Grasshopper (Orthoptera: Acridoidea) Species Diversity in the Pampas, Argentina
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Diversity and Distributions (2000) 6, 81-91 BIODIVERSITY RESEARCH Grasshopper (Orthoptera: Acridoidea) species diversity in the Pampas, Argentina MARÍA MARTA CIGLIANO.* MARÍA LAURA DE WYSIECKIf and CARLOS E. I.ANGIA * Departamento Científico de Entomología, Museo de Ciencias Naturales, Paseo del Boscpte sin 1900 La Plata, Argentina. E-mail: [email protected], t Centro de Estudios Parasitológicos y de Vectores (CEPAVE), Calle 2 Nro. 584 1900 La Plata, Argentina Abstract. A study was conducted to describe buted species made up 14.7% of species composi the major features of geographical and temporal tion and intermediately and narrowly distributed variation in the diversity of grassland grasshopper species made up 26.5% and 58.8%. respectively. species (Orthoptera: Acridoidea) in different sites The three top-ranked species in the studied sites of the Pampas. Argentina. Species richness and were Dichroplus elongatus. D. pratensis and relative abundance were assessed at 12 sites in Staurorhectus longicornis. Results showed eastern La Pampa and western Buenos Aires that, contrary to what was expected, one of provinces, from 1994 through 1999. Mean spe the widely distributed species in the region (i.e. cies richness at the regional level was 10. and Baeacris punctulatus) does not always constitute 34 grasshopper species were collected throughout one of the most abundant species. Finally, the of the study. Comparison with grasshopper spe loss of one of the historically most common cies diversity from the Great Plains of North species in the Pampas. D. mactilipennis. is also America is discussed. An evaluation of the discussed. proportions of species in each of the three distribution groups (broad, intermediate and Key words. Acridoidea. diversity, grasshoppers. narrow) revealed that, over all sites, broadly distri Orthoptera. Pampas grasslands. in weather conditions (Dempster. 1963; Uvarov. INTRODUCTION 1966. 1977; Capinera & Florton. 1989; Joem & Ecologists and biogeographers have struggled to Gaines. 1990; Kemp & Cigliano. 1994; Lockwood. understand spatial and temporal variations in 1997; Schell & Lockwood. 1997). the abundance, distribution, and number of spe Grasshoppers are among the most import cies. At the community level, the structure of ant native herbivores throughout much of the an assemblage with time may greatly change Pampas. Of the 230 grasshopper species known in terms of both number and relative abund for Argentina, about 110 inhabit grasslands ance of the species. Many populations of herbi (Cigliano & Lange. 1998). The Pampas region vorous insects fluctuate in size, although some covers approximately 15% of the country, and others are relatively constant from year to year. in the last few decades most of it has under Grasshopper communities exhibit large temporal gone increasing change in land use. Grazing oscillations in abundance (Gage & Mukerji. 1977; and agricultural activities have been intensified, Joem & Pruess. 1986; Kemp. 1987; 1992a; 1992b; and natural pasture areas have been drastically Cigliano et al., 1995b) mostly attributed to changes reduced or altered (Llorens. 1995). Grasshoppers © 2000 Blackwell Science Ltd. http://www.blackwell-science.com/ddi 81 82 Al. Al. Cigliano et al. are a recurrent pest of the natural and artificial MATERIALSAND METHODS pastures of Argentina, inflicting damage on graz Study area and collections ing systems and competing for food with the stock (Hemming & Waloff, 1972; Liebermann, The study area was located in western Buenos 1972; De Wysiecki & Sánchez, 1992; Cigliano Aires and eastern La Pampa provinces (Fig. 1) et al., 1995a; Cigliano & Lange, 1998). in the Pampas biogeographic region as defined Despite the importance of grasshoppers in by Cabrera & Willink (1973). This region encom the Pampas, little work has been conducted on passes a large proportion of available grassland analysing the relative abundance and species habitat types in the country. Two sites (Santa composition of grasshopper communities in the Rosa and Carhué) were monitored from 1994 area (Sánchez & de Wysiecki, 1993). The goal through 1999. The remaining sites were visited of this paper is to describe the major features during 1 year (Villa Sauri, Guatraché, Padre of spatial and temporal variation in the divers Buodo, General Acha and El Durazno), 2 years ity of species in different sites of this grassland (Alta Italia and Ojeda) or 3 years (América, region. Pehuajó and Castex). Fig. I Map showing sites used for collection of grassland grasshopper data 1994-99, Buenos Aires (BA) and eastern La Pampa (LP) provinces, Argentina. 