Geology topics

Susan D. Jewell

Publications and source records attributed to Susan D. Jewell.

3 recordsLinked to original sources

USGS2023

Disinfection protocols for herpetofaunal pathogens

The spread of disease-causing pathogens is a major threat to amphibians and reptiles worldwide (Converse and Greene 2005; Picco et al. 2007; Picco and Collins 2008; St-Amour et al. 2008; O’Hanlon et al. 2018; Scheele et al. 2019). The World Organisation for Animal Health’s global list of notifiable animal diseases includes herpetofaunal diseases caused by infection with Ranavirus spp. (RV) and two chytrid fungi, Batrachochytrium dendrobatidis (Bd) and B. salamandrivorans (Bsal; WOAH 2023). Scientists began testing the efficacy of disinfection protocols even before human-assisted transmission of these pathogens was documented (Johnson et al. 2003; Johnson and Speare 2003; Brem et al. 2007; Bryan et al. 2009), and now guidance exists to determine the appropriate biosecurity measures as personal gear moves between habitats, construction equipment moves between project areas, and investigators handle multiple animals within a population (Phillot et al. 2010; Gray et al. 2017, 2018; Julian et al. 2020; Olson et al. 2021). People who are engaged in educational, recreational, commercial, or professional activities in wetlands and aquatic habitats play an important role in helping prevent the spread of pathogens and should know how and when to employ appropriate disinfecting procedures. In particular, working groups and regional chapters of Partners in Amphibian and Reptile Conservation (PARC) have developed a variety of educational materials on biosecurity and disinfection for a wide audience (e.g., PARC 2023). Herein, we provide the instructions for the disinfection of field equipment that were recently revised by the Emerging Disease Working Group of Northeast PARC (NEPARC 2022). The impetus for revision was to inform field personnel of the use of a stronger bleach concentration (ca. 10× stronger) that is needed for effectiveness against Bsal (Van Rooij et al. 2017). This is important for regions where Bsal is currently known to occur (e.g., central Europe) as well as regions where it is presumed absent but could arrive at any time (e.g., North America)

Herpetological Review↗

USGS2022

Three steps to minimize wildlife disease transmission via construction equipment

Aquatic wildlife can be harmed by viruses, bacteria, fungi, and parasites introduced into wetlands. These infectious pathogens can survive in mud, soil, vegetation, and other debris that collect on the bodies and crevices of drivable equipment. Construction and habitat restoration projects can accidentally transport pathogens from a contaminated aquatic habitat into a healthy one. These three steps can help minimize the spread of pathogens to amphibians, reptiles, and fishes. The information provided in this fact sheet has been extracted from the publication, "Minimizing the Spread of Herpetofaunal Pathogens in Aquatic Habitats by Decontaminating Construction Equipment " (http://northeastparc.org/wp-content/uploads/2021/01/Julian-2020-Decontamination-for-Herps-for-large-equipment.pdf)

Report↗

USGS2021

The unsung success of injurious wildlife listing under the Lacey Act

Previous papers discussing the effectiveness of injurious wildlife listings under 18 U.S.C. 42(a) of the Lacey Act have emphasized failures while ignoring the many successes. We looked at the 120-year history of injurious listing and then determined the effectiveness of the listings since the U.S. Fish and Wildlife Service (USFWS) gained the listing authority in 1940. We measured success by the effectiveness of listing relative to the stage of the invasion process – that is, whether or not a species was established at the time of listing, if it since established, and if it subsequently spread to other States. The USFWS started listing preemptively with its first rule in 1952 and has added the majority of species preemptively since then. We analyzed the 307 species that were listed for invasiveness (excluding species listed for other injurious reasons). Of those species, 288 (94%) were listed preemptively (before they became established). Although we acknowledge that other factors may play a role, we consider species that were listed before establishment and remained not established as “very effective” listings. All 288 remained not established – a 100% prevention rate when listed preemptively. Only 19 of the 307 species (6%) were listed after establishment, and they remain established. The listings are considered “effective” for the 4% that remained within the State(s) they were established in at listing and “ineffective” or “not applicable” for the 2% that spread to other States. The rationale for listing established species is explained herein. We conclude that injurious species listings can be effective at any stage, but prohibiting the importation into the United States of high-risk species prior to their introduction and establishment into U.S. environments is very effective in preventing invasions, and this success has heretofore been overlooked.

Management of Biological Invasions↗