Yidi Wang’s research while affiliated with Beijing Forestry University and other places

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Publications (1)


Composition and abundance of the metal community in the Yellow River. (a) Locations of all the sampling sites along the river. Blue lines indicate the river mainstream and its tributaries as the Yellow River crosses the plateau and non‐plateau regions. The monitored reach of the mainstream covers a 5,200 km continuum. 49 sampling sites are numbered sequentially from the source to the estuary. Tangnaihai, Toudaoguai, and Huayuankou successively demarcate the whole river into plateau, upstream, midstream, and downstream reaches. For detailed information on each site please refer to Table S1 in Supporting Information S2. (b) Non‐metric multidimensional scaling diagram based on Bray–Curtis distances showing metal community dissimilarities among the nine sample types, namely water‐plateau (W‐P), water‐spring (WS), water‐autumn (WA), SPM‐plateau (SPM‐P), SPM‐spring (SPMS), SPM‐autumn (SPMA), sediment‐plateau (S‐P), sediment‐spring (SS), and sediment‐autumn (SA) samples. Analysis of similarity r value quantifies the extent of inter‐group and intra‐group dissimilarities, with a higher r value indicating that inter‐group differences surpass intra‐group differences. The P value denotes the statistical significance level. (c) Composition of metal communities at group and individual levels for the nine sampling types in the river. Inner circular diagram shows relative abundance of different metals in the nine sample types. Only those dominant metals with a mean relative abundance of ≥1% in all samples are depicted. The ribbon width for each metal is directly proportional to its relative abundance in each sample type. The ribbon color relates to the metal category. (d) Metals content in water (μg/L), suspended particulate matter (μg/g), and sediment (μg/g) samples along the Yellow River. The 62 metals detected are divided into nine categories (alkali metals, alkaline‐earth metals, ferrous metals, lanthanides, platinum‐based metals, other transition metals, third main group metals, metalloids, and other metals) and individually color‐coded. Details of the metals content data for the nine sampling types are provided in Figure S3 in Supporting Information S1.
Coherence of metal communities from upper continental crust (UCC) to Yellow River, aquatic organisms (represented by fish) and extended to the human body. (a) Correlation between metal contents in UCC and in water‐plateau, SPM‐plateau, sediment‐plateau, water‐spring and water‐autumn, SPM‐spring and SPM‐autumn, and sediment‐spring and sediment‐autumn samples. Blue solid circles represent spring, whereas red solid circles represent autumn. (b) Heatmap showing the enrichment factor of metals in suspended particulate matter and sediment samples. (c) Piper trilinear diagram of chemical compositions for the Yellow River (unit: %). (d) Gibbs diagram of samples characterized by TDS versus Na⁺/(Na⁺ + Ca²⁺) and TDS versus Cl⁻/(Cl⁻ + HCO³⁻). (e) and (f) Correlation between metal content in sediment of the Yellow River, fish tissue (gill, muscle, gonad, and liver) and human organs and markers (brain, teeth, blood, and urine). Dashed lines represent fitted linear regressions. Correlation values (r) and significance level (P) are also provided.
Quorum effect analysis unravels the relationship between metal abundance and toxicity. (a) Water‐plateau (W‐P), (b) water‐spring (WS), (c) water‐autumn (WA), (d) SPM‐plateau (SPM‐P), (e) SPM‐spring (SPMS), (f) SPM‐autumn (SPMA), (g) sediment‐plateau (S‐P), (h) sediment‐spring (SS), and (i) sediment‐autumn (SA). Correlation values (r) and significance level (P) are also provided.
Consistency of metal resistance genes (MRGs) and metal toxicity in water, suspended particulate matter (SPM), and sediment of the Yellow River. (a) Composition profile of MRGs. (b) MRG abundance (copies/cell) rises with increasing metal toxicity in water, SPM, and sediment. Correlation values (r) and significance level (P) are also provided.
Nature unity schema showing (a) metal coherence from the upper crust through China's Mother River to its ecosystems and the associated significance for (b) drinking and (c) dietary standards. Correlation values (r) and significance level (P) are also provided.
Universal Coherence of Elements in River‐Fed Earth‐Human Systems
  • Article
  • Full-text available

November 2024

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145 Reads

Yidi Wang

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Qian Zhang

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Weiling Sun

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Elements are the indelible imprint left by the Earth on rivers and life entities. Here, we unveil the evident inheritance of persistent elements, from the Earth's upper continental crust, through the Yellow River, to the associated life entities along a 5,200 km continuum of the Mother River of the Chinese nation. In particular, we confirm the coherence of “metal community” composed of more than 60 detected metallic elements throughout water, suspended particulate matter, and sediment in the river, and further extend such elemental correlations to fish species and even the tissues in human body. Our study also reveals an interesting fact that media‐specific metal abundance occurs in a persistent inverse order with metal toxicity, and microbial cells in the river tend to establish their own self‐defense systems against toxic metals through hosting higher‐level resistance genes. These findings not only stress the human needs for integrated trace element provision, but also highlight the fundamental importance of elemental coherence in the river‐coordinated Earth‐life systems for establishing drinking water and dietary standards that benefit ecological and human health.

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