Rep o rt of th e tw en - Rotterdam Convention
Rep o rt of th e tw en - Rotterdam Convention
Rep o rt of th e tw en - Rotterdam Convention
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Trap d<strong>en</strong>sity<br />
Trap d<strong>en</strong>sity is critical for fruit fly surveys and will be dep<strong>en</strong>dant on <strong>th</strong>e target fruit fly species,<br />
trap effici<strong>en</strong>cy and biotic and abiotic factors. D<strong>en</strong>sity may change dep<strong>en</strong>ding on <strong>th</strong>e programme<br />
phase, wi<strong>th</strong> possibly differ<strong>en</strong>t d<strong>en</strong>sities being required during <strong>th</strong>e establishm<strong>en</strong>t and maint<strong>en</strong>ance<br />
phases <strong>of</strong> <strong>th</strong>e FF-PFA. Trap d<strong>en</strong>sity will also be dep<strong>en</strong>dant on host occurr<strong>en</strong>ce from production to<br />
marginal areas and <strong>th</strong>e risk associated wi<strong>th</strong> pot<strong>en</strong>tial points <strong>of</strong> <strong>en</strong>try.<br />
Trap deploym<strong>en</strong>t<br />
In FF-PFA programmes an ext<strong>en</strong>sive trapping ne<strong>tw</strong>ork should be deployed over areas where<br />
host plants are found. The trapping ne<strong>tw</strong>ork layout will dep<strong>en</strong>d on <strong>th</strong>e characteristics <strong>of</strong> <strong>th</strong>e area,<br />
host distribution and biology <strong>of</strong> <strong>th</strong>e fruit fly <strong>of</strong> concern. One <strong>of</strong> <strong>th</strong>e most impo<strong>rt</strong>ant features <strong>of</strong> trap<br />
placem<strong>en</strong>t is selecting a proper trap location and trap site wi<strong>th</strong>in <strong>th</strong>e selected host tree. If low growing<br />
host plants (strawberries, cucurbits etc.) are to be monitored or <strong>th</strong>e availability <strong>of</strong> suitable host trees<br />
is limited, traps should be placed as close as possible to <strong>th</strong>e canopies <strong>of</strong> non-host shade trees or an<br />
a<strong>rt</strong>ificial equival<strong>en</strong>t, 1 – 2 metres above <strong>th</strong>e ground.<br />
Traps should not be hung below <strong>th</strong>e foliage canopy <strong>of</strong> host trees, and should be a minimum<br />
<strong>of</strong> 1 metre above <strong>th</strong>e ground. If more <strong>th</strong>an one type <strong>of</strong> trap is deployed at a trapping site (e.g. <strong>tw</strong>o<br />
differ<strong>en</strong>t lure traps), <strong>th</strong>e traps should be separated by a minimum <strong>of</strong> 3 metres and should not be<br />
deployed in <strong>th</strong>e same host tree.<br />
Geographic positioning systems (GPS) and global information systems (GIS) are useful tools<br />
for managem<strong>en</strong>t <strong>of</strong> a trapping ne<strong>tw</strong>ork.<br />
Preferred host(s) and fruit maturity<br />
Trap location should take into consideration <strong>th</strong>e pres<strong>en</strong>ce <strong>of</strong> <strong>th</strong>e preferred hosts <strong>of</strong> <strong>th</strong>e target<br />
species. As <strong>th</strong>e pest is associated wi<strong>th</strong> mature fruit, <strong>th</strong>e location <strong>of</strong> traps should follow <strong>th</strong>e sequ<strong>en</strong>ce<br />
<strong>of</strong> fruit maturity in host plants. Consideration should be giv<strong>en</strong> to commercial managem<strong>en</strong>t practices<br />
in <strong>th</strong>e area where host trees are selected. For example, <strong>th</strong>e regular application <strong>of</strong> insecticides<br />
(and/or fungicides) to selected host trees may have a false-negative effect on <strong>th</strong>e trapping programme.<br />
Trap servicing<br />
The frequ<strong>en</strong>cy <strong>of</strong> trap servicing during <strong>th</strong>e period <strong>of</strong> trapping will be dep<strong>en</strong>d<strong>en</strong>t on:<br />
• attractant persist<strong>en</strong>cy (i.e. longevity <strong>of</strong> <strong>th</strong>e bait)<br />
• <strong>th</strong>e ret<strong>en</strong>tion system if it affects <strong>th</strong>e quality <strong>of</strong> specim<strong>en</strong>s<br />
• rate <strong>of</strong> catch<br />
• season <strong>of</strong> fly activity<br />
• <strong>en</strong>vironm<strong>en</strong>tal conditions.<br />
It is impo<strong>rt</strong>ant <strong>th</strong>at lure material does not contaminate <strong>th</strong>e external surface <strong>of</strong> <strong>th</strong>e trap, nearby<br />
soil or plant material. It is equally impo<strong>rt</strong>ant to <strong>en</strong>sure <strong>th</strong>at <strong>th</strong>ere is no cross-contamination be<strong>tw</strong>e<strong>en</strong><br />
lure types, or be<strong>tw</strong>e<strong>en</strong> lures and o<strong>th</strong>er chemicals.<br />
Trap replacem<strong>en</strong>t<br />
Traps have a definite working life, and <strong>th</strong>e replacem<strong>en</strong>t <strong>of</strong> traps should be unde<strong>rt</strong>ak<strong>en</strong><br />
periodically based on <strong>th</strong>e expected longevity <strong>of</strong> <strong>th</strong>e trap in <strong>th</strong>e pa<strong>rt</strong>icular <strong>en</strong>vironm<strong>en</strong>t. The condition<br />
<strong>of</strong> each trap should also be examined during trap servicing and inspection activities, and where<br />
applicable (e.g. signs <strong>of</strong> deterioration), traps should be replaced.<br />
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