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Anuran Responses to Spatial Patterns of Agricultural Landscapes in Argentina

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Anuran Responses to Spatial Patterns of Agricultural Landscapes in Argentina View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Servicio de Difusión de la Creación Intelectual Landscape Ecol (2016) 31:2485–2505 DOI 10.1007/s10980-016-0426-2 RESEARCH ARTICLE Anuran responses to spatial patterns of agricultural landscapes in Argentina Romina P. Sua´rez . Maria E. Zaccagnini . Kimberly J. Babbitt . Noela C. Calamari . Guillermo S. Natale . Alexis Cerezo . Nadia Codugnello . Teresa Boca . Maria J. Damonte . Josefina Vera-Candioti . Gregorio I. Gavier-Pizarro Received: 25 February 2015 / Accepted: 28 July 2016 / Published online: 13 August 2016 Ó Springer Science+Business Media Dordrecht 2016 Abstract and evaluated landscape influence on communities Context Amphibians are declining worldwide and and individual species at two spatial scales. land use change to agriculture is recognized as a Methods We compared anuran richness, frequency leading cause. Argentina is undergoing an agricultur- of occurrence, and activity between landscapes using alization process with rapid changes in landscape call surveys data from 120 sampling points from 2007 structure. to 2009. We evaluated anuran responses to landscape Objectives We evaluated anuran response to land- structure variables estimated within 250 and 500-m scape composition and configuration in two land- radius buffers using canonical correspondence analy- scapes of east-central Argentina with different degrees sis and multimodel inference from a set of candidate of agriculturalization. We identified sensitive species models. Results Anuran richness was lower in the landscape with greater level of agriculturalization with reduced amount of forest cover and stream length. This pattern Electronic supplementary material The online version of this article (doi:10.1007/s10980-016-0426-2) contains supple- mentary material, which is available to authorized users. R. P. Sua´rez (&) Á M. E. Zaccagnini Á A. Cerezo M. J. Damonte Á G. I. Gavier-Pizarro Asociacio´n Aves Argentinas, Matheu 1246, Buenos Aires, Biodiversidad, Ecologı´a y Gestio´n Ambiental en Argentina Agroecosistemas (BIOEGA), Instituto de Recursos Biolo´gicos (IRB), Instituto Nacional de Tecnologı´a A. Cerezo Agropecuaria (INTA), Centro Nacional de Departamento de Me´todos Cuantitativos, Facultad de Investigaciones Agropecuarias (CNIA), De los Reseros y Agronomı´a, Universidad de Buenos Aires, Av. San Martı´n Nicola´s Repetto s/n, Hurlingham (1686), Buenos Aires, 4453, CP 1417 Buenos Aires, Argentina Argentina e-mail: [email protected] N. Codugnello Laboratorio de Ecologı´a, Universidad Nacional de Luja´n, K. J. Babbitt Ruta 5 y Constitucio´n, Luja´n (6700), Buenos Aires, Department of Natural Resources and the Environment, Argentina University of New Hampshire, Durham, NH 03861, USA G. S. Natale N. C. Calamari Centro de Investigaciones del Medio Ambiente, Instituto Nacional de Tecnologı´a Agropecuaria (INTA), Departamento de Quı´mica, Facultad de Ciencias Exactas, EEA Parana´, Factores Bio´ticos y Proteccio´n Vegetal, Ruta Universidad Nacional de La Plata, Calle 47 y 115 (s/n), La 11 km 12.7, Oro Verde (3101), Entre Rı´os, Argentina Plata, Buenos Aires, Argentina 123 2486 Landscape Ecol (2016) 31:2485–2505 was driven by the lower occurrence and calling In Argentina, agriculture expansion and intensifi- activity of seven out of the sixteen recorded species. cation occurs primarily in the Pampas and Espinal eco- Four species responded positively to the amount of regions (Viglizzo et al. 2003), which are the most forest cover and stream habitat. Three species productive regions in the country. Natural vegetation, responded positively to forest cohesion and negatively such as forests and grasslands are reduced and to rural housing. Two responded negatively to crop replaced by row crop production expansion (Tassi area and diversity of cover classes. et al. 2011). Although there are several important Conclusions Anurans within agricultural landscapes crops in these regions, soybean production is the main of east-central Argentina are responding to landscape driver of the agriculturalization process (Young 2006) structure. Responses varied depending on species and and the dominant type of row crop (FAOSTAT 2014; study scale. Life-history traits contribute to responses SAGPYA 2014). differences. Our study offers a better understanding of Therefore, agricultural landscapes show a lower landscape effects on anurans and can be used for land land-use diversity and heterogeneity (Aizen et al. 2009). management in other areas experiencing a similar Also, greater input of agrochemical products to enhance agriculturalization process. production is observed (Pe´rez Leiva and Anastasio 