| Crop Damage by Wild Animalssection i
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| | nippon population in eastern Hokkaido,
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| general discussions
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| | Japan, increased rapidly during 1990-1998
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| G.M. Wani
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| | . This increase appeared to have halted
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| Ph.D ; D.V.M (Germany)
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| | in 1999-2000, probably due to increased
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| FN ISSGAPU, FN DAAD
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| | hunting and nuisance control. The period
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| Director Extension Education / SAMETI
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| | of rapid increase was associated with a
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| Sher-e-Kashmir University of Agricultural
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| | disproportionately rapid increase in
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| Sciences and Technology of Kashmir
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| | compensation paid for deer damage to
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| Shalimar, Srinagar, 191121
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| | crops. We studied changes in diet during
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| Â
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| | 1990-2000, as reflected by stable isotope
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| Â
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| | ratios of C and N in tooth collagen. We
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| Â
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| | hypothesized that isotope ratios would
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| A brief global review to asses the damage
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| | demonstrate dietary shifts related to
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| caused to cultivated crops by wild
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| | population levels and/or time, and that
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| animals around the world. The review was
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| | shifts in isotope ratios would be
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| attempted in response to a recommendation
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| | consistent with increasing individualÂ
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| of ICAR Regional Committee No.1 held in
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| | consumption of pasture grasses at higher
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| Oct, 2007 at Solan, H.p. presided over by
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| | population levels, delta 13C isotope
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| Hon'ble Director General, ICAR Dr.
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| | ratios of tooth collagen in 3 year-old
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| Mangala Rai inauguration was chaired by
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| | sika indicated a diet dominated by C3
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| Hon'ble Agriculture Minister J&K, Jenab
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| | plants throughout the period, and that
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| Ab. Aziz Zargar.
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| | forage species other than pasture grasses
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | and dwarf bamboo Sasa nipponica ( the
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | main crop and woodland understory
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | plants, respectively) were important
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| Author
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| | elements. There was a significant decline
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| Â
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| | in the delta 13C isotope ratio duringÂ
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | 1990-2000 in both males and females,
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | delta 15N values showed no trend with
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| Â
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| | time for males, but increased over time
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| Â
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| | in females. Indices of population
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| Â
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| | (Sightings per Unit Effort, SPUE) were
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| Published by:Â Director State
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| | negatively correlated with female delta
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| Agricultural Management and Extension
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| | 13C, and positively correlated with
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| Training Institute of Kashmir (SAMETI-K)
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| | female delta 15N, values indicating a
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| , SKUAST-K , Shalimar , Post Box: 461,
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| | shift in diet over the period ,
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| G.P.O, Srinagar.
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| | especially among females. This shift may
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| Â
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| | be related to population and/or offtake
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| Â
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| | levels, in particular the rapid
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | increase in female offtake for nuisance
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| Publication No: SAMETI/Pub/3/1000
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| | control and hunting during the period.
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| January, 2008
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| | The data are consistent with a relative
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| Â
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| | increase in pasture grass consumption per
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| Â
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| | individual at higher population levels,
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| Â
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| | however, other explanations of the data
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| P.O.Box: 461, GPO, Srinagar, E.Mail: Â Â
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| | are equally plausible. Possible dietary
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| Â Â Â Â Â Â Â Phone:Â Â Â Â Â Â
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| | changes, and other factors, influencing
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| 0194-2461317,0194-2463460,0194-2463459Â
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| | the observed shift in isotope ratios are
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| Â Â Â Â Â Â Â Â Â Cell: Â Â Â Â Â Â Â
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| | discussed. Although statistically
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| 09419095342Â ;
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| | significant, the magnitude of dietary
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| Residence:0194-2431508,2435741
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| | shifts nevertheless appeared small, and
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| Â
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| | did not provide evidence which would
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| Â
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| | justify modifying the current policy, of
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| Â
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| | limiting crop damage through managed
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| Introduction:
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| | population reduction to about 25% of peak
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| Â
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| | levels( Halley et al 2006).
