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. 2007 Sep 25;62(2):142–160. doi: 10.1111/j.1574-6941.2007.00375.x

Table 2.

Interpretation of ordination diagrams

Linear methods (PCA, RDA)

PCA, RDA RDA


Scaling 1 Scaling 2
Samples Species ENV NENV Focus on sample (rows) distance Focus on species (columns) correlation
Euclidean distances among samples
Linear correlations among species
Marginal effects of ENV on ordination scores Correlations among ENV
Euclidean distance between sample classes
Abundance values in species data
Values of ENV in the samples
Membership of samples in the classes
Linear correlations between species and ENV
Mean species abundance within classes of nominal ENV
Average of ENV within classes

Unimodal methods (CA, CCA)

CA, CCA CCA Focus on sample (rows) distance and Hill's scaling Focus on species (columns) distances

Turnover distances among samples χ2 distances between samples
- χ2 distances among species distributions
Marginal effects of ENV Correlations among ENV
Turnover distances between sample classes χ2 distances between sample classes
Relative abundances of the species table Relative abundances of the species table
Values of ENV in the samples
Membership of samples in the classes
Weighted averages – the species optima in respect to particular ENV
Relative total abundances in the sample classes
ENV averages within sample classes

The interpretation of ordination diagrams depends on the focus of the study, because sample scores are rescaled as a function of the scaling choice. Approximate relationships between and among the different elements represented in biplots and triplots as species (represented as dots or arrows), samples (dots), environmental variables (ENV; arrows), and nominal (qualitative) environmental variables (NENV; dots). A meaningless interpretation (“–”) happens when the suggested comparison is not optimal because of inappropriate scaling of the ordination scores. Adapted from ter Braak (1994); Leps & Smilauer (1999); ter Braak & Smilauer (2002).