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  • 1
    Call number: 9783319714042 (e-book)
    Type of Medium: 12
    Pages: 1 Online-Ressource (xv, 435 Seiten) , Illustrationen, Diagramme
    Edition: Second edtion
    ISBN: 9783319714042 (e-book)
    Series Statement: Use R!
    Language: English
    Note: Contents 1 Introduction 1.1 Why Numerical Ecology? 1.2 Why R? 1.3 Readership and Structure of the Book 1.4 How to Use This Book 1.5 The Data Sets 1.5.1 The Doubs Fish Data 1.5.2 The Oribatid Mite Data 1.6 A Quick Reminder About Help Sources 1.7 Now It Is Time 2 Exploratory Data Analysis 2.1 Objectives 2.2 Data Exploration 2.2.1 Data Extraction 2.2.2 Species Data: First Contact 2.2.3 Species Data: A Closer Look 2.2.4 Ecological Data Transformation 2.2.5 Environmental Data 2.3 Conclusion 3 Association Measures and Matrices 3.1 Objectives 3.2 The Main Categories of Association Measures (Short Overview) 3.2.1 Q Mode and R Mode 3.2.2 Symmetrical or Asymmetrical Coefficients in Q Mode: The Double-Zero Problem 3.2.3 Association Measures for Qualitative or Quantitative Data 3.2.4 To Summarize 3.3 Q Mode: Computing Dissimilarity Matrices Among Objects 3.3.1 Q Mode: Quantitative Species Data 3.3.2 Q Mode: Binary (Presence-Absence) Species Data 3.3.3 Q Mode: Quantitative Data (Excluding Species Abundances) 3.3.4 Q Mode: Binary Data (Excluding Species Presence-Absence Data) 3.3.5 Q Mode: Mixed Types Including Categorical (Qualitative Multiclass) Variables 3.4 R Mode: Computing Dependence Matrices Among Variables 3.4.1 R Mode: Species Abundance Data 3.4.2 R Mode: Species Presence-Absence Data 3.4.3 R Mode: Quantitative and Ordinal Data (Other than Species Abundances) 3.4.4 R Mode: Binary Data (Other than Species Abundance Data) 3.5 Pre-transformations for Species Data 3.6 Conclusion 4 Cluster Analysis 4.1 Objectives 4.2 Clustering Overview 4.3 Hierarchical Clustering Based on Links 4.3.1 Single Linkage Agglomerative Clustering 4.3.2 Complete Linkage Agglomerative Clustering 4.4 Average Agglomerative Clustering 4.5 Ward's Minimum Variance Clustering 4.6 Flexible Clustering 4.7 Interpreting and Comparing Hierarchical Clustering Results 4.7.1 Introduction 4.7.2 Cophenetic Correlation 4.7.3 Looking for Inteipretable Clusters 4.8 Non-hierarchical Clustering 4.8.1 k-means Partitioning 4.8.2 Partitioning Around Medoids (PAM) 4.9 Comparison with Environmental Data 4.9.1 Comparing a Typology with External Data (ANOVA Approach) 4.9.2 Comparing Two Typologies (Contingency Table Approach) 4.10 Species Assemblages 4.10.1 Simple Statistics on Group Contents 4.10.2 Kendall's W Coefficient of Concordance 4.10.3 Species Assemblages in Presence-Absence Data 4.10.4 Species Co-occurrence Network 4.11 Indicator Species 4.11.1 Introduction 4.11.2 IndVal: Species Indicator Values 4.11.3 Correlation-Type Indices 4.12 Multivariate Regression Trees (MRT): Constrained Clustering 4.12.1 Introduction 4.12.2 Computation (Principle) 4.12.3 Application Using Packages mvpart and MVPARTwrap 4.12.4 Combining MRT and IndVal 4.13 MRT as a Monothetic Clustering Method 4.14 Sequential Clustering 4.15 A Very Different Approach: Fuzzy Clustering 4.15.1 Fuzzy c-means Using Package cluster's Function fanny () 4.15.2 Noise Clustering Using the vegclust () Function 4.16 Conclusion 5 Unconstrained Ordination 5.1 Objectives 5.2 Ordination Overview 5.2.1 Multidimensional Space 5.2.2 Ordination in Reduced Space 5.3 Principal Component Analysis (PCA) 5.3.1 Overview 5.3.2 PCA of the Environmental Variables of the Doubs River Data Using rda () 5.3.3 PCA on Transformed Species Data 5.3.4 Domain of Application of PCA 5.3.5 PCA Using Function PCA. newr () 5.3.6 Imputation of Missing Values in PCA 5.4 Correspondence Analysis (CA) 5.4.1 Introduction 5.4.2 CA Using Function cca () of Package vegan 5.4.3 CA Using Function CA. newr () 5.4.4 Arch Effect and Detrended Correspondence Analysis (DCA) 5.4.5 Multiple Correspondence Analysis (MCA) 5.5 Principal Coordinate Analysis (PCoA) 5.5.1 Introduction 5.5.2 Application of PCoA to the Doubs Data Set Using cmdscaleO and vegan 5.5.3 Application of PCoA to the Doubs Data Set Using pcoa () 5.6 Nonmetric Multidimensional Scaling (NMDS) 5.6.1 Introduction 5.6.2 Application to the Doubs Fish Data 5.6.3 PCoA or NMDS? 5.7 Hand-Written PCA Ordination Function 6 Canonical Ordination 6.1 Objectives 6.2 Canonical Ordination Overview 6.3 Redundancy Analysis (RDA) 6.3.1 Introduction 