Effects of Vegetation Change on Ant Communities of Arid Rangelands

1981 ◽  
Vol 10 (6) ◽  
pp. 893-897 ◽  
Author(s):  
Wendy A. Wisdom ◽  
Walter G. Whitford
2013 ◽  
Vol 32 (1) ◽  
Author(s):  
Mouldi Gamoun

AbstractThe response of a plant community to protection from grazing, as a function of year and soil type, was studied in the arid rangelands of southern Tunisia between 2007 and 2009. The vegetation of rangelands is often altered under grazing pressure, but unfortunately, removing the grazing pressure often does not reverse the changes in the way the succession model predicts. Rainfall variability is a key driver of ecosystem structure and function in arid rangelands, and this arid area of North Africa is characterized by low and erratic rainfall and is prone to drought conditions which normally occur every two to three years.Steppes are likely to exhibit strong and rapid structural and functional responses to these altered rainfall patterns. Although drought affects vegetation cover more in loamy soil than in all other soils, it affects diversity on all soils; particularly limestone and loam soils


1987 ◽  
Vol 9 (1) ◽  
pp. 5 ◽  
Author(s):  
AD Wilson ◽  
NA Abraham ◽  
R Barratt ◽  
J Choate ◽  
DR Green ◽  
...  

Methods for measuring long-term changes in vegetation and soil condition were evaluated in terms of recording error, efficiency and value in meeting management objectives. The evaluation was made on 4-5 sites for each of six vegetation types across the semi-arid rangelands of South Australia and New South Wales. In the semi-arid woodlands the lowest errors of measurement (C.V. = 12-14%) were associated with point measures of canopy cover, while in the chenopod shrublands the most precise measure in most situations was the density of shrub clumps (C.V. = 12-16%). Measures of herbaceous and litter cover had a high error of measurement (e.g. C.V. = 60%) and observers were significantly different. The point measurement of the area of degraded soil surface was reliable on duplex soils, but not on gradational soils. The results are discussed in terms of their application for the monitoring of change in range condition. It is concluded that the most appropriate measure of the shrub layer is foliar cover in woodlands and clump density in chenopod shrublands.


Biologija ◽  
2016 ◽  
Vol 62 (2) ◽  
Author(s):  
Mouldi Gamoun ◽  
Bouajila Essifi ◽  
Chris Dickens ◽  
Belgacem Hanchi

Arid rangelands worldwide regularly confront drought and overgrazing. Land degradation is mostly apparent in desert rangelands, where drought events are important and grazing influences and intrinsic vegetation change act intermittently. The objectives of this study were to determine the effects of grazing and drought stress on diversity, species richness and primary production in desert rangeland of southern Tunisia. This assessment was conducted in March 2008 (wet year) and March 2009 (dry year) both on grazed and ungrazed sites. Diversity, species richness and biomass production exhibited bigger variation between years than among sites within two years. Although protection from grazing could slightly increase rangeland production in favorable years, the additive effects of heavy grazing and drought could result in restoration failure. This study suggests that climatic variations, particularly droughts, control major trends in plant species composition, diversity and biomass. Under grazing, plants of desert regions are able to respond very rapidly to small drought. The latter is the most debilitating risk in desert areas.


2000 ◽  
pp. 26-31
Author(s):  
E. I. Parfenova ◽  
N. M. Chebakova

Global climate warming is expected to be a new factor influencing vegetation redistribution and productivity in the XXI century. In this paper possible vegetation change in Mountain Altai under global warming is evaluated. The attention is focused on forest vegetation being one of the most important natural resources for the regional economy. A bioclimatic model of correlation between vegetation and climate is used to predict vegetation change (Parfenova, Tchebakova 1998). In the model, a vegetation class — an altitudinal vegetation belt (mountain tundra, dark- coniferous subalpine open woodland, light-coniferous subgolets open woodland, dark-coniferous mountain taiga, light-coniferous mountain taiga, chern taiga, subtaiga and forest-steppe, mountain steppe) is predicted from a combination of July Temperature (JT) and Complex Moisture Index (CMI). Borders between vegetation classes are determined by certain values of these two climatic indices. Some bioclimatic regularities of vegetation distribution in Mountain Altai have been found: 1. Tundra is separated from taiga by the JT value of 8.5°C; 2. Dark- coniferous taiga is separated from light-coniferous taiga by the CMI value of 2.25; 3. Mountain steppe is separated from the forests by the CMI value of 4.0. 4. Within both dark-coniferous and light-coniferous taiga, vegetation classes are separated by the temperature factor. For the spatially model of vegetation distribution in Mountain Altai within the window 84 E — 90 E and 48 N — 52 N, the DEM (Digital Elevation Model) was used with a pixel of 1 km resolution. In a GIS Package IDRISI for Windows 2.0, climatic layers were developed based on DEM and multiple regressions relating climatic indices to physiography (elevation and latitude). Coupling the map of climatic indices with the authors' bioclimatic model resulted into a vegetation map for the region of interest. Visual comparison of the modelled vegetation map with the observed geobotanical map (Kuminova, 1960; Ogureeva, 1980) showed a good similarity between them. The new climatic indices map was developed under the climate change scenario with summer temperature increase 2°C and annual precipitation increase 20% (Menzhulin, 1998). For most mountains under such climate change scenario vegetation belts would rise 300—400 m on average. Under current climate, the dark-coniferous and light-coniferous mountain taiga forests dominate throughout Mountain Altai. The chern forests are the most productive and floristically rich and are also widely distributed. Under climate warming, light-coniferous mountain taiga may be expected to transform into subtaiga and forest-steppe and dark-coniferous taiga may be expected to transform partly into chern taiga. Other consequences of warming may happen such as the increase of forest productivity within the territories with sufficient rainfall and the increase of forest fire occurrence over territories with insufficient rainfall.


2013 ◽  
Vol 21 (3) ◽  
pp. 343-351
Author(s):  
Lu Zhixing ◽  
Chen Youqing ◽  
Zhang Wei ◽  
Wang Siming ◽  
Li Qiao

2002 ◽  
Vol 39 (2) ◽  
pp. 279-293 ◽  
Author(s):  
R.S. Smith ◽  
R.S. Shiel ◽  
D. Millward ◽  
P. Corkhill ◽  
R.A. Sanderson

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