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| Â Â Â Â Â Â Wild animal-human conflicts
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| | Â
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| have started since beginning of human era
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| | 12. White-tailed deer damages
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| from Adam and Eve. This conflict of
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| | Â Â Â Â Â Â Â Â Â White-tailed deer
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| wilderness made man to hide in caves and
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| | (Odocoileus virginianus) may cause more
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| he was called as "Cave man". Slowly, with
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| | damage than any other species of
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| his advancement it is he who invented Axe
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| | wildlife. These damages include crop
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| and other weapon in stone and iron ages
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| | loss, automobile and aviation collisions,
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| to frighten the wild animals, initially.
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| | disease transmission, environmental
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| Later on he hunted them to save himself.
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| | degradation, and destruction of
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| This feeling of uncertainty and fear of
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| | ornamental plantings. One practical
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| wild animals and wilderness reduced with
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| | method of controlling deer damage is the
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| the invention of fire. He made sharp
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| | use of exclusionary fences. The
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| weapons of bones and iron. These initial
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| | relatively high cost of labor and
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| weapons were the beginning of this
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| | materials required to build effective
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| conflict, Animal human conflict.
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| | fences has limited most applications to
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| Thirty thousand years ago, the human
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| | the protection of orchards, vegetable
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| population rose to 6 million. They were
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| | farms, other high -value resources, and
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| still hunters. With the invention of
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| | mitigation of human health and safety
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| fire, he set fire a vast majority of
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| | risks. Improvements in fence technology
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| sanctuaries, which scared wild life and
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| | resulting in less expensive, yet
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| they migrated from his neighborhood. Many
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| | effective fence have expanded the use of
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| forests, hills and difficult terrains
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| | fence to manage damage caused by deer.
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| were still beyond the reach of man three
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| | Fence typically installed to manage
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| thousand years before, although human
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| | white-tailed deer damage include wire or
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| population has increased to 60 million.
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| | plastic mesh, electrified high-tensile
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| Man has already started primitive
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| | steel wire, and electrified polytape or
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| agriculture. He had made his terrains and
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| | polyrope fence. They reviewed the
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| wild life scared by him left his close
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| | scientific literature on fencing to
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| habitats and searched for fresh abodes.
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| | determine which fence designs would be
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| Man by now had lust for fur, horns,
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| | the most effective for excluding deer in
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| ornaments and other forest resources. He
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| | a variety of situations (VerCauteren et
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| invented many means to frighten whole
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| | al 2006).
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| wild life. He became a "Danger "not only
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| | Â Â Â Â Â Â Â Â Â The installation of
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| for wild animals but for his own species,
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| | fences to protect agricultural products,
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| environment and eco-biodiversity.
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| | natural resources, or other areas from
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| Three hundred years ago he industrialized
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| | deer (Odocoileus spp.) can be expensive
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| crop production and produced enough food,
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| | and potential benefits of fencing are
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| for nearly 600 million people. This
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| | difficult to quantify. A rational method
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| continued and from 30 year now he is
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| | is needed to help evaluate whether
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| feeding 6000 million people. Today we
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| | fencing can be cost effective and which
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| have a global food security for 7.5
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| | fence designs will be optimal for
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| billion. Human food security gains
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| | particular applications. They describe an
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| resulted in reduction of all other wild
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| | interactive, dynamic simulation model
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| species, thus, the origin of wild- life-
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| | that conducts economic analyses and
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| human conflict is the lust of man for
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| | predicts economic benefit associated with
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| more food, more luxury or sometimes fun
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| | fences for crops relative to area and
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| for hunting or fur. This reduced wild
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| | perimeter of protected plot, value of
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| life reserves and now a open conflict
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| | crop, percentage of crop damaged by deer
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| came into existence.
