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Inventory and Survey Methods for Nonindigenous Plant Species (PDF)

Inventory and Survey Methods for Nonindigenous Plant Species (PDF)

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Chapter 4Digital Aerial Sketch-Mapping <strong>for</strong> EarlyDetection <strong>and</strong> MappingJason W. Karl <strong>and</strong> Mark PorterIntroductionAn ideal technique <strong>for</strong> conducting cost-effective <strong>and</strong>timely nonindigenous species (NIS) inventories/surveysin large, rugged l<strong>and</strong>scapes would allow detectionof multiple species at a time, would not be overlysensitive to environmental conditions, <strong>and</strong> could bereadily per<strong>for</strong>med by most experienced weed managerswithout extensive training. Digital aerial sketch-mapping(DASM) was pioneered by the USDA Forest Serviceto detect infestations of <strong>for</strong>est insects <strong>and</strong> pathogens(Morris 2001). Using DASM, a trained observer inan aircraft draws locations of infected st<strong>and</strong>s on atouch-sensitive, digital, moving-map computer display(McConnell et al. 2000), downloads the in<strong>for</strong>mationimmediately upon l<strong>and</strong>ing, <strong>and</strong> gives it to l<strong>and</strong> managers<strong>for</strong> treatment of infected areas. Here we proposea st<strong>and</strong>ard protocol <strong>for</strong> conducting DASM <strong>for</strong> nonindigenousplant species, review technical requirements <strong>for</strong>conducting DASM, <strong>and</strong> discuss practical considerationsaffecting the efficacy of DASM as an inventory/surveytechnique.<strong>Survey</strong> ProtocolProtocols <strong>for</strong> digital aerial sketch-mapping ofnonindigenous plant species (NIS) were derived fromthose used in mapping <strong>for</strong>est pathogens (Pywell et al. 2001;B.C. Ministry of Forests 2000) <strong>and</strong> surveying big gamepopulations (Unsworth et al. 1999), with modificationsspecific to plants. Since survey protocols aid researchers incontrolling <strong>for</strong> factors that could confound results, deviatingfrom the protocols can seriously affect the quality of datacollected. Once an inventory/survey protocol has been set,such factors as the number of observers, type of aircraftused, flight pattern, <strong>and</strong> survey subunits should not bechanged during successive flights (Unsworth et al. 1999).Simply put, DASM is a method <strong>for</strong> rapidly identifying <strong>and</strong>recording NIS infestations over large areas. Hence, DASMcan be employed within the context of either a full inventoryor a (biased or unbiased) survey. Due to flight costs,however, DASM is most commonly used in a biased surveyapproach where areas with a high likelihood of target NISare prioritized <strong>for</strong> searching, <strong>and</strong> lower priority areas areeither not searched or are searched with less ef<strong>for</strong>t.Selecting Targets <strong>and</strong> Timing the<strong>Inventory</strong>/<strong>Survey</strong>Flights should be designed around one or a few NIS toaid delineation of survey areas <strong>and</strong> timing. It is importantto underst<strong>and</strong> the life history <strong>and</strong> habitat associations oftarget NIS so that the detection reliability can be judged <strong>and</strong>the appropriate time of year <strong>for</strong> conducting surveys can beidentified.Aerial mapping should be timed to coincide with thephenological stage of the target species that is most visible tothe human observer. Many plants have certain phenologicalstages that are more distinct than others (see Lass <strong>and</strong>Callihan 1997), while other species may be difficult to detectregardless of their growth stage. Likewise, the minimumpatch size (i.e., survey resolution) that can be reliably identifiedby observers may also vary by species, although it canbe assumed that smaller patches <strong>and</strong> individual plants willbe more difficult to detect than larger patches. Almost anyplant species or any size patch is detectable if the observercan get close enough to it. However, the closer to the ground<strong>and</strong> slower the flight required to identify target species(i.e., to obtain finer resolution), the less cost efficient DASMsurveys become because less area per unit time is covered.One advantage of DASM over other techniques <strong>for</strong>covering large areas is that the observer is able to detectoccurrences of nontarget NIS over the course of the survey.It is important, however, to recognize that detections ofnontarget NIS during DASM may not be reliable indicatorsof their actual distribution within the study area <strong>for</strong> severalreasons. First, detection rates of NIS patches may decreasewith patch size (i.e., it is harder to see small patches than tosee large ones). Second, flights designed around maximumvisibility of one target NIS may not be optimal <strong>for</strong> nontargetspecies. In a trial DASM flight <strong>for</strong> hoary cress (Cardariadraba) conducted in Hells Canyon, Idaho, on May 17, 2004,we also detected 26 patches of Dalmatian toadflax (Linariadalmatica). A subsequent flight over the same area targetingDalmatian toadflax in full bloom on June 14, 2004, found a350% increase of Dalmatian toadflax (91 patches) detected.Despite the potential limitations of mapping nontarget NIS,such incidental observations can be quite useful <strong>and</strong> shouldbe recorded when observed.SubunitsA DASM inventory/survey area may be divided intosubunits, making it easier to track progress during the flight,quantify effective area sampled, <strong>and</strong> estimate confidenceintervals of detection rates <strong>and</strong> population sizes. Properlydefined subunits help focus the sampling <strong>and</strong> increase itsefficiency. Subunits can be any size, but Unsworth et al.33<strong>Inventory</strong> <strong>and</strong> <strong>Survey</strong> <strong>Methods</strong> <strong>for</strong> <strong>Nonindigenous</strong> <strong>Plant</strong> <strong>Species</strong>

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