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Geochemical Responses to Anthropogenic and Natural Influences in Ebinur Lake Sediments of Arid Northwest China

Identifieur interne : 000067 ( Pmc/Corpus ); précédent : 000066; suivant : 000068

Geochemical Responses to Anthropogenic and Natural Influences in Ebinur Lake Sediments of Arid Northwest China

Auteurs : Long Ma ; Jinglu Wu ; Jilili Abuduwaili ; Wen Liu

Source :

RBID : PMC:4866693

Abstract

Geochemical concentrations were extracted for a short sediment core from Ebinur Lake, located in arid northwest China, and mathematical methods were used to demonstrate the complex pattern of the geochemical anomalies resulting from the temporal changes in natural and anthropogenic forces on the lake sediments. The first element assemblage (C1) (aluminum, potassium, iron, magnesium, beryllium, etc.) was predominantly terrigenous; among the assemblage, total phosphorus and titanium were generally consistent with aluminum except with regards to their surface sequences, which inferred the differences of source regions for terrigenous detrital material led to this change around ca. 2000AD. The second assemblage (C2) (calcium and strontium) was found to have a negative relationship with aluminum through a cluster analysis. The third assemblage (C3) included sodium and magnesium, which were influenced by the underwater lake environment and deposited in the Ebinur depression. The concentration ratio of C1/(C1+C2) was used as an indicator for denudation amount of detrital materials, which was supported by the values of magnetic susceptibility. The enrichment factors for heavy metals suggested that the influence of human activities on heavy-metal enrichment in Ebinur Lake region was not severe over the past century. Prior to the 1960s, geochemical indicators suggested a stable lacustrine environment with higher water levels. Beginning in the 1960s, high agricultural water demand resulted in rapid declines in lake water level, with subsequent increases of lake water salinity, as evidenced by enhanced sodium concentration in lake core sediments. During this period, anthropogenic activity also enhanced the intensity of weathering and the denudation of the Ebinur watershed.