6.3.2 RDA of the Doubs River Data 6.3.3 Distance-Based Redundancy Analysis (db-RDA) 6.3.4 A Hand-Written RDA Function 6.4 Canonical Correspondence Analysis (CCA) 6.4.1 Introduction 6.4.2 CCA of the Doubs River Data 6.5 Linear Discriminant Analysis (LDA) 6.5.1 Introduction 6.5.2 Discriminant Analysis Using Ida () 6.6 Other Asymmetric Analyses 6.6.1 Principal Response Curves (PRC) 6.6.2 Co-correspondence Analysis (CoCA) 6.7 Symmetric Analysis of Two (or More) Data Sets 6.8 Canonical Correlation Analysis (CCorA) 6.8.1 Introduction 6.8.2 Canonical Correlation Analysis Using CCorA () 6.9 Co-inertia Analysis (CoIA) 6.9.1 Introduction 6.9.2 Co-inertia Analysis Using Function coinertia () of ade4 6.10 Multiple Factor Analysis (MFA) 6.10.1 Introduction 6.10.2 Multiple Factor Analysis Using FactoMineR 6.11 Relating Species Traits and Environment 6.11.1 The Fourth-Corner Method 6.11.2 RLQ Analysis 6.11.3 Application in R 6.12 Conclusion 7 Spatial Analysis of Ecological Data 7.1 Objectives 7.2 Spatial Structures and Spatial Analysis: A Short Overview 7.2.1 Introduction 7.2.2 Induced Spatial Dependence and Spatial Autocorrelation 7.2.3 Spatial Scale 7.2.4 Spatial Heterogeneity 7.2.5 Spatial Correlation or Autocorrelation Functions and Spatial Correlograms 7.2.6 Testing for the Presence of Spatial Correlation: Conditions 7.2.7 Modelling Spatial Structures 7.3 Multivariate Trend-Surface Analysis 7.3.1 Introduction 7.3.2 Trend-Surface Analysis in Practice 7.4 Eigenvector-Based Spatial Variables and Spatial Modelling 7.4.1 Introduction 7.4.2 Distance-Based Moran's Eigenvector Maps (dbMEM) and Principal Coordinates of Neighbour Matrices (PCNM) 7.4.3 MEM in a Wider Context: Weights Other than Geographic Distances 7.4.4 MEM with Positive or Negative Spatial Correlation: Which Ones should Be Used? 7.4.5 Asymmetric Eigenvector Maps (AEM): When Directionality Matters 7.5 Another Way to Look at Spatial Structures: Multiscale Ordination (MSO) 7.5.1 Principle 7.5.2 Application to the Mite Data - Exploratory Approach 7.5.3 Application to the Detrended Mite and Environmental Data 7.6 Space-Time Interaction Test in Multivariate ANOVA, Without Replicates 7.6.1 Introduction 7.6.2 Testing the Space-Time Interaction with the sti Functions 7.7 Conclusion 8 Community Diversity 8.1 Objectives 8.2 The Multiple Facets of Diversity 8.2.1 Introduction 8.2.2 Species Diversity Measured by a Single Number 8.2.3 Taxonomic Diversity Indices in Practice 8.3 When Space Matters: Alpha, Beta and Gamma Diversities 8.4 Beta Diversity 8.4.1 Beta Diversity Measured by a Single Number 8.4.2 Beta Diversity as the Variance of the Community Composition Table: SCBD and LCBD Indices 8.4.3 Partitioning Beta Diversity into Replacement, Richness Difference and Nestedness Components 8.5 Functional Diversity, Functional Composition and Phylogenetic Diversity of Communities 8.5.1 Alpha Functional Diversity 8.5.2 Beta Taxonomic, Phylogenetic and Functional Diversities 8.6 Conclusion Bibliography Index
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  • 2
    ISSN: 1432-1939
    Keywords: Body size ; Host-parasite relationship ; Lognormally skewed distribution ; Nematodes ; Independent comparisons
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Studying the diversification of body size in a taxon of parasites allows comparison of patterns of variation observed in the parasites with patterns found in free-living organisms. The distributions of body size of oxyurid nematodes (obligate parasites of vertebrates and invertebrates) are lognormally right-skewed, except for male oxyurids in invertebrates which show left-skewed distributions. In these parasitic forms, speciose genera do not have the smallest body sizes. Parasite body size is positively correlated with host body size, the largest hosts possessing the largest parasites. This trend is shown to occur within one monophyletic group of oxyurids, those of Old World primates. Comparative methods are used to take account of the effects of phylogeny. The use of multiple linear regression on distance matrices allows measurements of the contribution of phylogeny to the evolution of body size of parasites. Evolution of body size in female pinworms of Old World primates appears to be dependent only on the body size of their hosts. The tendency of parasite body size to increase with host body size is discussed in the light of the evolution of life-history traits.
