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Grasslands of the World.pdf - Disasters and Conflicts - UNEP

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<strong>Grassl<strong>and</strong>s</strong> <strong>of</strong> Patagonia 145<br />

2001). Currently, nitrogen dynamics are being studied in relation to: <strong>the</strong> effect<br />

<strong>of</strong> litter nitrogen content <strong>of</strong> different plant life forms on soil N fractions in<br />

<strong>the</strong> grass-steppe ecosystems (Sain, Bertiller <strong>and</strong> Carrera, 2001) <strong>and</strong> <strong>the</strong> Monte<br />

shrub steppes (Carrera et al., 2001); effects <strong>of</strong> levels <strong>of</strong> soil nitrogen fractions<br />

on <strong>the</strong> segregation <strong>of</strong> male <strong>and</strong> female Poa ligularis individuals (Bertiller, Sain<br />

<strong>and</strong> Carrera, 2001); soil nitrogen mineralization rates in relation to grazing<br />

(Anchorena et al., 2001); decomposition rates <strong>of</strong> litter with different nitrogen<br />

content (Semmartin et al., 2001); <strong>and</strong> nitrogen use efficiency (toge<strong>the</strong>r with<br />

water use efficiency) <strong>of</strong> 26 species <strong>of</strong> plants from Patagonian ecosystems<br />

(Golluscio, Oesterheld <strong>and</strong> Soriano, 2001).<br />

Current studies on <strong>the</strong> effects <strong>of</strong> fire on Patagonian ecosystems mostly<br />

include monitoring <strong>of</strong> vegetation following natural wildfire outbreaks. Such<br />

studies include: descriptions <strong>of</strong> post-burn secondary succession patterns<br />

(Gherm<strong>and</strong>i, Guthmann <strong>and</strong> Bran, 2001; González et al., 2001; Rafaelle <strong>and</strong><br />

Veblen, 2001); study <strong>of</strong> biotic <strong>and</strong> abiotic (including wea<strong>the</strong>r) conditions that<br />

promote wildfire outbreaks (Defossé et al., 2001; De Torres Curth, Gherm<strong>and</strong>i<br />

<strong>and</strong> Pfister, 2001); <strong>and</strong> effects <strong>of</strong> wildfires on survival <strong>of</strong> adult tussocks or seeds<br />

in soil seed-banks (Gittins, Bran <strong>and</strong> Gherm<strong>and</strong>i, 2001; González, Gherm<strong>and</strong>i<br />

<strong>and</strong> Becker, 2001). Almost all fire-related studies have been conducted ei<strong>the</strong>r in<br />

<strong>the</strong> shrub-steppe ecosystems or <strong>the</strong> steppe-forest ecotones .<br />

Current studies on wildlife in Patagonia include: surveys <strong>of</strong> animal numbers<br />

such as guanaco population numbers in relation to sheep density <strong>and</strong> forage<br />

availability (Baldi, Albon <strong>and</strong> Elston, 2001); calculations <strong>of</strong> Rhea densities<br />

using improved field methods (Funes et al., 2001); census <strong>of</strong> migratory bird<br />

species in sou<strong>the</strong>rn Patagonia (Manero et al., 2001); predator -prey relations<br />

studying fox <strong>and</strong> European hare populations <strong>and</strong> diets <strong>of</strong> a number <strong>of</strong> predators<br />

<strong>of</strong> <strong>the</strong> shrub steppe ecosystems (Donadío et al., 2001; Novaro et al., 2001);<br />

habitat use by Rheas (Bellis et al., 2001); <strong>and</strong> deer reproductive ecology in relation<br />

to droughts (Flueck, 2001).<br />

ANPP <strong>of</strong> Patagonian ecosystems is currently being studied in relation to<br />

range condition (Bonvissuto, González Carteau <strong>and</strong> Moraga, 2001), grazing<br />

system (Collantes, St<strong>of</strong>fella <strong>and</strong> Pomar, 2001), competition among plant lifeforms<br />

(Schlichter, Fernández <strong>and</strong> Gyenge, 2001), or forage production (Bustos<br />

<strong>and</strong> Marcolín, 2001). Satellite image analysis using NDVI at regional scales<br />

continues to be used as a tool to estimate ANPP (Fabricante et al., 2001).<br />

Decomposition is being studied at regional scales ei<strong>the</strong>r along rainfall gradients<br />

(Austin <strong>and</strong> Sala, 2001), or in relation to a species’ successional status within<br />

<strong>the</strong> plant community <strong>and</strong> its litter N content (Semmartin et al., 2001). At local<br />

scales, decomposition <strong>of</strong> forbs is being studied in relation to increased ultraviolet-B<br />

radiation, derived from <strong>the</strong> thinning in <strong>the</strong> ozone layer at high latitudes in<br />

<strong>the</strong> sou<strong>the</strong>rn hemisphere (Pancotto et al., 2001).<br />

A number <strong>of</strong> ongoing research projects include <strong>the</strong> study <strong>of</strong> aspects <strong>of</strong><br />

<strong>the</strong> biology <strong>of</strong> a few shrub species, namely: shrub secondary compounds

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