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BIOLOGICAL
PEST CONTROL OUTDOORS
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Species
Targeted For Biological Control
Introduction Pests encountered outdoors in cities and towns are similar to
those found in agriculture, but the habitat may often differ markedly from agriculture.
Dahlsten & Hall (1999) point out that although the principles of biology
and ecology pertain to the diverse, human structured environment, the diffuse
management and economic goals encountered there make it difficult to apply
ecological concepts to control problems. Integrated pest management has
nevertheless has appeared in the control of pest problems in cities and towns
(Olkowski et al. 1976, 1978; Frankie & Ehler 1978, Frankie & Koehler
1978, 1983; Bennett & Owens 1986) . The National Research Council (1980)
estimated that 5.3-10.6 pounds of pesticide are applied per acre to gardens
and lawns of metropolitan areas, which are higher rates than the average for
agriculture or other managed lands. Olkowski et
al. (1978) have divided pest management in cities and towns into medical,
psychological, architectural, agricultural, floricultural, silvacultural and
horticultural areas. Medical entomologists usually deal with medical and
veterinary problems. Arthropod
fauna in cities and towns is diverse (Frankie & Ehler 1978). As an
example, in a small suburban yard near New York City, there were 1,402 insect
species collected over a few years (Lutz 1941). Human expansion has furnished
some unique opportunities for insects to exploit buildings, and environmental
conditions favorable to insect growth and development year round. A number of
human influences affect the distribution and abundance of arthropods in these
environments. The size of the area may range from a backyard garden with a
couple of fruit trees to miles of highway borders covered by African ice
plant. Native and introduced flora is usually very diverse, as was shown by
the 132 tree, 147 shrub and 53 ground cover species found in Austin, Texas
(Frankie & Ehler 1978). In the area of Berkeley, California only 10 tree
species constitute the native tree flora, but there are 123 total tree
species (Frankie & Ehler 1978, Olkowski 1974), and almost 300 species on
the Berkeley campus of the University of California (Cockrell & Warnke
1976). Public concern over chemical pollutants has provided
incentives for the initiation of biological control in cities and towns
(Dahlsten et al. 1985). Typically, most successful biological control in
metropolitan areas is not well documented, but there is a strong desire among
researchers to gather critical data in some modern projects, e.g., the
biological control of the elm leaf beetle, Xantherogaleruca luteola
(Müller) with the egg parasitoid, Tetrastichus
gallerucae (Fonscolmbe)
(Clair et al. 1987, 1988). Overall little attention has been given thus far
to classical biological control in metropolitan areas. A report by the
National Research Council (1980) lists 70 species of natural enemies released
against 15 pests with an establishment rate of 34.3%. Among these most
successful projects have been against Homoptera on perennial plants, which is
the pattern found in agriculture as well (Flanders 1986). However, Hagen et
al. (1971) emphasize that the importance of naturally occurring biological
control should not be underestimated in city and town environments. Shade tree pests may be the most fruitful
area for biological control in this environment. They state that with the
rapidly expanding concept of the urban forest, it may be possible to organize
larger programs and generate public support for biological control. The urban
forest is defined as trees and other vegetation growing in close association
with people (Kielbaso & Kennedy 1983). Kielbaso & Kennedy (1983) estimated
that the amount of money spent on tree care programs in the United States is
substantial, and in 1980 amounted to US$2.19 per capita or $10.78 per tree.
The value of street trees in 1974 in the United States was valued at over $15
billion. Although many trees are planted in cities and towns, there has been
a tendency to develop monocultures and there is concern over the low
diversity of such forest trees (Kielbaso & Kennedy 1983). Olkowski et al (1978) and Dahlsten et al.
(1985) suggest
that the focus of developing biological control programs in urban forests has
been on defoliators and homopterans as six of the 10 most important
metropolitan area forest pests nationally are defoliators and the top two
pests are aphids and scales. Species
Targeted For Biological Control Principal species of arthropods that have
been investigated for biological control in cities and towns include
cockroaches, European earwig, Forficula
auricularia L., Cuban laurel
thrips, Gynaikothrips ficorum Marchal, acacia
psyllis, Acizzia uncatoides (Ferris &
Klyver), woolly whitefly, Aleurothrixus
floccosus (Maskell), oak
aphid, Myzocallis annulara (Harttig), urban tree
aphids, Eucallipterus tiliae L. & Tinocallis platani (Kaltenbach), pine needle scale, Chionaspis pinifoliae (Fitch), goldon oak scale, Asterodiaspis variolosa
(Ratzeburg), European fruit lecanium, Lecanium
corni (Bouche), green guava
mealybug, Chloropulvinaria psidii (Maskell), ice plant
scales, Pulvinariella mesembryanthemi (Vallot) & Pulvinaria delottoi Gill, Rhodesgrass mealybug, Antonina graminis
(Maskell), Comstock mealybug, Pseudococcus
comstocki (Kuwana), Lebbeck
mealybug, Nipaecoccus virdis (Maskell), hibiscus
mealybug, Maconellicoccus hirsutus (Green), elm leaf
beetle, Xanthogaleruca luteola (Müller), Japanese
beetle, Popillia japonica Newman, Nantucket pine
tip moth, Rhyacionia frustrana (Comstock), and holly
leafminer, Phytomyza ilicis Curtis. Please refer to
separate discussions of each of these arthropods under the section on Case
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