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| | annually prior to fencing, efficacy of
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| Many man-wild life conflicts have been
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| | fence, and costs of fence materials and
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| reported from Gir forests of Gujarat,
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| | labor. Users of the model can easily
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| Rajaji National Park in UP and many other
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| | adjust these variables to fit their
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| states where forest lands became
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| | individual situations and needs. By
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| cultivable lands. Elephants, wild boars,
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| | running a series of simulations, model
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| monkeys, squirrels, deer , birds like
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| | users can answer questions related
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| crows, parakeets, wild dogs, jackals,
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| | directly to fence efficacy and
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| gaur, sambur, langure, fowls, pea cocks,
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| | cost-effectiveness (VerCauteren K et al
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| neilgai, Hippos, biats, blackbirds,
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| | 2006).
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| rodents, wild pigs, feral species,
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| | Â
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| primates, beetles, foxes, pigeons, feral
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| | 13. Corn damage by wild life
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| hogs and a variety of other species
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| | Â Â Â Â Â Â Â Â Â Corn damages in USA
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| damage crops. The carnivores even attack
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| | were estimated at 6.6 per hac due to wild
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| human too. These attacks are for search
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| | life. The white tailed deer was the wild
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| of food or their loss of habitat. Many
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| | animal responsible for loss. The average
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| such accidents came to be known in Jammu
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| | hacters owned by farmers were 125 out of
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| and Kashmir. The bear leopod and other
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| | which 55 hectares were sown corn.
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| wild animals are reducing in number.
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| | (Tzilkowsi et al 2002).
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| Their habitats used by human.
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| | Â
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| The human causalities are due to
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| | 14. Â Deer Damage
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| carnivorous species, but herbivores
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| | Â Â Â Â Â Â Â Â Â Deer (Odocoileus spp.)
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| inflict economic and human losses too.
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| | can cause substantial damage to
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| The crop damages by wild life has been
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| | agricultural crops, resulting in economic
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| the new threat to agricultural
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| | losses for producers. They developed a
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| productivity throughout the world. This
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| | deer activated bio-acoustic frightening
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| also concerns us in Asia and India. This
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| | device to reduce white-tailed deer (O,
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| review is aimed to find out:
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| | virginianus) damage in agricultural
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| 1.      Extent of damage to crops.
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| | fields. The device considered of an
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| 2.      Nature of crop damage
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| | infrared detection system that activated
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| 3.      Ways and means to prevent
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| | an audio component which broadcast
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| these losses.
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| | recorded distress and alarm calls of
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| 4.      A strategic planning to
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| | deer. They tested the device against
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| drive a line between wildlife
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| | unprotected controls in cornfields during
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| conservation and farm economics
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| | the silking-tasseling stage of growth in
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| especially in India.
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| | July 2001. The device was not effective
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| Â
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| | in reducing damage: track-count indices
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| Executive Abstracts and Strategic
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| | (F1,4=0.02), corn yield
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| elementaries: [EASE]
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| | (F1,9=1.27,P=0.289), and estimated damage
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| 1.    Importance
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| | levels (F1,10=0.87, P=0.374) did not
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | differ between experimental and control
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| Species causing crop damages ranges from
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| | fields. The size (F2,26=1,00,P=0.380),
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| elephant's wild birds, monkeys,
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| | location (F2,25=0.39,P=0.684), and
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| squirrels, deer, parakeet, wild dogs,
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| | percent overlap (F2,25=0.20,P=0.818) of
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| foxes, deer and many others like Neilgai.
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| | use-areas of radiomarked female deer did
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| On an average this damage to crops by
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| | not differ between during and after
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| wild animals amounts to U$ 961 per
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| | treatment periods. They concluded that
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| hectare. It is much more than an Indian
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| | the deer-activated bio-acoustic device
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| Farmer earns from a hacter annually.
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| | was not effective in protecting
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| Therefore, by these estimates, the
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| | cornfields in this study; however, the
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| damages are spectacular and economically
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| | device may be more effective in small
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| important.