    Type of Medium: Electronic Resource
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  • 3
    Electronic Resource
    Electronic Resource
    Springer
    Microbial ecology 12 (1986), S. 355-379 
    ISSN: 1432-184X
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract The process of wastewater treatment was studied by modeling the relationships between physical, chemical, and biological (bacteria, phytoplankton, zooplankton) components of the sewage treatment lagoons of an urban wastewater center, based upon a two-year sampling program. The models of interactions between variables were tested by path analysis. The path coefficients were computed from the results of ridge regression, instead of linear multiple regression. The results show that fecal coliforms were effectively controlled by the environmental variables included in the model, which have a cyclic seasonal behavior. This control grew stronger with distance from the input (R 2=0.71) to the output (R 2=0.88) of the treatment plant, resulting in effective elimination of most enteric bacteria. Simultaneously, the ecosystem's community of aerobic heterotrophic bacteria became more independent from the model's predictive variables, with increased distance from the sewage input, thus demonstrating its maturation as an autonomous community in the lagoon ecosystem. Consequences of modeling are discussed, with respect to the understanding of biological wastewater treatment mechanisms and ecosystem dynamics and to plant management.
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    Springer
    Journal of classification 5 (1988), S. 283-304 
    ISSN: 1432-1343
    Source: Springer Online Journal Archives 1860-2000
    Topics: Mathematics
    Type of Medium: Electronic Resource
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  • 5
    ISSN: 1432-1343
    Keywords: Analysis of variance ; Choropleth map ; Ecology ; Genetics ; Geography ; Permutation test ; Spatial autocorrelation
    Source: Springer Online Journal Archives 1860-2000
    Topics: Mathematics
    Description / Table of Contents: Résumé Cet article présente une solution au problème de l'analyse de variance, pour certains cas où la variable à analyser est spatialement autocorr élée alors que le critère de classification représente des sous-régions connexes du territoire à l'étude. On sait que les méthodes classiques d'analyse de variance ne sont pas applicables dans ce type de situation puisque la condition d'indépendance des échantillons n'est pas respectée; l'autocorrélation positive réduit la variabilité intragroupe, si bien que la quantité relative de variabilité intergroupe s'en trouve artificiellement augmentée. Cette situation correspond en réalité à une vaste catégorie de problèmes en génétique des populations, en écologie et dans d'autres branches de la biologie, ainsi qu'en épidémiologie, en géographie, en géologie, en science économique, en science politique et en sociologie. Ce nouveau test appartient à la famille des tests par permutation. Nous calculons la somme des dispersions intragroupes et testons contre une distribution de référence obtenue en permutant les régions géographiques un grand nombre de fois sur la carte. La véritable difficulté de ce test est d'ordre algorithmique, puisqu'il n'est pas facile de permuter des régions sur une carte, de façon à ce que chaque groupe demeure connexe, et que la carte permutée occupe le même espace total que la carte d'origine. Cet article présente la théorie, les algorithmes, ainsi que des résultats obtenus par cette méthode. Un programme écrit en PASCAL est disponible.
    Notes: Abstract The classical method for analysis of variance of data divided in geographic regions is impaired if the data are spatially autocorrelated within regions, because the condition of independence of the observations is not met. Positive autocorrelation reduces within-group variability, thus artificially increasing the relative amount of among-group variance. Negative autocorrelation may produce the opposite effect. This difficulty can be viewed as a loss of an unknown number of degrees of freedom. Such problems can be found in population genetics, in ecology and in other branches of biology, as well as in economics, epidemiology, geography, geology, marketing, political science, and sociology. A computer-intensive method has been developed to overcome this problem in certain cases. It is based on the computation of pooled within-group sums of squares for sampled permutations of internally connected areas on a map. The paper presents the theory, the algorithms, and results obtained using this method. A computer program, written in PASCAL, is available.
