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The Utility of Zooarchaeological Data to Guide Listing Efforts for an Imperiled Mussel Species (Bivalvia: Unionidae: Pleurobema Riddellii)

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The Utility of Zooarchaeological Data to Guide Listing Efforts for an Imperiled Mussel Species (Bivalvia: Unionidae: Pleurobema Riddellii) See discussions, stats, and author profiles for this publication at: https://www.researchgate.net/publication/343135336 The utility of zooarchaeological data to guide listing efforts for an imperiled mussel species (Bivalvia: Unionidae: Pleurobema riddellii) Article in Conservation Science and Practice · July 2020 DOI: 10.1111/csp2.253 CITATIONS READS 0 103 7 authors, including: Charles Randklev Steve Wolverton Texas A&M University University of North Texas 66 PUBLICATIONS 405 CITATIONS 106 PUBLICATIONS 1,554 CITATIONS SEE PROFILE SEE PROFILE Nathan Johnson Chase Smith United States Geological Survey University of Texas at Austin 62 PUBLICATIONS 563 CITATIONS 27 PUBLICATIONS 57 CITATIONS SEE PROFILE SEE PROFILE Some of the authors of this publication are also working on these related projects: Ancient DNA - Lama guanicoe View project New and Confirmed Fish Hosts of the Texas Fatmucket View project All content following this page was uploaded by Steve Wolverton on 22 July 2020. The user has requested enhancement of the downloaded file. Received: 4 March 2020 Revised: 14 May 2020 Accepted: 2 June 2020 DOI: 10.1111/csp2.253 CONTRIBUTED PAPER The utility of zooarchaeological data to guide listing efforts for an imperiled mussel species (Bivalvia: Unionidae: Pleurobema riddellii) Charles R. Randklev1 | Steve Wolverton2 | Nathan A. Johnson3 | Chase H. Smith4 | Traci P. DuBose5 | Clinton R. Robertson6 | Julian Conley7 1Texas A&M Natural Resources Institute, Texas A&M AgriLife Research Center at Abstract Dallas, Dallas, Texas The status of species in freshwater systems shift over time due to natural and 2Department of Geography and the anthropogenic causes. Determining the magnitude and cause of these shifts Environment & the Advanced requires a long-term perspective. This process is complicated when there are Environmental Research Institute, University of North Texas, Denton, Texas also questions about the taxonomic validity of a species. Addressing these 3US Geological Survey, Wetland and issues is important because both can undermine conservation and manage- Aquatic Research Center, Gainesville, ment efforts if incorrect. Pleurobema riddellii, Louisiana Pigtoe, is under review Florida for protection under the U.S. Endangered Species Act, but its status in the 4Department of Integrative Biology, University of Texas, Austin, Texas Trinity River basin, where the taxon was described, remains in doubt due to 5Oklahoma Biological Survey, Department questions about its taxonomy and occurrence within this basin. To address of Biology, and Ecology and Evolutionary these questions, we compared shell morphometrics of P. riddellii dating to the Biology Graduate Program, University of late Holocene with modern P. riddellii, late Holocene Fusconaia sp., and mod- Oklahoma, Norman, Oklahoma 6Texas Parks and Wildlife Department, ern Fusconaia sp. using multivariate analyses to test associations between the Rivers Studies Program, San Marcos, putative morphotypes. Based on these analyses, we demonstrate that P. Texas riddellii was likely present in the Trinity during the late Holocene, which indi- 7 Department of Geosciences, East cates questions about its taxonomic validity or presence in this basin are Tennessee State University, Johnson City, Tennessee unfounded. Our study further highlights the role zooarchaeological studies can play in status assessments and their utility in better understanding biogeo- Correspondence graphic patterns for rare species. Charles R. Randklev, Texas A&M Natural Resources Institute, Texas A&M AgriLife Research Center at Dallas, Dallas, TX KEYWORDS 75252. conservation, morphometrics, mussels, shifting baselines, Texas, zooarchaeology Email: [email protected] 1 | |INTRODUCTION perspective to disentangle natural variability from other trends (Lyman, 2012; Rick & Lockwood, 2013). Unfortu- The distribution and abundance of species in freshwater nately, conservationists and natural resource managers communities shift over time due to natural and anthro- often perceive faunal changes over relatively short-time pogenic causes. Determining the magnitude and poten- scales, typically during the career length of individual tial causes of these changes requires a long-term biologists (Humphries & Winemiller, 2009). This short- This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited. © 2020 The Authors. Conservation Science and Practice published by Wiley Periodicals LLC on behalf of Society for Conservation Biology Conservation Science and Practice. 