5 results
Descriptive evaluation of antibody responses to severe acute respiratory coronavirus virus 2 (SARS-CoV-2) infection in plasma and gingival crevicular fluid in a nursing home cohort—Arkansas, June–August 2020
- Part of
- Nicole E. Brown, Amanda K. Lyons, Amy J. Schuh, Megan M. Stumpf, Jennifer L. Harcourt, Azaibi Tamin, Mohammad Ata Ur Rasheed, Lisa Mills, Sandra N. Lester, Natalie J. Thornburg, Kenny Nguyen, Veronica Costantini, Jan Vinjé, Jennifer Y. Huang, Sarah E. Gilbert, Paige Gable, Susan Bollinger, Sarah Sabour, Elizabeth Beshearse, Diya Surie, Caitlin Biedron, Christopher J. Gregory, Nakia S. Clemmons, Brett Whitaker, Melissa M. Coughlin, Kathryn A. Seely, Kelley Garner, Trent Gulley, Tafarra Haney, Atul Kothari, Naveen Patil, Alison Laufer Halpin, L. Clifford McDonald, Preeta K. Kutty, Allison C. Brown
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- Journal:
- Infection Control & Hospital Epidemiology / Volume 43 / Issue 11 / November 2022
- Published online by Cambridge University Press:
- 22 November 2021, pp. 1610-1617
- Print publication:
- November 2022
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Objective:
To characterize and compare severe acute respiratory coronavirus virus 2 (SARS-CoV-2)–specific immune responses in plasma and gingival crevicular fluid (GCF) from nursing home residents during and after natural infection.
Design:Prospective cohort.
Setting:Nursing home.
Participants:SARS-CoV-2–infected nursing home residents.
Methods:A convenience sample of 14 SARS-CoV-2–infected nursing home residents, enrolled 4–13 days after real-time reverse transcription polymerase chain reaction diagnosis, were followed for 42 days. After diagnosis, plasma SARS-CoV-2–specific pan-Immunoglobulin (Ig), IgG, IgA, IgM, and neutralizing antibodies were measured at 5 time points, and GCF SARS-CoV-2–specific IgG and IgA were measured at 4 time points.
Results:All participants demonstrated immune responses to SARS-CoV-2 infection. Among 12 phlebotomized participants, plasma was positive for pan-Ig and IgG in all 12 participants. Neutralizing antibodies were positive in 11 participants; IgM was positive in 10 participants, and IgA was positive in 9 participants. Among 14 participants with GCF specimens, GCF was positive for IgG in 13 participants and for IgA in 12 participants. Immunoglobulin responses in plasma and GCF had similar kinetics; median times to peak antibody response were similar across specimen types (4 weeks for IgG; 3 weeks for IgA). Participants with pan-Ig, IgG, and IgA detected in plasma and GCF IgG remained positive throughout this evaluation, 46–55 days after diagnosis. All participants were viral-culture negative by the first detection of antibodies.
Conclusions:Nursing home residents had detectable SARS-CoV-2 antibodies in plasma and GCF after infection. Kinetics of antibodies detected in GCF mirrored those from plasma. Noninvasive GCF may be useful for detecting and monitoring immunologic responses in populations unable or unwilling to be phlebotomized.
Transactional relations between caregiving stress, executive functioning, and problem behavior from early childhood to early adolescence
- Linda L. Lagasse, Elisabeth Conradt, Sarah L. Karalunas, Lynne M. Dansereau, Jonathan E. Butner, Seetha Shankaran, Henrietta Bada, Charles R. Bauer, Toni M. Whitaker, Barry M. Lester
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- Journal:
- Development and Psychopathology / Volume 28 / Issue 3 / August 2016
- Published online by Cambridge University Press:
- 18 July 2016, pp. 743-756
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Developmental psychopathologists face the difficult task of identifying the environmental conditions that may contribute to early childhood behavior problems. Highly stressed caregivers can exacerbate behavior problems, while children with behavior problems may make parenting more difficult and increase caregiver stress. Unknown is: (a) how these transactions originate, (b) whether they persist over time to contribute to the development of problem behavior and (c) what role resilience factors, such as child executive functioning, may play in mitigating the development of problem behavior. In the present study, transactional relations between caregiving stress, executive functioning, and behavior problems were examined in a sample of 1,388 children with prenatal drug exposures at three developmental time points: early childhood (birth to age 5), middle childhood (ages 6 to 9), and early adolescence (ages 10 to 13). Transactional relations differed between caregiving stress and internalizing versus externalizing behavior. Targeting executive functioning in evidence-based interventions for children with prenatal substance exposure who present with internalizing problems and treating caregiving psychopathology, depression, and parenting stress in early childhood may be particularly important for children presenting with internalizing behavior.
10 - Patterns and processes in geographic range size in coral reef fishes
- from PART II - PATTERNS AND PROCESSES
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- By Benjamin I. Ruttenberg, California Polytechnic State University, Sarah E. Lester, University of California
- Edited by Camilo Mora, University of Hawaii, Manoa
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- Book:
- Ecology of Fishes on Coral Reefs
- Published online:
- 05 May 2015
- Print publication:
- 23 April 2015, pp 97-103
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Summary
Coral reef fishes vary dramatically in the extent of their geographic distributions, and the patterns, causes, and consequences of this extensive variation have long interested coral reef fish ecologists. Although there is still a great deal of uncertainty regarding the drivers of range size variation in coral reef fishes, research over the last several decades has greatly improved our understanding. Ecologists once suspected that larval traits, primarily pelagic larval dispersal potential, had a strong influence on species' ranges, but recent synthetic work has shown that larval dispersal only impacts range sizes when ranges cross the greatest dispersal barriers in the Pacific. Emerging work suggests that adult traits, such as body size, habitat preferences, and even nocturnal activity are correlated with range size, likely by increasing persistence of newly established populations. Processes that operate over evolutionary scales are also likely important, but it has been challenging to empirically examine these factors. However, the quantity and availability of biological information are increasing rapidly, providing reef fish ecologists with richer datasets with which to evaluate a broader range of hypotheses.