1, Carhué; 2, Guatraché; 3, Padre Buodo; 4, General Acha; 5, El Durazno; 6, Villa Sauri; 7, Santa Rosa; 8, Castex; 9, Alta Italia; 10, Ojeda; 11, América; and 12, Pehuajó. © 2000 Blackwell Science Ltd, Diversity and Distributions, 6, 81-91 Grasshopper diversity in the Argentine Pampas 83 Sweep-net collections were made at each site, (Table 1). Average species richness ranged from along vegetation transects. Sites were visited four to 12 species per site among the 12 studied twice in the season (early January, early/mid- sites. Low numbers of grasshopper species per February) to ensure detection of species with site were found in Villa Sauri (four species) and different phenological patterns. Three hundred General Acha (five species). Higher values of sweeps per site were made at each sampling species richness (12-16 species) were found in period between 1000 and 1600 h under sunny Ojeda (15), Alta Italia (12), Santa Rosa (16), sky and light winds. To reduce chances of vari Castex (15) and Pehuajo (12). Mean species ability caused by sampling error, collections were richness at the regional level (all sites, all years) always made by the same two people. One should was 10. be aware of the existence of possible biases when testing hypotheses that rely on grasshopper Taxonomic diversity community composition estimates obtained from sweep samples. However, studies have shown From a taxonomic perspective, within the Acrid- that sweep netting generally provide accurate idae the Melanoplinae was the most abundant estimates of grasshopper diversity on grasslands and diverse subfamily (14 species belonged to (Evans et al., 1983; Larson et al., 1999). Grass this subfamily that represented 68.8% of the total hoppers collected via sweep-net were placed in grasshoppers’ relative abundance) in our study, cages, and taken to the laboratory for identifica followed by the Gomphocerinae (nine species tion to species and determination of development belonged to this subfamily, representing 23.8% stages. of the total grasshoppers’ relative abundance), Acridinae (three species belonged to this sub family, representing 3.3% of the grasshoppers’ Analyses relative abundance), Copiocerinae (two species of Relative abundance the grasshoppers caught were copiocerine repres Of grasshopper species was calculated as the enting 2.4% of the total grasshoppers’ relative abundance of species i relative to the total abund abundance) and Leptysminae (only one species ance of all species collected at each site. For of Leptysminae was caught representing 0.32% each year mean values from January-February of the total). Only five species of Romaleinae were considered in the analysis. (1.28% of the total relative abundance) were col lected (Tables 1 and 2). Species distribution hierarchy In order to examine whether the proportion of Relative abundance species in distribution hierarchy groups was con stant over the entire region, the proportion of the Average relative abundance of grasshopper spe species at each site that were narrowly (present cies from the 12 studied sites fluctuated among at <25% of the 30 total site-years), intermediately years (Table 1). For all the sites and years the (present at > 25 and < 75% of the 30 total site — most abundant three species (D. elongatus, D. years) and broadly (present at >75% of the 30 pratensis and S', longicornis) constituted 63.4% total site-years) distributed were computed. of the grasshopper assemblage (Table 1). Many species can be considered uncommon Species richness or rare. B. punctulatus was detected during most Species richness was quantified as the total number of the years but in low numbers (numerical rarity). of species present in a community. Some species (L. pulcher) were found in reason able numbers, in many years, but only in some locations (spatial rarity). RESULTS There were no major differences in grass hopper assemblages between the two sites that Grasshopper species richness were monitored for a longer time. For Carhue Thirty-four grasshopper species, belonging to the most abundant four species (S. longicornis, two families and six subfamilies were recorded D. elongatus, D. pratensis and L. pulcher) constituted © 2000 Blackwell Science Ltd, Diversity and Distributions, 6, 81-91 84 Table I (A) Mean relative abundance (individuals/300 sweeps) patterns of grassland grasshopper species collected in Guatrache, Padre Buodo (P. Buodo), Al. General Acha (G. Acha), El Durazno, Villa Sauri (V. Sauri), Castex, Alta Italia, Ojeda and América, in the Pampas, Argentina 1994-99 Al. Family/subfamily/species Castex Alta Italia Ojeda América Cigliano Guatrache r. buodo or. Acna Bl Durazno V. bauri 1994 1994 1994 1995 1995 1995 1996 1997 1997 1999 1997 1999 1997 1998 1999 ACRIDIDAE et Acridinae al. Allotruxalis strigata (Bruner) 13 4 7 6 2 2 3 2 Covasacris albitarsis Liebermann 4 5 Parorphula gramínea Bruner 1 Leptysminae Leptysma argentina