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| | areas such as gardens or for high value
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| 2.      Human Elephant conflicts
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| | crops that do not grow tall enough to
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| (HEC):
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| | offer protective cover (Gilsdorf et al
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| Â Â Â Â Â Â Â Â Â i) Economic Losses:
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| | 2004).
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| Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â Â
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| | Â Â Â Â Â Â Â Â Â White -tailed deer
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| Among elephants crop raiding is common.
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| | (Odocoileus virginianus) cause millions
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| The crops near their home ranges are
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| | of dollars of damage to agricultural
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| damaged more. Elephants damaging crops
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| | crops annually . They tested the
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| had twice big ranges than those who did
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| | effectiveness of propane exploders and
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| not damage the crops. Thus, more
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| | Electronic Guards (Pocatello Supply
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| proximity of the crops near their ranges
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| | Depot, Pocatello, Id). For reducing deer
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| are prone to crops damages. Train
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| | damage in corn fields during the
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| accidents instigate elephants more to
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| | silking-tasseling stage of growth.
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| crop or human damages. Indonesia saw more
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| | Track-count indices (F2,7=0.70,P=0.532),
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| frequent raids of elephants on crops.
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| | corn yield (F2,6=0.14, P=0.873), and
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| Human elephant conflict (HEC) is frequent
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| | estimated damage levels (F2, 12=1,45
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| and poses serious challenges in Africa.
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| | P=0.272) did not differ between
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| Both male groups and family group attacks
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| | experimental and control fields. The size
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| have been observed. HEC losses in West
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| | (F2,11=0.08,P =0.924), LocationÂ
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| Bengal were worth 3.2 croses of Rupees.
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| | (F2,9=0.30, P=0.750), and percent overlap
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| This damage occurred in 3368sq
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| | (F2,9=0.46, P=0.644) of use -areas of
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| kms.radius. The numerical number of
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| | radiomarked female deer in the vicinity
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| elephants was 62 only. Assam observes
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| | of experimental fields did not differÂ
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| damages to the woodcutters by elephants
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| | among before, during and after 18 day
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| Asian wild Elephants raid and damage
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| | treatment periods. In a related study, we
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| crops in herds of 10-13 individuals or
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| | placed propane exploders in cornfields
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| big herds comprising 50-74 elephants. In
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| | within use-areas of 12 radiomarked female
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| Darjeeling district alone over an area of
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| | deer. The deer did not react appreciably
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| 200 kms. East to west, in last two
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| | to the devices; the size (F2, 17=0.08,
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| decades 277 houses were demolished by
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| | P=0.921), location (F2,22=1.37, P=0.275),
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| elephants, killing 66 people in 5
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| | and percent overlap (f2,10=0.47, P=0.636)
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| districts. As a result of this conflict
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| | of deer use areas did not differ among
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| 23 elephants lost their lives. In 2001,
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| | before, during, and after 14 day
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| economic loss of the order of US fifty
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| | treatment periods. They conclude that
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| thousand dollars was estimated to be
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| | propane exploders and Electronic Guards
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| inflicted by elephants. This scenario
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| | have limited potential for reducing deer
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| necessitates comprehensive measures to be
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| | damage to corn at the silking-tasseling
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| taken to lessen these damage. The review
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| | stage (Glisdorf et al 2004l.
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| of the measures, around the world suggest
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| | Â
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| following few studies to be undertaken
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| | Â Â Â Â Â Â Â Â Â A welfare measure for
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| and resultant measures to be applied to
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| | wildlife damage to Ontario (Canada) field
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| lessen these damages.ii)Â Â Â Â
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| | crop producers during the 1998 was. The
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| Mitigation of losses:
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| | welfare measure presented in this study
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| Â Â Â Â Â Â Â Â Â Methods developed and
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| | provides a more accurate picture of
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| used to mitigate crop damages by
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| | losses from wildlife damage to
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| elephants consisted of frightening of
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| | agricultural. Other damage estimates
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| animals by drum beating, firegracks or
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| | based on yield loss overstate the damage
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| even air gun fires. Guarding the crops by
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| | since benefits from wildlife are netted
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| fences or even using electric fencing or
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| | out. Results for the Ontario field crop
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| raising poles and wiring may be
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| | producers indicate that the magnitude of
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| effective. Chemical based deterrents, and
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| | the difference between the value of the
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| electric fencing have been found to
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| | yield loss and the welfare measure of
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| reduce crop damages. High voltage
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| | damage is approximately 50%. This
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| electric fencing using energizers in west
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| | difference indicates that most farmers
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| have prevented wild animals damaging crop
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| | were willing to tolerate the wildlife
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| but this preposition may not be
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| | damage they experienced (Heigh et al
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| applicable in areas where even
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| | 2001).