One of the most fundamental traits of a species is the size of its geographic range. Coral reef fishes show dramatic variation in range size, and even closely related species can have vastly different geographic extents. For example, the surge wrasse Thalassoma purpureum extends from South Africa to Central and South America, a span of nearly 28 000 km, while the Clipperton wrasse Thalassoma robertsoni is endemic to Clipperton Atoll in the tropical eastern Pacific, an island approximately 6 km long (Figure 10.1). Therefore, it is not surprising that this variation has interested coral reef biologists and biogeographers for decades.
The size of a species' range is likely the product of a wide variety of biotic and abiotic forces and as such can provide great insight into biogeographic and evolutionary patterns. Geographic range size can also have a large impact on a species' extinction risk, since widespread species are thought to be much less vulnerable to extinction than geographically restricted species [357, 915].
11 - NETWORKS – The assessment of marine reserve networks: guidelines for ecological evaluation
- from Part IV - Scale-up of marine protected area systems
- Edited by Joachim Claudet, Centre National de la Recherche Scientifique (CNRS), Paris
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- Book:
- Marine Protected Areas
- Published online:
- 05 August 2012
- Print publication:
- 29 September 2011, pp 293-321
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Summary
Introduction
As marine ecosystems are plagued by an ever-increasing suite of threats including climate change, pollution, habitat degradation, and fisheries impacts (Roessig et al., 2004; Lotze et al., 2006; Jackson, 2008), there are now no ocean areas that are exempt from anthropogenic impacts (Halpern et al., 2008). In order to preserve marine biodiversity, ecosystem function, and the goods and services provided by resistant and/or resilient systems, marine reserves have been increasingly recommended as part of an ecosystem-based approach to management (Browman and Stergiou, 2004; Levin et al., 2009). Marine reserves are defined as “areas of the ocean completely protected from all extractive and destructive activities” (Lubchenco et al., 2003) and can be experimental controls for evaluating the impact of these activities on marine ecosystems. Growing scientific information has shown consistent increases in species density, biomass, size, and diversity in response to full protection inside reserves of varying sizes and ages located in diverse regions (Claudet et al., 2008; Lester et al., 2009; Molloy et al., 2009). However, most of these data are from individual marine reserves and therefore have inherently limited transferability to networks of marine reserves, which when properly designed can outperform single marine reserves for a variety of ecological, economic, and social management goals (Roberts et al., 2003; Almany et al., 2009; Gaines et al., 2010).
The concept of marine reserve networks grew out of a desire to achieve both conservation and fishery management goals by minimizing the potential negative economic, social, and cultural impacts of a single large reserve while still producing similar or even greater ecological and economic returns (Murray et al., 1999; Gaines et al., 2010). In addition, reserves networks can provide insurance by protecting areas across a region and spreading the risk that these sites may be impacted by localized catastrophes such as hurricanes or oil spills (Allison et al., 2003). The World Conservation Union's Marine Programme defines a network as “a collection of individual marine protected areas (MPAs) or reserves operating co-operatively and synergistically, at various spatial scales and with a range of protection levels that are designed to meet objectives that a single reserve cannot achieve” (IUCN–WCPA, 2008). However, general terms such as “co-operatively” and “synergistically” can have myriad meanings. Without a clear definition of a network, it becomes difficult to identify attainable management goals and design a process for evaluating whether the network achieves those goals. Besides, different management goals may in turn result in the need for different types of networks. The use of MPAs with varying protection levels together with no-take zones in multiple-zoning schemes adds another layer of complexity to network design and evaluation; however, partially protected areas are generally used to manage coastal uses and avoid conflicts (rather than for strict ecological purposes) and are therefore a function of the local social, economic, and cultural context. As we are here interested in the ecological effects of networks, for the purposes of this chapter, we focus on marine reserves because these areas are no-take and therefore offer greater ecological benefits than other types of MPAs that allow some forms of extraction (Lester and Halpern, 2008).
Spillover from marine reserves and the replenishment of fished stocks
- BENJAMIN S. HALPERN, SARAH E. LESTER, JULIE B. KELLNER
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- Journal:
- Environmental Conservation / Volume 36 / Issue 4 / December 2009
- Published online by Cambridge University Press:
- 24 February 2010, pp. 268-276
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No-take marine reserves are widely recognized as an effective conservation tool for protecting marine resources. Despite considerable empirical evidence that abundance and biomass of fished species increase within marine reserve boundaries, the potential for reserves to provide fisheries and conservation benefits to adjacent waters remains heavily debated. This paper uses statistical and population models to evaluate published empirical data on adult spillover from marine reserves and shows that spillover is a common phenomenon for species that respond positively to reserve protection, but at relatively small scales, detectable on average up to 800 m from reserve boundaries. At these small scales, local fisheries around reserves were likely unsustainable in 12 of 14 cases without the reserve, and spillover partially or fully offsets losses in catch due to reserve closure in the other two cases. For reserves to play a role in sustaining and replenishing larger-scale fished stocks, networks of reserves may be necessary, but as few exist this is difficult to evaluate. The results suggest reserves can simultaneously meet conservation objectives and benefit local fisheries adjacent to their boundaries.