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Final Comprehensive Conservation Plan - U.S. Fish and Wildlife ...

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Hakalau Forest National <strong>Wildlife</strong> Refuge<br />

<strong>Comprehensive</strong> <strong>Conservation</strong> <strong>Plan</strong><br />

purpose(s), Refuge System resources of concern (Federally listed species, migratory birds, selected<br />

marine mammals, <strong>and</strong> interjurisdictional fish), <strong>and</strong> native species for maintaining/restoring BIDEH.<br />

The next priority would be treating established pests that appear in one or more previously uninfested<br />

areas. Moody <strong>and</strong> Mack (1988) demonstrated through modeling that small, new outbreaks of<br />

invasive plants eventually would infest an area larger than the established, source population. They<br />

also found that control efforts focusing on the large, main infestation rather than the new, small<br />

satellites reduced the chances of overall success. The lowest priority would be treating large<br />

infestations (sometimes monotypic st<strong>and</strong>s) of well established pests. In this case, initial efforts<br />

would focus upon containment of the perimeter followed by work to control/eradicate the established<br />

infested area. If containment <strong>and</strong>/or control of a large infestation is not effective, then efforts would<br />

focus upon halting pest reproduction or managing source populations. Maxwell et al. (2009) found<br />

treating fewer populations that are sources represents an effective long-term strategy to reduce of<br />

total number of invasive populations <strong>and</strong> decreasing meta population growth rates.<br />

Although state listed noxious weeds would always be of high priority for management, other pest<br />

species known to cause substantial ecological impact would also be considered. For example,<br />

cheatgrass may not be listed by a state as noxious, but it can greatly alter fire regimes in shrub steppe<br />

habitats resulting in large monotypic st<strong>and</strong>s that displace native bunch grasses, forbs, <strong>and</strong> shrubs.<br />

Pest control would likely require a multi-year commitment from the refuge staff. Essential to the<br />

long-term success of pest management would be pre- <strong>and</strong> post-treatment monitoring, assessment of<br />

the successes <strong>and</strong> failures of treatments, <strong>and</strong> development of new approaches when proposed<br />

methods do not achieve desired outcomes.<br />

5.0 Best Management Practices (BMPs)<br />

The BMPs can minimize or eliminate possible effects associated with pesticide usage to non-target<br />

species <strong>and</strong>/or sensitive habitats as well as degradation of water quality from drift, surface runoff, or<br />

leaching. Based upon the Department of Interior Pesticide Use Policy (517 DM 1) <strong>and</strong> the Service<br />

Pest Management Policy <strong>and</strong> Responsibilities (30 AM 12), the use of applicable BMPs (where<br />

feasible) also would likely ensure that pesticide uses may not adversely affect federally listed species<br />

<strong>and</strong>/or their critical habitats through determinations made using the process described in 50 CFR part<br />

402.<br />

The following are BMPs pertaining to mixing/h<strong>and</strong>ling <strong>and</strong> applying pesticides for all ground-based<br />

treatments of pesticides, which would be considered <strong>and</strong> utilized, where feasible, based upon target-<br />

<strong>and</strong> site-specific factors <strong>and</strong> time-specific environmental conditions. Although not listed below, the<br />

most important BMP to eliminate/reduce potential impacts to non-target resources would be an IPM<br />

approach to prevent, control, eradicate, <strong>and</strong> contain pests.<br />

5.1 Pesticide H<strong>and</strong>ling <strong>and</strong> Mixing<br />

• As a precaution against spilling, spray tanks would not be left unattended during filling.<br />

• All pesticide containers would be triple rinsed <strong>and</strong> the rinsate would be used as water in the<br />

sprayer tank <strong>and</strong> applied to treatment areas.<br />

• All pesticide spray equipment would be properly cleaned. Where possible, rinsate would be used<br />

as part of the makeup water in the sprayer tank <strong>and</strong> applied to treatment areas.<br />

G-10 Appendix G. Integrated Pest Management

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