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| habitations do not have access to
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| | Â
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| electricity. However, this method may act
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| | 15. Grapevine damages
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| as a temporary boundary separating wild
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| | Â Â Â Â Â Â Â Â Â In field trials in
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| and domestic habitats. This could prevent
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| | 1999-2000 in Gundla Pochampally, Andhra
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| intrusions from sly vatic to domestic
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| | Pradesh, India , the incidence of damage
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| foci. Guarding fields, digging trenches,
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| | to green grapevines was studied. Visits
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| modifying cropping patterns have a
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| | to the vines by bats begain around 45
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| possibility of reducing man elephant
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| | minutes after sunset and foraging
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| conflicts or Human elephant conflicts. A
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| | continued until 1 hour before sunrise.
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| 30% open space between two habitats may
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| | Damage occurred to ripe fruit only, and
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| help to avoid HEC. This means a distance
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| | increased around harvesting time,
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| to be maintained between cropping fields
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| | percentage damage ranged from 0 to 100%
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| and elephant habitates. A proper
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| | (Bhargavi et al, 2001).
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| investigation on these lines is needed. A
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| | Â
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| grid based geographical information
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| | 16. Â Â Hippo damage
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| system (GIS) with a 25Km2 resolution may
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| | Â Â Â Â Â Â Â Â Â The introduction to
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| help to have cost effective data source
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| | the paper described the various
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| to analyze these situations. There is
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| | ecological effects known to result from
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| urgent need of identifying spatial
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| | grazing, movement along paths, and
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| predictors of HEC. On the basis of this
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| | wallowing by the common hippo.
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| study one can suggest or plan mitigation
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| | Hippopotamus amphibious. The study
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| strategies, early warnings of attacks,
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| | reported was carried out at Kainji Lake
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| use of barriers and deterrents. The
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| | National Park., Nigeria, during  the dry
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| utility of the methods could be assessed
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| | season periods {of 1991 and 1992} . The
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| for land use and livelihood strategies to
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| | method adopted by Agnew, A.D.Q. (East
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| limit HEC.
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| | African Wildlife Journal (1966) 4, 38-46)
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| Â
| |
| | was used to assess hippo foraging
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| 3.      Dear-Nilgai Damages.
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| | footprints at three hippo pool sites. A
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| Â Â Â Â Â Â Â Â Â A survey of 2500 farms
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| | total of 32 footpaths were enumerated out
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| in UK revealed that 69% (n=192) cereal
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| | of which 18 were located at Kaii hippo
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| crops were damaged by deer. This damage
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| | pool site, while the frequency of
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| costed £500 per annum per farm. Damages
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| | utilization of paths was also higher for
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| varied with deer density. In USA too deer
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| | this site relative to those in other
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| damages comprised of crop loss, landscape
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| | area. The upstream-downstream trend in
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| damages, car accidents and property
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| | hippo occupancy of dry  season water
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| damages. Nilgai damages alongwith deer
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| | pools could expose the hippo to crop
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| damages are common in India too. Tree
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| | damage conflicts at the peripheral areas.
