Forest Stewardship Councilsions drawn may cont<strong>in</strong>ue <strong>to</strong> be applicable <strong>to</strong> that group of sites dur<strong>in</strong>g the proposed period ofoperations, unless there are significant changes <strong>in</strong> the prevail<strong>in</strong>g conditions, for example <strong>in</strong>site type, location, nature of <strong>pest</strong> <strong>in</strong>festation, control technology, climate etc.The decision framework comprises three ma<strong>in</strong> steps.1) Identify <strong>and</strong> quantify the problemThe actual or potential problem must be identified <strong>and</strong> quantified, <strong>to</strong> allow a prediction <strong>to</strong> bemade of the likely consequences if the problem is not addressed.Without an underst<strong>and</strong><strong>in</strong>g of what the current or potential future causal agent is, it is impossible<strong>to</strong> judge what further action is required. An assessment of the nature of the <strong>pest</strong>, <strong>weed</strong> or<strong>disease</strong> problem, based upon its life cycle <strong>and</strong> role with<strong>in</strong> the natural ecosystem, is the bestway <strong>to</strong> judge likely current <strong>and</strong> future impacts. Correct identification therefore consists of underst<strong>and</strong><strong>in</strong>gnot only what the causal agent is, but also its population density <strong>and</strong> biology, lifecycle <strong>and</strong> likely impacts.Once likely impacts are determ<strong>in</strong>ed, decisions can be made on whether any further actionneeds <strong>to</strong> be taken, or on the economic <strong>and</strong> environmental thresholds which might trigger theneed <strong>to</strong> take action. For example, it may not be necessary <strong>to</strong> <strong>in</strong>itiate control measures until aproblem species exceeds a particular density threshold. Ongo<strong>in</strong>g moni<strong>to</strong>r<strong>in</strong>g of key <strong>pest</strong>s,<strong>disease</strong>s <strong>and</strong> <strong>weed</strong>s is therefore likely <strong>to</strong> be required <strong>in</strong> order for judgements <strong>to</strong> be made onwhen key thresholds for tak<strong>in</strong>g action have been reached.A good underst<strong>and</strong><strong>in</strong>g of the causal agent is also key <strong>to</strong> determ<strong>in</strong><strong>in</strong>g the range <strong>and</strong> comb<strong>in</strong>ationof options that might potentially be used for its mitigation or control. For example, an underst<strong>and</strong><strong>in</strong>gof an <strong>in</strong>sect species life cycle can be vital <strong>in</strong> identify<strong>in</strong>g the optimum tim<strong>in</strong>g forcontrol measures.Often the cause of ill health of trees is not obvious, or may be a result of a number of <strong>in</strong>terrelatedfac<strong>to</strong>rs. Therefore when deal<strong>in</strong>g with new or unfamiliar situations, it is advisable, if practicable,<strong>to</strong> obta<strong>in</strong> specialist advice before plann<strong>in</strong>g any <strong>management</strong> operations. Particulardifficulties may arise if the problem is a new <strong>in</strong>cursion <strong>to</strong> a region or country, <strong>and</strong> contact withspecialists from the place of orig<strong>in</strong> of the <strong>in</strong>vad<strong>in</strong>g species should form part of the problemscop<strong>in</strong>g exercise. However, it may not always be practical <strong>to</strong> engage <strong>in</strong> long term studies of aparticular <strong>pest</strong>, <strong>weed</strong> or <strong>disease</strong> problem before decid<strong>in</strong>g on the need for action. Managersshould therefore endeavour <strong>to</strong> make use of the best available exist<strong>in</strong>g knowledge, be thatthrough reference <strong>to</strong> published <strong>in</strong>formation, or contact with specialists such as researchers orother forest managers with relevant experience of similar situations, when plann<strong>in</strong>g managemen<strong>to</strong>perations.10 of 19® <strong>FSC</strong>, A.C. All rights reserved. <strong>FSC</strong>-SECR-0002 / Cover pho<strong>to</strong> credits: Ma<strong>in</strong> pho<strong>to</strong> © <strong>FSC</strong> / Juan Carlos Reyes; small pho<strong>to</strong>s left <strong>to</strong> right © Anders Hagman, © Milan Reska, © Juan Carlos Reyes, © Erik Goethals
IPM <strong>Guide</strong>With familiar problems <strong>and</strong> situations, once the <strong>pest</strong>, <strong>disease</strong> or <strong>weed</strong> is identified, it may besufficient <strong>to</strong> refer <strong>to</strong> exist<strong>in</strong>g guidance or his<strong>to</strong>ric <strong>management</strong> records <strong>to</strong> evaluate the likelyfuture consequences for the forest if no further action is taken.2) Consider the control options(i) Take no actionIn many cases, particularly where <strong>in</strong>sect <strong>pest</strong> <strong>and</strong> fungal <strong>disease</strong>s are concerned, the bestapproach may be <strong>to</strong> make a conscious <strong>and</strong> <strong>in</strong>formed decision <strong>to</strong> take no further action otherthan moni<strong>to</strong>r<strong>in</strong>g the situation. This may be the case when there are no effective control measures,or when the economic cost or environmental or social impacts of such control measuresoutweigh the risk <strong>to</strong> the forest from tak<strong>in</strong>g no action, or where critical thresholds have not beenexceeded. However, past experience may dictate that some form of <strong>management</strong> <strong>in</strong>put is essential<strong>to</strong> ma<strong>in</strong>ta<strong>in</strong> adequate growth <strong>and</strong> survival of trees, as is often the case when deal<strong>in</strong>gwith tree regeneration.(ii) Avoid the problemGiven a good underst<strong>and</strong><strong>in</strong>g of the nature of the <strong>pest</strong>, <strong>disease</strong> or <strong>weed</strong> agent, it may be possible<strong>to</strong> take action <strong>to</strong> avoid the current problem, or <strong>to</strong> prevent a potential problem occurr<strong>in</strong>g <strong>in</strong>the future.Such an approach may be far cheaper, <strong>and</strong> <strong>in</strong>volve fewer potentially damag<strong>in</strong>g impacts on theenvironment <strong>and</strong> <strong>in</strong>digenous populations than tak<strong>in</strong>g remedial action.Examples of strategies for avoid<strong>in</strong>g the problem might be <strong>to</strong> prevent the import or spread ofalien <strong>in</strong>vasive species, ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g healthy <strong>and</strong> vigorous st<strong>and</strong>s through good silviculturalpractice, select<strong>in</strong>g suitable tree species well matched <strong>to</strong> the site <strong>and</strong> capable of adaptation <strong>to</strong>future climate change, the use of resistant varieties, genotypes <strong>and</strong> species, ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g adequatetree nutrition, <strong>and</strong> the adoption of alternative silvicultural systems. Further region specificexamples are given <strong>in</strong> the l<strong>in</strong>ks provided from the ‘examples of strategies <strong>in</strong> practice’ section.(iii) Take remedial actionIf it is not practical <strong>to</strong> take no action or avoid the problem, it may be necessary <strong>to</strong> considerremedial control measures. All remedial actions carry the risk of potential non target impacts.For example, mechanised <strong>weed</strong> cutt<strong>in</strong>g can lead <strong>to</strong> soil compaction <strong>and</strong> petrochemical pollution,<strong>and</strong> herbicides can kill non target plants <strong>and</strong> cause wider pollution if misused. Managersmust therefore consider the potential negative impacts of all c<strong>and</strong>idate control measures, <strong>and</strong>11 of 19