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Structural equation modeling of a winnowed soil microbiome identifies how invasive plants re-structure microbial networks

机译:持续的土壤微生物组的结构方程模型确定了侵入性植物如何重新结构微生物网络

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Conceptual diagram of the general winnowing and network prediction algorithms for microbial taxa with example results using degree centrality. Abundance data were conditioned using Laplace (add-1) smoothed [65] to reduce the undue influence of absent or rare species on subsequent network analyses (step 1). Correlation matrices were generated using maximal information coefficient (MIC) [50] (step 2). Centrality metrics drawn from graph theory highlight different aspects of changing microbial populations (step 3) [66] (see Supporting Information for results of the other centrality measures). Winnowed microbial communities were ordered by decreasing centrality (step 4) and a certain number selected (step 5) based on area under the curve (AUC) sensitivity analysis of the metric of interest. The selected operational taxonomic units (OTUs) were evaluated by treatment effect (i.e., brome-invaded versus natural grasslands; step 6) by testing the homogeneity of multivariate dispersions within groups using permutational analysis of variance (PERMANOVA) [52] at 5% AUC intervals. The F-statistic was scaled from 0 to 1 and spline-smoothed (solid line) to facilitate comparisons among the datasets. The dashed line indicates standard deviation calculated within a 5% moving window. Closed circles indicate retained taxa. Points were plotted at 1% intervals around each cut-off point. The number of sequentially ordered OTUs were selected to maximize the F-statistic and minimize the standard deviation (e.g., 99 OTUs in blue text). To test the consistency of the selection procedure, we ran a sensitivity analysis to evaluate the effect of parameter selection on the winnowing process conditioning for each centrality measure (select j OTUs per iteration; step 7). BW betweenness, CL closeness, DG degree, EV eigenvector. To generate the data used for the structural equation modeling (SEM), we iterated the winnowing pipeline in a leave-one-out procedure to quantify the contribution of each sample plot to abundance and centrality for each OTU (n = number of samples; steps 8–9). We used the sum of all OTU abundance-centrality distances to origin (step 10) as an endogenous variable in our SEM. Winnowed OTUs are represented by enlarged points with black outlines in the abundance versus occupancy plot
机译:一般风选和网络的预测算法,用于使用程度中心示例结果的微生物类群概念图。丰度数据使用拉普拉斯(添加-1)平滑空调[65],以减少不存在或稀有物种对后续的网络分析(步骤1)的不适当的影响。采用最大信息系数(MIC)[50]产生相关矩阵(步骤2)。从图论拉伸中心度量突出改变的微生物种群(步骤3)[66]的不同方面(见支持信息对的另一中心性措施的结果)。淘微生物群落是通过降低中心性(步骤4)和一定数目的选择基于所述度量的兴趣的曲线(AUC)敏感性分析下面积(步骤5)排序。通过使用方差permutational分析(PERMANOVA)组内的测试多元分散体的均匀性[52]在5%AUC;所选择的操作分类单元(的OTU)通过治疗效果(步骤6即雀麦 - 侵入与天然草地)来评价间隔。 F统计按比例从0到1和样条平滑(实线),以促进数据集之间进行比较。虚线表示在5%移动窗口内计算的标准偏差。封闭的圆圈表示保留类群。点物在围绕每个截止点的1周%的时间间隔作图。选择顺序排列的OTU的数量最大化F统计和最小化的标准偏差(例如,99个OTU在蓝色文本)。为了测试选择过程的一致性,我们进行了灵敏度分析,以评估参数选择的针对每个中心度量的风选过程调节(选择Ĵ个OTU每次迭代;步骤7)的效果。 BW介,CL亲近,DG度,EV特征向量。为了产生用于结构方程模型(SEM)的数据,我们迭代在留一出过程的风选管道定量每个样品情节丰度和中心的每个OTU的贡献(样品N =数目;步骤8-9)。我们使用的所有OTU丰度,中心性距离的总和原点(步骤10),在我们的SEM上的内生变量。淘的OTU通过与在丰与占用情节黑色轮廓扩大点表示

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