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| cover of Acacia in the area is generally
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| | Â
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| used as shelter by Nilgai. We have
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| | 17. Hygo-Japan-mammal crop damages
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| encountered huge crop damage in Mathura
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| | Â
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| (CIRG) and nearby area by Nilgai visits.
| |
| | Â Â Â Â Â Â Â Â Â Mammals inhabiting Â
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| Grazing and browsing of Nilgai inflict
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| | Hyogo consist of seven orders, 17
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| losses on farms. This is regarded as a
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| | families and about 40 species. Except for
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| mammalian crop threat by the farmers.
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| | Lagomorpha and Artiodactyla, the
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| This behaviour of their inflict ozone
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| | remaining five orders among them include
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| injury to the young sapling, so precious
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| | species which need some protection and
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| for the growth of trees in Indian
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| | they total about 55% of all species
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| semi-arid farms.
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| | excluding extinct, introduced and feral
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| Â
| |
| | species. Ecological information in Hyogo
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| Â Â Â Â Â Â Â Â Â Corn damages by deer
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| | prefecture has been accumulated in few
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| in USA amounts to 6.6.% per hectare. In
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| | protection-required species there is no
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| an area where a farmer owned 125 hectare
| |
| | recent information of spatial
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| on an average 55 hectares were used to
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| | distribution on Oriental water-shrew,
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| sow corn. There is a 6.6% loss of the
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| | Japanese noctule-bat and Japanese
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| product which is a huge economic loss.
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| | dormouse; and little information on
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| Similar damages by deer in Ontario,
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| | Japanese shrew, Japanese horse-shoe bat,
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| Canada, Portugal, Japan, South America
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| | Japanese large -footed bat. Schreiber's
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| and other parts of the world have been
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| | bent-winged bat, Japanese tube-nosed bat,
|
| reviewed. In Virginia too a study
| |
| | common parti-colored bat, Japanese
|
| involving 1506 agricultural producer
| |
| | squirrel, Japanese small flying-squirrel,
|
| farmers revealed 58% of them experiencing
| |
| | Japanese giant flying-squirrel, smith's
|
| deer damages. Ways and means to prevent
| |
| | vole harvest mouse and Japanese badger.
|
| such attacks on crops have been reviewed.
| |
| | Damage and population managements is also
|
| Most of the possible measures to be
| |
| | necessary in sika deer and Japanese wild
|
| adopted are similar to these described
| |
| | boar, to reduce their crop--damaging, and
|
| for elephants (HEC).
| |
| | comprehensive management in Japanese
|
| Â
| |
| | black bear, an endangered local
|
| 4.   Other Mammal and bird damages
| |
| | population, to prevent human-bear fatal
|
| Â
| |
| | accident. Habitat alteration due to human
|
| Â Â Â Â Â Â Â Â Â Monkey damages maize,
| |
| | activities, however, has affected the
|
| sweet potato and other crops. It is
| |
| | population sizes and spatial distribution
|
| suggested to reduce or change cropping
| |
| | of all these, mammals in Hyogo. Habitat
|
| pattern or alternating with
| |
| | management has priority over damage.
|
| non-agricultural activities near location
| |
| | Fundamental and applied scientific
|
| of monkey habitats. Various methods are
| |
| | studies and understanding of ecology and
|
| reviewed. Bat damage, Hygo crop damages
| |
| | wildlife management science needs
|
| in Japan, Grape wine damages by bats in
| |
| | promotion by citizens (Mitani M 2000).
|
| Andra Pradesh, India have been studied.