    Type of Medium: Electronic Resource
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  • 6
    Electronic Resource
    Electronic Resource
    Springer
    Journal of paleolimnology 6 (1991), S. 103-110 
    ISSN: 1573-0417
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology , Geosciences
    Notes: Conclusion The problem of correctly estimating the true mean of a time series of observations is not a simple one. Data normalization must be done with care, and no general recipe can be found that applies to all pH data series — or, for that matter, to any other variable of limnological interest. It depends on the type of variable and on the sampling scale (temporal or spatial), among other factors; each case has to be subjected anew to the search of the best normalizing transformation. Then, when estimating the confidence interval of the mean from a few observations only, the autocorrelation properties of the series must imperatively be taken into account. If they are not, the width of the confidence interval can be grossly underestimated.
    Type of Medium: Electronic Resource
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  • 7
    ISSN: 1572-9761
    Keywords: spatial pattern ; variogram ; correlogram ; fractal ; sampling design ; analysis of variance
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Detection of structured spatial variation and identification of spatial scales are important aspects of ecological studies. Spatial structures can correspond to physical features of the environment or to intrinsic characteristics of ecological processes and phenomena. Spatial variability has been approached through several techniques such as classical analysis of variance, or the calculation of fractal dimensions, correlograms or variograms. Under certain assumptions, these techniques are all closely related to one another and represent equivalent tools to characterize spatial structures. Our perception of ecological variables and processes depends on the scale at which variables are measured. We propose simple nested sampling designs enabling the detection of a wide range of spatial structures that show the relationships among nested spatial scales. When it is known that the phenomenon under study is structured as a nested series of spatial scales, this provides useful information to estimate suitable sampling intervals, which are essential to establish the relationships between spatial patterns and ecological phenomena. The use of nested sampling designs helps in choosing the most suitable solutions to reduce the amount of random variation resulting from a survey. These designs are obtained by increasing the sampling intensity to detect a wider spectrum of frequencies, or by revisiting the sampling technique to select more representative sampling units.
    Type of Medium: Electronic Resource
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  • 8
    ISSN: 1432-184X
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Time series of a population of fecal coliforms and a community of total viable counts were recorded during years 5 and 6 after the “birth” of an eutrophic aquatic ecosystem (sewage treatment lagoons). These time series were used to re-examine models, previously published, describing their temporal dynamics as well as the relationships between bacterial and environmental variables. The dynamics of the fecal coliforms and their relationships to the environment were unchanged; the fecal coliform abundances displayed an annual cycle with maximum reduction in numbers during the summer, which would be due at least partly to environmental variables (hypotheses of control by irradiance and pH, which have a seasonal behavior, are supported by the data). On the contrary, the total viable count dynamics moved towards a closer dependence on phytoplankton, from a situation of relative independence with respect to other biotic components of the ecosystem. Indeed during the first two years, only one of the abiotic variables in the model (the biological oxygen demand, which is an indicator of available organic matter) seemed to have an effect on the total viable counts. The behavior of these bacterial groups, measured during 1980–1982 and 1984–1986, shows that demographic and ecological laws founded on the observation of other organisms also apply to heterotrophic bacteria. A population, such as the fecal coliforms in the present study, has a limited ecological amplitude and is then more likely to react to environmental variables such as irradiance, pH, and phytoplanktonic metabolic products, whose bactericidal action is highest during the summer months and lowest during winter. On the other hand, a community such as that detected by the total viable counts of the present study is composed of many species and thus has a larger ecological amplitude. This makes it easier for the species to occupy the various available habitats and to maintain themselves through ecological succession and endogenous rhythms.
    Type of Medium: Electronic Resource
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  • 9
    Electronic Resource
    Electronic Resource
    Springer
    Microbial ecology 7 (1981), S. 283-296 
    ISSN: 1432-184X
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Microbial ecologists attempting to describe community structures through the use of synthetic parameters face enormous difficulties. These stem in part from the necessity of using standard taxonomic reference levels in a field where the species level is poorly defined. This paper presents an attempt to obviate this problem. A “functional evenness” index (E) is defined using information measures; it is based directly on the characteristics of the bacteria, as determined, for example, with the API 20B method. Comparisons of this index with classic structure indices, such as taxonomic evenness (Pielou) or systematic dominance (Hulburt), show that it behaves like an evenness index, while bypassing the taxonomic study required before computation of the classic indices. Its use is illustrated with samples of aerobic heterotrophic bacteria obtained from brackish lagoon sediments.
    Type of Medium: Electronic Resource
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  • 10
    Electronic Resource
    Electronic Resource
    Springer
    Statistics and computing 3 (1993), S. 197-199 
    ISSN: 1573-1375
    Source: Springer Online Journal Archives 1860-2000
    Topics: Computer Science , Mathematics
    Type of Medium: Electronic Resource
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