2020;e253. wileyonlinelibrary.com/journal/csp2 1of12 https://doi.org/10.1111/csp2.253 2of12 RANDKLEV ET AL. time scale is problematic because it can lead to shifting Anthropogenic alterations to freshwater environ- conservation baselines, wherein ideas of a “natural” base- ments have led to species loss comparable to mass extinc- line or reference point from which to measure biological tions during major transitions of geological time periods change shift from one generation to the next due to (Barnosky et al., 2011; Strayer & Dudgeon, 2010), and changing cultural and scientific perceptions. As a conse- more freshwater mollusk extinctions have occurred in quence, benchmarks become a progressively less accurate North American rivers than for any other region on target for the intended “natural” condition (Humphries Earth (Regnier, Fontaine, & Bouchet, 2009). Freshwater & Winemiller, 2009; Papworth, Rist, Coad, & Milner- mussels (hereafter mussels) are among the most imper- Gulland, 2009; Pauly, 1995), leading to incorrect conclu- iled faunas in North America and have one of the highest sions regarding changes in species abundances, distribu- extinction and imperilment rates globally (Haag, 2012; tions, and assemblage composition. In turn, such Haag & Williams, 2014; Williams, Warren, Cummings, conclusions can result in ineffective conservation and Harris, & Neves, 1993). Natural resource managers and management actions (see discussions in Dromrosky, conservationists have attempted to mitigate these Wolverton, & Nagaoka, 2016; Lyman, 1998; Peacock, declines through a variety of strategies (FMCS (Freshwa- Randklev, Wolverton, Palmer, & Zaleski, 2012; Popejoy, ter Mollusk Conservation Society), 2016; NNMCC Randklev, Neeson, & Vaughn, 2018; Randklev, (National Native Mussel Conservation Committee), 1998), Wolverton, Lundeen, & Kennedy, 2010). including formal listing at state and/or federal levels For researchers and conservationists who do employ (Earl et al., 2018). In Texas, located in the southwestern a longer temporal perspective, the baseline chosen is typi- United States, similar efforts have resulted in the listing cally the last 200 years. This phenomenon is described as of 19 mussel species as state-threatened or endangered the “Pre-1800 Dilemma,” and is based largely on the false (TPWD (Texas Parks and Wildlife Department), 2010; notion that data for this period are: (a) more numerous 2020), of which 1 species (Popenaias popeii) is now listed and accessible compared to data from earlier periods; (b) as Endangered under the U.S. Endangered Species Act more compatible with recently collected ecological data; (ESA), 3 (Cyclonaias aurea, Cyclonaias houstonensis, and (c) provide a more appropriate baseline for contra- Fusconaia lananensis) were excluded from ESA listing sting between pre- and post-European settlement condi- due to taxonomic revisions (Johnson et al., 2018; Pieri tions, which are widely considered to be the catalyst of et al., 2018), 4 (Fusconaia askewi, Fusconaia chunii, most, if not all, of today’s conservation issues (Szabo & Lampsilis satura, Potamilus streckersoni) have not been Hedl, 2011). However, conservation targets based on evaluated by U.S. Fish and Wildlife Service (USFWS), 1 benchmarks attuned to conditions within the last couple (Obovaria arkansasensis) had a negative 90-day finding of hundred years may be problematic because communi- resulting in no USFWS action (USFWS, 2010), and 10 ties change naturally on time scales that are much longer others are currently under review for protection under (Callicott, 2002; Landres, 1992), contributing to a shifting the ESA (USFWS, 2009a; 2009b; 2011; 2016; Table S1). baseline problem. Thus, parsing the natural and anthro- The conservation status for these 10 species is being pogenic drivers of biodiversity change requires long-term determined, in part, using knowledge of their historical data that incorporate natural community changes and contemporary presumptive ranges and trends in dis- (Magurran et al., 2010). Paleozoological data from tribution and abundance (Smith et al., 2018; archaeological and paleontological faunas offer greater TPWD, 2012). In both cases an assumption has been time depth but are often dismissed for being too descrip- made, knowingly or unknowingly, that recent historical tive and imprecise, which is shown repeatedly not to be ranges for these species (since about late 1800s; e.g., the case (Dietl & Flessa, 2011; Louys, Wilkinson, & Singley, 1893; Strecker, 1931) represent a “natural condi- Bishop, 2012; Lyman, 1998; Peacock, Randklev, tion” to measure current change against. Wolverton, Palmer, & Zaleski, 2012; Wolverton, Ken- Pleurobema riddellii, Louisiana Pigtoe, one of the ten nedy, & Cornelius, 2007). It is true that paleozoological species petitioned for listing by USFWS (2009b), is con- data have been used in ecological and
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