2003; Zaccagnini et al. 2007a; Bernardos and Zaccag- Keywords Amphibian conservation Á Agriculture nini 2011; CASAFE 2014). As a consequence, the expansion and intensification Á Entre Rios Á Espinal Á composition and spatial configuration of agricultural Landscape structure Á Habitat loss Á Forest landscapes are changing, altering the integrity and connectivity Á Landscape heterogeneity sustainability of agroecosystems (Zaccagnini et al. 2007b; De la Fuente and Sua´rez 2008; Aizen et al. 2009) and resulting in loss of biodiversity in the region (Schrag et al. 2009; Gavier-Pizarro et al. 2012). Introduction Biodiversity conservation is an essential consider- ation for sustainable agroecosystems (Altieri 1999). World population growth and food demand is leading Of special concern in agroecosystems are amphibians, to an agriculturalization process in many countries, which play key ecological roles in ecosystem func- which involves rapid changes in land use and tioning (Seale 1980; Wyman 1998; Marcot and promotes environmental degradation (Rabinovich Vander Heyden 2001). In agroecosystems, adult and Torres 2004; Young 2006). This process is stages are valuable as biological pest controllers for characterized by the expansion and intensification of agriculture production (Attademo et al. 2005), and are land production areas that results in landscapes with considered good biological indicators because they reduced natural vegetation distributed in remnant respond quickly to environmental change (EPA 2002). patches and greater technology use to enhance Many amphibian species are declining worldwide and production yields (Viglizzo et al. 2001; Aizen et al. habitat loss, fragmentation and degradation by agri- 2009; Oesterheld 2008). culture have been recognized as leading factors in several countries (Bishop and Pettit 1992; Sparling T. Boca 2002). In Argentina, these factors are also expected to Instituto de Clima y Agua, Instituto Nacional de affect amphibian conservation in agroecosystems, but Tecnologia Agropecuaria (INTA), Centro Nacional de Investigaciones Agropecuarias (CNIA), De los Reseros y effects of landscape change through agriculturaliza- Nicola´s Repetto s/n Hurlingham (1686), Buenos Aires, tion are still not clear. Agriculturalization generates Argentina landscapes with varying levels of transformation. By comparing these different landscapes, we can better J. Vera-Candioti Instituto Nacional de Tecnologı´a Agropecuaria (INTA) understand how amphibians respond to agricultural A.E.R., Venado Tuerto, Santa Fe, Argentina expansion and intensification by identifying sensitive species and key factors that determine their persis- J. Vera-Candioti tence (Pulliam 1988; Opdam 1990). Consejo Nacional de Investigaciones Cientı´ficas y Te´cnicas (CONICET), Ciudad Auto´noma de Buenos Many amphibians have a biphasic life cycle Aires, Argentina requiring both aquatic and terrestrial natural habitats 123 Landscape Ecol (2016) 31:2485–2505 2487 for reproduction, larval development, feeding, hiber- dependent anurans may show greater sensitivity to nation and dispersal processes (Heyer et al. 1994). forest loss and fragmentation in the surrounding Thus, the availability, quality and connectivity of landscape matrix (Gibbs 1998) than highly mobile required habitats are fundamental for their persistence habitat-generalist species or less mobile forest-depen- in agroecosystems. Recent international research on dent species. Thus, it is important to study agricultural the relationships between amphibians and landscape effects on anurans at the community and species levels attributes indicate that habitat loss and fragmentation at multiple scales to better understand the differential exert strong negative effects on amphibians (Cushman response of each species (Cushman 2006). 2006). Forest area surrounding ponds (Knutson et al. Our aim was to evaluate the effect of agricultural- 1999; Houlahan et al. 2000; Herrmann et al. 2005), ization and resulting landscape structure on anurans in proximity of ponds to forests and distance among Argentina. Thus, we compared anuran responses ponds (Guerry and Hunter 2002; Veysey et al. 2011)as patterns between two agricultural landscapes with well as connectivity of both ponds and forested different levels of agriculture expansion and intensi- habitats (Hecnar and M’Closkey 1996; Marsh and fication and evaluated the relation to landscape Trenham 2001; Rothermel 2004) were identified as composition and configuration. We used these two key predictors of regional viability of amphibian agricultural landscapes as a proxy to represent a populations. Several studies demonstrate that local gradient of landscapes changes occurring during the and landscape changes resulting from agricultural agriculturalization process. Considering anuran life expansion have negative effects on amphibian diver-
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