2014
DOI: 10.3391/mbi.2014.5.3.03
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Estimating sampling effort for early detection of non-indigenous benthic species in the Toledo Harbor Region of Lake Erie

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Cited by 12 publications
(10 citation statements)
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“…Our META and MORPH datasets both identified most of the AIS species found by Ram, Banno, Gala, Gizicki, and Kashian (2014) (Clarke et al, 2017;Elbrecht & Leese, 2015;Zhou et al, 2013). Additionally, MORPH surveys often fail to sample and distinguish taxa due to low population numbers, crypsis, and/or capture method biases (Darling & Mahon, 2011).…”
Section: Application For Ais Detection and Monitoring (Hypothesis 3)supporting
confidence: 54%
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“…Our META and MORPH datasets both identified most of the AIS species found by Ram, Banno, Gala, Gizicki, and Kashian (2014) (Clarke et al, 2017;Elbrecht & Leese, 2015;Zhou et al, 2013). Additionally, MORPH surveys often fail to sample and distinguish taxa due to low population numbers, crypsis, and/or capture method biases (Darling & Mahon, 2011).…”
Section: Application For Ais Detection and Monitoring (Hypothesis 3)supporting
confidence: 54%
“…Our META and MORPH datasets both identified most of the AIS species found by Ram, Banno, Gala, Gizicki, and Kashian (2014) in their benthic sampling of the Maumee River and accompanying individual specimen barcoding. An exception was that our META missed the faucet snail B. tentaculata (here solely found at the mouth of the Maumee River by the OEPA), and neither MORPH nor META identified the chironomid Lipiniella sp.…”
Section: Discussionmentioning
confidence: 61%
“…The finding that the estimated number of samples to detect 95% of projected richness varied substantially between methods of resolving ambiguous taxa has implications for survey design and evaluation. For example, under the binational 2012 Great Lakes Water Quality Agreement, US and Canadian federal agencies are tasked with implementing monitoring programs for exotic aquatic species, and projected taxa richness (Chao1) is being used to estimate the sampling effort needed to detect taxa of a given rarity (which equates to a given level of establishment for exotic species), as well as develop more efficient monitoring programs (Hoffman et al, 2011;Ram et al, 2014). Given the sensitivity of estimated sampling effort to detect 95% of projected taxa, appropriate caution is warranted when determining how many additional samples are needed as part of a monitoring program.…”
Section: Possible Effect Of Study Area Characteristics and Survey Desmentioning
confidence: 99%
“…Accordingly, choices for resolving ambiguous taxa can impact nonparametric estimates of projected species richness (aka, asymptotic richness) that rely on the number of rare taxa encountered with a given sampling effort to estimate the total species pool of an area. Projected richness estimates are commonly used in prioritizing biodiversity conservation efforts (Desmet and Cowling 2004;Sambuichi and Haridasan 2007), and to assess sampling effort sufficiency (Schreiber and Brauns 2010;Ram et al, 2014). We recognize that these non-parametric estimates of projected taxa richness have been criticized because their precision and accuracy depend on both sampling effort (D'Alessandro and Fattorini 2002) and distribution patterns, especially rarity and spatial aggregation (Reese et al, 2014;Walther andMoore 2005, Chiarucci et al, 2003).…”
Section: Introductionmentioning
confidence: 99%
“…Thankfully, there seems to be no longer any debate amongst policy-makers and protection agencies that invasive species represent one of the greatest threats to biodiversity in aquatic ecosystems, with the ICAIS conference and its proceedings reflecting this. Many of the contributions dealt with detection (e.g., the use of vital stains to detect freshwater taxa [Adams et al 2014]; sampling effort [Ram et al 2014]; predictors for environmental suitability [Prescott et al 2014]; and environmental DNA techniques for Asian Carp [Wilson et al 2014]) and risk assessment (e.g., Champion et al's 2014 aquatic weed risk assessment; and Baier et al's 2014 biofilm assessment) acknowledging that the best way to 'manage' a biological invasion is to stop it happening in the first place. However, if an invader evades biosecurity protocols and mitigation (e.g., ballast water filtration issues [Briski et al 2014]; and methods to mitigate green crab impact [Best et al 2014]) and control measures fail (e.g., harvest incentives [Pasko and Goldberg 2014]; or the use of microbial biocides such as Zequanox [Meehan et al 2014]) and then starts to spread out and establish itself, it is here that the old fashioned niche concept perhaps comes into its own.…”
mentioning
confidence: 99%