| |
| | Â
|
| Crop economic loss assessment has been
| |
| | 18. Monkey damage
|
| reviewed in these pages. Clover rather
| |
| | Â
|
| than grass can reduce wild mammal
| |
| | Â Â Â Â Â Â Â Â Â Forty-seven property
|
| damages. Alley cropping of black walnuts
| |
| | owners in Entebbe, Uganda were questioned
|
| helped to save soyabean and maize crop
| |
| | about vervet monkey activities on their
|
| damages. Pesticide damages wildlife and
| |
| | property. The objective was to
|
| minimize their attacks, enclosures and
| |
| | investigate the interactions between
|
| other electric fencing help to avoid such
| |
| | humans and vervet monkeys in an
|
| damage. Can one use harmful means to save
| |
| | agricultural area adjacent to a forest
|
| crops, need a suitable strategy to
| |
| | zone. Other studies have reported that
|
| preserve ecology and biodiversity. Both
| |
| | farms located within 300 m of a forested
|
| crops and wild animals need security and
| |
| | boundary probably incur the greatest risk
|
| conservation. A management strategy is
| |
| | of crop-raiding. Two other factors that
|
| needed to safeguard human and wildlife
| |
| | may influence susceptibility to vervet
|
| equally. Â A policy framework is
| |
| | crop-raiding were also examined: the
|
| envisaged.
| |
| | types of crops grown and the types of
|
| Â
| |
| | direct preventive measures used. The
|
| Â Â Â Â Â Â Â Â Â Blackbird crop damage
| |
| | effect of these two factors on vervet
|
| in USA amounts to 5-8 million dollars. A
| |
| | crop-raiding is not straight forward.
|
| considerable sum of crores of rupees have
| |
| | However, the distance a property is
|
| been estimated to be damages in the form
| |
| | located from the forest edge is an
|
| of crop, human and property losses by
| |
| | important factor influencing vervet crop
|
| wild animals, birds and other rodents in
| |
| | raiding. Surveyed  gardens 200 m from
|
| India. Many measures to reduce these
| |
| | the forest edge received significantly
|
| losses are needed and have been reviewed.
| |
| | less crop -raiding than farms locatedÂ
|
| Â
| |
| | 100 or 50m (P=0.040,< alpha=0.05). In
|
| Â
| |
| | this study, 8 out of 13 farmers (61.5%)
|
| Â
| |
| | said that maize, sweet potato, or both,
|
| Â
| |
| | were most likely to be damaged by the
|
| Â
| |
| | vervets. Other crops singled out by the
|
| Review
| |
| | farmers are receiving damage by the
|
| 1. Wild animals damaging crops
| |
| | vervets were bananas, mangoes, groundnuts
|
| To elephants wild boar, porcupine, rheus
| |
| | and yam. They suggest that the
|
| macaque (Macaca mulatta), hoary-bellied
| |
| | development of non-agriculturalÂ
|
| squirrel, barking deer (Muntiacus
| |
| | activities on land directly adjacent to
|
| muntjak), red-breasted parakeet
| |
| | forested areas may reduce vervet crop
|
| (Psittacula alexandri), and wild dog are
| |
| | -raiding by deterring vervets from
|
| wild animals damaging crops.
| |
| | traveling greater distances from the
|
| Methods developed and being used to
| |
| | forest edge due to increased obstacles or
|
| mitigate man-wildlife conflict include,
| |
| | risks  (Saj et al 2001).
|
| frightening the animals; guarding the
| |
| | Â
|
| crops; and using some sort of scarecrow
| |
| | 19. Bait damage
|
| and traps (Miah et al 2001).
| |
| | Â Â Â Â Â Â Â Â Â The longevity of zinc
|
| Accurate estimation of crop damage by
| |
| | phosphide (ZP) on whole wheat bait  was
|
| wildlife (raccoons, white-tailed deer,
| |
| | determined at the end of the "dry" and
|
| and coyotes) often requires
| |
| | "wet" seasons, Â is Western Australia..
|
| labour-intensive sampling procedure.
| |
| | While the total rainfall during the two
|
| Variable area transect (VAT) sampling has
| |
| | trials was 74 mm and 155mm, substantial
|
| been identified as a potential
| |
| | loss of ZP was recorded only after
|
| labour-saving alternative to quadrat
| |
| | significant rainfall events. Irrespective
|
| sampling ( Engerman et al 2002).
| |
| | of season, the loss of ZP from bait
|
| Â
| |
| | applied in bait stations was minimal. The
|
| 2. Wild life Human conflicts
| |
| | maximum recorded loss was 17% and this
|