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In a recent Perspective, Gerth et al. (2011) expressed concern over how Wolbachia (Wolbachia pipientis Hertig) infections may affect the success of DNA barcoding efforts in bees. The potential and realized effects of endosymbiont-induced selective sweeps on host mitochondrial DNA diversity have been noted repeatedly – and rightly so – in the literature for some years. However, we are equally concerned with other misconceptions, including (a) presuming that a positive Wolbachia test indicates a stable infection, (b) presuming that Wolbachia-infected hosts cannot be identified with a single-locus barcode, and (c) inferring specific Wolbachia–mtDNA interactions based only on incomplete genotyping of Wolbachia strains. We address these issues in the context of the Gerth et al. (2011) survey of Wolbachia prevalence among the German bee fauna. We also clarify some of the context-dependent strengths and limitations of DNA barcoding when it is used as a research tool by taxonomists and ecologists.  相似文献   

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Garcia et al. (2011) recently discussed early human dispersals into the Iberian Peninsula, describing several putative lithic artifacts (Martínez et al., 2010) recovered from layer 7 of the Vallpara díssection (Madurell-Malapeira et al., 2010) in Terrassa (Vallès-Penedès Basin, Catalonia, Spain). According to the authors' opinion, such evidence (1) fills a gap in the chronology of early human occupation in Iberia, (2) indicates that these populations had primary and early access to carcasses, and (3) confirms that early human populations were equipped with advanced cultural traits enabling them to survive in unfavourable climatic conditions. We argue below that the record of human activity at Vallparadís (Martínez et al., 2010;Garcia et al., 2011) is doubtful and even that if confirmed, a chronological gap would remain (contra Garcia et al., 2011). Additional remarks on assertions by these authors on the Vallparadís geology, taphonomy and paleonvironment are also provided.  相似文献   

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《新西兰生态学杂志》2011,32(2):238-239
Walker et al. (2008) are critical of the methods used by ecologists and others with ?vested interests? to identify significant biodiversity values and provide for their protection under the Resource Management Act (1991) (RMA), particularly the use of the draft criteria proposed in Norton & Roper-Lindsay (2004). However, we believe that their criticism is flawed because of their failure to fully understand the context of the Norton?Roper-Lindsay criteria; unjustified presumptions they make about the roles of ecologists in assisting those applying for resource consents and administering the RMA; and a failure to take into account the current realities of native biodiversity conservation for those parts of New Zealand covered by the RMA. In this reply we address these issues and outline a way to move forwards in this debate.  相似文献   

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