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  • 1
    Online Resource
    Online Resource
    Oxford :Oxford University Press, Incorporated,
    Keywords: Desert ecology. ; Electronic books.
    Description / Table of Contents: A revised and thoroughly updated edition of this concise but comprehensive introduction to desert ecology.
    Type of Medium: Online Resource
    Pages: 1 online resource (395 pages)
    Edition: 2nd ed.
    ISBN: 9780191047305
    Series Statement: Biology of Habitats Series
    DDC: 578.754
    Language: English
    Note: Cover -- Preface to the First Edition -- Preface to the Second Edition -- Contents -- Plates -- 1 Introduction -- 1.1 General introduction -- 1.2 What creates a desert? -- 1.3 Deserts have low precipitation and high variability in precipitation -- 1.4 How old are deserts? -- 1.5 Deserts are created by a lack of precipitation and not high temperatures -- 1.6 Aridity indices -- 1.7 What denies rainfall to deserts? -- 1.8 Global change and deserts -- 2 Abiotic Factors -- 2.1 Precipitation -- 2.1.1 Rainfall -- 2.2 Temperature -- 2.2.1 Hot deserts -- 2.2.2 Cold deserts -- 2.3 Declines in pan evaporation -- 2.4 Geology -- 2.4.1 Desert landscapes -- 2.5 Fire -- 2.6 Wind erosion -- 3 Morphological and Physiological Adaptations of Desert Plants to the Abiotic Environment -- 3.1 Classifications of desert plants -- 3.2 Types of photosynthesis -- 3.3 Biological soil crusts -- 3.4 Annual plants -- 3.4.1 Desert versus mesic annual species -- 3.4.2 Seed germination and dispersal strategies -- 3.4.3 Why is long-range dispersal rare in desert plants? -- 3.4.4 Delayed germination -- 3.4.5 Seed heteromorphism -- 3.5 Grasses, forbs, and shrubs/perennials -- 3.5.1 Clonality -- 3.5.2 Photosynthesis and stomatal opening -- 3.5.3 Heat shock proteins -- 3.5.4 Specific leaf area -- 3.5.5 Leaf pubescence -- 3.5.6 Fog-an unusual water source -- 3.5.7 Grasses -- 3.6 Geophytes -- 3.6.1 Hysteranthy and its consequences -- 3.7 Stem and leaf succulents -- 3.7.1 Stem succulents -- 3.7.2 Leaf succulents -- 3.8 Halophytes -- 3.9 Phreatophytes -- 3.9.1 Hydraulic lift -- 4 Morphological, Physiological, and Behavioural Adaptations of Desert Animals to the Abiotic Environment -- 4.1 Evaders and evaporators -- 4.1.1 Snails -- 4.1.2 Frogs -- 4.1.3 Rodents -- 4.1.4 Spider burrows and termite mounds -- 4.1.5 Physiological mechanisms of controlling heat gain. , 4.2 Adaptations to handle unique situations -- 4.2.1 Salt glands in birds and reptiles -- 4.2.2 Mammals that consume halophytes -- 4.2.3 Animals in temporary pools -- 4.3 Endurers -- 4.3.1 Ants -- 4.3.2 Large mammals -- 4.4 Removing the effects of phylogeny -- 4.4.1 Insects (tenebrionid beetles) -- 4.4.2 Birds -- 4.4.3 Marsupial mammals -- 5 The Role of Competition and Facilitation in Structuring Desert Communities -- 5.1 Plant communities -- 5.1.1 Annual plant communities -- 5.1.2 Interactions among desert shrubs -- 5.1.3 Fairy circles, heuweltjies, and mima mounds-competition, herbivory, or self-organization? -- 5.1.4 Facilitation and nurse-plant effects -- 5.2 Competition between animals -- 5.2.1 Patch scale -- 5.2.2 Habitat selection models -- 5.3 Indirect interactions: keystone species and apparent competition -- 5.3.1 Keystone species -- 5.3.2 Short-term apparent competition -- 6 The Importance of Predation and Parasitism -- 6.1 Direct mortality -- 6.2 Predation risk -- 6.3 Apparent predation risk -- 6.4 Priority effects -- 6.5 Spiders -- 6.6 Scorpions -- 6.7 Visually hunting predators -- 6.8 Snakes, scent-hunting predators -- 6.9 Keystone predation -- 6.10 Animal parasites and parasitoids -- 6.10.1 Parasites -- 6.10.2 Parasitoids -- 7 Plant-Animal Interactions in Deserts -- 7.1 Herbivory -- 7.1.1 Grazing effects on species composition -- 7.1.2 Long-term studies of the effects of large mammals on arid vegetation -- 7.1.3 Effects of herbivory on relationships among plant functional types -- 7.1.4 Is Australia a special case?