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Canoco version 5

Manufactured by Microcomputer Power
Sourced in United States

CANOCO version 5 is a software package for multivariate data analysis, including ordination methods such as principal component analysis (PCA), correspondence analysis (CA), and canonical correspondence analysis (CCA). The software is designed for ecologists and biologists to explore and interpret the relationships between species and environmental variables.

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5 protocols using canoco version 5

1

Spatiotemporal Analysis of Environmental Variables

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Patterns of spatiotemporal variability of physical and chemical variables were assessed via PCA, using the software CANOCO version 5 (Microcomputer Power, Ithaca, NY, USA). Variables were log transformed (except pH due to its logarithmic nature), centered, and standardized prior to the analysis. Comparisons among the three sampling periods for each physical and chemical variable were performed using repeated-measures ANOVA. Data were Box-Cox transformed when needed to fit homogeneity of variance assumption.
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2

Ecological Niche Comparison of Plant Hybrids

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Environmental conditions were characterized by mean Landolt indicator values (Landolt 2010) of accompanying vascular plant species in herb and shrub layers calculated for circular plots centered at each target individual. Landolt indicator values describe ecological requirements of species in terms of climate (temperature, T; continentality, K; light, L) and soil parameters (moisture, F; reaction, R; nutrients, N; humus content, H; aeration, D; moisture variability, W) ranging from 1 (low) to 5 (high). Niche differences among the two parental species and their hybrids (identified with NewHybrids, see Results) were tested by comparing averaged indicator values of accompanying species in a multivariate analysis of variance (MANOVA) in R version 3.0.2. Visualization of particular ecological niches was performed using a principal component analysis (PCA) with Canoco version 5 (Microcomputer Power, Ithaca, US), based on standardized indicator values. Differences in additional environmental factors recorded at sites were inferred in R, either using an analysis of variance (ANOVA) followed by Tukey's HSD post hoc test (coverage of vegetation layers, species diversity) or, if the assumptions of ANOVA were not met, using a Kruskal–Wallis rank_ sum test followed by a multiple comparison test available in the package Pgirmess version 1.5.9 (Giraudoux 2014; bare rock cover).
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3

Rhizosphere Bacterial Community Analysis

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Microsoft Excel Software was used to analyze the abundance and distribution of the key rhizosphere bacterial communities at the class and order level. Also, Shinyheatmap online tool (www1.heatmapper.ca/expression/) was used for the plotting of heatmaps using the relative abundance values. Equitability_J, Fisher_alpha, Berger-Parker and Chao-1 indices for diversity assessment were used for samples across rhizosphere and bulk soil samples, and the comparison of these indices was performed using Kruskal–Wallis test. The analyses were carried out using PAST version 3.20 (Hammer et al. 2001 ). Beta (β) diversity of the bacterial communities of the samples was determined using the Euclidean-based principal coordinate analysis (PCoA) and ANOSIM through 999 permutations. p < 0.05 was considered statistically significant for all datasets. Both PCoA and Principal Component Analysis (PCA) graphs were used to evaluate the relationship between bacterial communities and the measured physiochemical parameters, which were plotted using CANOCO version 5.0 (Microcomputer Power, Ithaca, NY). The effects of pH, total N and OM on the bacterial community distribution were determined using Canonical Correspondence analysis (CCA). Graphs and one-way ANOVA for functional measurements were achieved using GraphPad Prism 7 (GraphPad Software, California).
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4

Soil Enzyme Activities and Physico-Chemical Correlations

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All statistical analyses were performed using the software package SAS version 8.0 (SAS Institute, Inc., Cary, NC, USA). The data were statistically assessed through two-way ANOVA between means within the factors (treatments and days of incubation). The means and standard deviations (±SD) of three replications were reported. Comparisons of means were conducted using the LSD test, at P = 0.05. Redundancy analysis (RDA) with the Monte Carlo permutation test (499 permutations) was performed to determine if soil enzyme activities were correlated with variation of soil physic-chemical parameters, using the software Canoco version 5.0 (Microcomputer Power Inc., Ithaca, NY, USA).
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5

Evaluating Bacterial Community Diversity

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We evaluated the richness and diversity of the bacterial community through the application of Chao1 and Shannon indices, which were computed using Mothur (version 1.30.2). The taxonomic OTU tables were annotated to the Functional Annotation of Prokaryotic Taxa (FAPROTAX) to output the putative function groups. Analysis of Variance (ANOVA) followed by Duncan's multiple post hoc comparison tests (P < 0.05), was employed to determine the differences among different reclamation stages or land uses.
Permutational multivariate analysis of variance (PERMANOVA) with 999 permutations was performed to determine the effect of reclamation duration on bacterial community composition and functional groups in different land use.
To evaluate multicollinearity among environmental factors, the Variance Inflation Factor (VIF) was determined, and parameters with highest multicollinearity were eliminated for subsequent analysis.
Redundancy analysis (RDA) was performed using CANOCO (version 5.0) (Microcomputer Power, Ithaca, NY, USA) to visualize the relationships between different bacterial groups and environmental variables.
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