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                     BIOLOGICAL
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| 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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