as possible. These older kills usually harbor numerous checkered beetles, and they also provide various woodpeckers with nesting sites.
Fig. 2. An adult checkered beetle feeding on a southern pine beetle Checkered beetles require a longer development period than southern pine beetles and this reason that older kill trees be left when feasible