-a meta-analysis -- 7.1.5 Effects of insect herbivory on desert plants -- 7.2 Pollination -- 7.2.1 Yucca-yucca moth mutualism -- 7.2.2 The senita cactus-senita moth obligate mutualism -- 7.3 Seed dispersal and seed predation -- 7.3.1 Myrmecochory -- 7.3.2 Diplochory: using two mechanisms to disperse. , 7.4 Are these coevolved systems? -- 7.4.1 Senita and yucca systems -- 7.4.2 Why Negev flowers are often red -- 7.4.3 Dorcas gazelle-lily system -- 7.4.4 Wood rats and their toxic diets -- 8 Desert Food Webs and Ecosystem Ecology -- 8.1 Do deserts have simple food webs? -- 8.1.1 Can we scale up from two-species interactions to desert ecosystems? -- 8.2 Food webs -- 8.2.1 Polis and Ayal's problems with food-web models -- 8.3 Interactions among habitats-spatial subsidies -- 8.4 Effects of precipitation, nutrients, disturbances, and decomposition -- 8.4.1 Effects of precipitation -- 8.4.2 Effects of nutrients -- 8.4.3 Disturbances -- 8.4.4 Decomposition -- 9 Biodiversity and Biogeography of Deserts -- 9.1 Are deserts species-poor? α, β, and γ diversity patterns -- 9.1.1 Plants -- 9.1.2 Animals -- 9.2 Productivity-diversity relationships in deserts -- 9.3 Convergence and divergence of desert communities -- 9.3.1 Community-wide character displacement -- 9.4 Large-scale patterns in desert biogeography -- 9.4.1 Plants -- 9.4.2 Animals -- 10 Human Impacts and Desertification -- 10.1 The sensitive desert ecosystem: myth or reality? -- 10.2 Pastoralism is the most important use of desert lands -- 10.2.1 Oscillations of vegetation and herbivore populations -- 10.2.2 Woody plant encroachment -- 10.2.3 Invasive species -- 10.2.4 Global climate changes -- 10.3 Pumping aquifers: a problem of less water and more salinity -- 10.4 When is it desertification? The importance of reversibility -- 11 Conservation of Deserts -- 11.1 Are deserts worth conserving? -- 11.2 Conservation of desert species or habitats -- 11.2.1 Umbrella species -- 11.2.2 Keystone species -- 11.2.3 Focal species -- 11.2.4 Single populations -- 11.2.5 SLOSS or metapopulations -- 11.2.6 Conserving the entire habitat -- 11.3 The 3 Rs: reintroduction, recolonization, and revegetation. , 11.3.1 Asiatic wild ass -- 11.3.2 Arabian oryx -- 11.3.3 Recolonization by the American black bear -- 11.3.4 Revegetation -- 11.4 Genotype by environment interactions and intraspecific variability -- 11.5 Who gets to pay for this conservation and how is it controlled? -- 11.6 People are also part of the desert environment -- 11.7 Conclusions -- References -- Index.
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  • 2
    Electronic Resource
    Electronic Resource
    Melbourne, Australia : Blackwell Science Pty
    Austral ecology 25 (2000), S. 0 
    ISSN: 1442-9993
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: Flowering and fruiting were assessed on 14 populations of the grasstree, Xanthorrhoea preissii Endl., occurring in the Darling Range near Perth, Western Australia. Independent of site, season of burn or year of flowering, there was a strong relationship between plant height, which varied from 0.1 to over 2 m, and the incidence of postfire flowering, which varied from 1% (winter burn) to 75% (summer burn) of grasstrees present. There was no relationship between inflorescence dimensions, or flower or fruit production on a spike basis, and plant size/age (height). When standardized for height, spring-burnt populations produced 40% as many inflorescences as autumn-burnt populations and 20% as many as summer-burnt populations. Inflorescences produced by spring-burnt plants were moderately smaller than those by summer–autumn-burnt plants. Fruit density per spike in autumn-burnt plants was 80% of that in spring–summer-burnt plants. The net effect was an average of 70 000 fruits produced per 100 summer-burnt plants, 22 000 in autumn-burnt plants, and 14 000 in spring-burnt plants. Ecophysiological explanations of these results and their implications for population dynamics have yet to be explored.
    Type of Medium: Electronic Resource
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