Url:
DOI: 10.1371/journal.pone.0155819
PubMed: 27176765
PubMed Central: 4866693

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PMC:4866693

Le document en format XML

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<p>Geochemical concentrations were extracted for a short sediment core from Ebinur Lake, located in arid northwest China, and mathematical methods were used to demonstrate the complex pattern of the geochemical anomalies resulting from the temporal changes in natural and anthropogenic forces on the lake sediments. The first element assemblage (C1) (aluminum, potassium, iron, magnesium, beryllium, etc.) was predominantly terrigenous; among the assemblage, total phosphorus and titanium were generally consistent with aluminum except with regards to their surface sequences, which inferred the differences of source regions for terrigenous detrital material led to this change around ca. 2000AD. The second assemblage (C2) (calcium and strontium) was found to have a negative relationship with aluminum through a cluster analysis. The third assemblage (C3) included sodium and magnesium, which were influenced by the underwater lake environment and deposited in the Ebinur depression. The concentration ratio of C1/(C1+C2) was used as an indicator for denudation amount of detrital materials, which was supported by the values of magnetic susceptibility. The enrichment factors for heavy metals suggested that the influence of human activities on heavy-metal enrichment in Ebinur Lake region was not severe over the past century. Prior to the 1960s, geochemical indicators suggested a stable lacustrine environment with higher water levels. Beginning in the 1960s, high agricultural water demand resulted in rapid declines in lake water level, with subsequent increases of lake water salinity, as evidenced by enhanced sodium concentration in lake core sediments. During this period, anthropogenic activity also enhanced the intensity of weathering and the denudation of the Ebinur watershed.</p>
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<article-id pub-id-type="pmc">4866693</article-id>
<article-id pub-id-type="doi">10.1371/journal.pone.0155819</article-id>
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<article-title>Geochemical Responses to Anthropogenic and Natural Influences in Ebinur Lake Sediments of Arid Northwest China</article-title>
<alt-title alt-title-type="running-head">Geochemical Responses to Anthropogenic Influences in Northwest China</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<contrib-id authenticated="true" contrib-id-type="orcid">http://orcid.org/0000-0002-8233-8640</contrib-id>
<name>
<surname>Ma</surname>
<given-names>Long</given-names>
</name>
<xref ref-type="aff" rid="aff001">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff003">
<sup>3</sup>
</xref>
<xref ref-type="corresp" rid="cor001">*</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Wu</surname>
<given-names>Jinglu</given-names>
</name>
<xref ref-type="aff" rid="aff002">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff003">
<sup>3</sup>
</xref>
<xref ref-type="corresp" rid="cor001">*</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Abuduwaili</surname>
<given-names>Jilili</given-names>
</name>
<xref ref-type="aff" rid="aff001">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff003">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Liu</surname>
<given-names>Wen</given-names>
</name>
<xref ref-type="aff" rid="aff001">
<sup>1</sup>
</xref>
</contrib>
</contrib-group>
<aff id="aff001">
<label>1</label>
<addr-line>State Key Laboratory of Desert and Oasis Ecology, Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi, China</addr-line>
</aff>
<aff id="aff002">
<label>2</label>
<addr-line>State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing, China</addr-line>
</aff>
<aff id="aff003">
<label>3</label>
<addr-line>CAS Research Center for Ecology and Environment of Central Asia, Urumqi, China</addr-line>
</aff>
<contrib-group>
<contrib contrib-type="editor">
<name>
<surname>Zhu</surname>
<given-names>Liping</given-names>
</name>
<role>Editor</role>
<xref ref-type="aff" rid="edit1"></xref>
</contrib>
</contrib-group>
<aff id="edit1">
<addr-line>Institute of Tibetan Plateau Research, CHINA</addr-line>
</aff>
<author-notes>
<fn fn-type="conflict" id="coi001">
<p>
<bold>Competing Interests: </bold>
The authors have declared that no competing interests exist.</p>
</fn>
<fn fn-type="con" id="contrib001">
<p>Conceived and designed the experiments: LM JW. Performed the experiments: LM WL. Analyzed the data: LM WL. Contributed reagents/materials/analysis tools: JW JA. Wrote the paper: LM JW WL JA.</p>
</fn>
<corresp id="cor001">* E-mail:
<email>malong@ms.xjb.ac.cn</email>
(LM);
<email>w.jinglu@niglas.ac.cn</email>
(JW)</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>13</day>
<month>5</month>
<year>2016</year>
</pub-date>
<pub-date pub-type="collection">
<year>2016</year>
</pub-date>
<volume>11</volume>
<issue>5</issue>
<elocation-id>e0155819</elocation-id>
<history>
<date date-type="received">
<day>1</day>
<month>11</month>
<year>2015</year>
</date>
<date date-type="accepted">
<day>4</day>
<month>5</month>
<year>2016</year>
</date>
</history>
<permissions>
<copyright-statement>© 2016 Ma et al</copyright-statement>
<copyright-year>2016</copyright-year>
<copyright-holder>Ma et al</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<license-p>This is an open access article distributed under the terms of the
<ext-link ext-link-type="uri" xlink:href="http://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License</ext-link>
, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.</license-p>
</license>
</permissions>
<self-uri content-type="pdf" xlink:href="pone.0155819.pdf"></self-uri>
<abstract>
<p>Geochemical concentrations were extracted for a short sediment core from Ebinur Lake, located in arid northwest China, and mathematical methods were used to demonstrate the complex pattern of the geochemical anomalies resulting from the temporal changes in natural and anthropogenic forces on the lake sediments. The first element assemblage (C1) (aluminum, potassium, iron, magnesium, beryllium, etc.) was predominantly terrigenous; among the assemblage, total phosphorus and titanium were generally consistent with aluminum except with regards to their surface sequences, which inferred the differences of source regions for terrigenous detrital material led to this change around ca. 2000AD. The second assemblage (C2) (calcium and strontium) was found to have a negative relationship with aluminum through a cluster analysis. The third assemblage (C3) included sodium and magnesium, which were influenced by the underwater lake environment and deposited in the Ebinur depression. The concentration ratio of C1/(C1+C2) was used as an indicator for denudation amount of detrital materials, which was supported by the values of magnetic susceptibility. The enrichment factors for heavy metals suggested that the influence of human activities on heavy-metal enrichment in Ebinur Lake region was not severe over the past century. Prior to the 1960s, geochemical indicators suggested a stable lacustrine environment with higher water levels. Beginning in the 1960s, high agricultural water demand resulted in rapid declines in lake water level, with subsequent increases of lake water salinity, as evidenced by enhanced sodium concentration in lake core sediments. During this period, anthropogenic activity also enhanced the intensity of weathering and the denudation of the Ebinur watershed.</p>
</abstract>
<funding-group>
<award-group id="award001">
<funding-source>
<institution>National Basic Research Program of China</institution>
</funding-source>
<award-id>2012CB956100</award-id>
<principal-award-recipient>
<name>
<surname>Wu</surname>
<given-names>Jinglu</given-names>
</name>
</principal-award-recipient>
</award-group>
<award-group id="award002">
<funding-source>
<institution>West Light Foundation of The Chinese Academy of Sciences</institution>
</funding-source>
<award-id>2015-XBQN-B-18</award-id>
<principal-award-recipient>
<name>
<surname>Liu</surname>
<given-names>Wen</given-names>
</name>
</principal-award-recipient>
</award-group>
<award-group id="award003">
<funding-source>
<institution-wrap>
<institution-id institution-id-type="funder-id">http://dx.doi.org/10.13039/501100001809</institution-id>
<institution>National Natural Science Foundation of China</institution>
</institution-wrap>
</funding-source>
<award-id>41471173</award-id>
<principal-award-recipient>
<contrib-id authenticated="true" contrib-id-type="orcid">http://orcid.org/0000-0002-8233-8640</contrib-id>
<name>
<surname>Ma</surname>
<given-names>Long</given-names>
</name>
</principal-award-recipient>
</award-group>
<award-group id="award004">
<funding-source>
<institution-wrap>
<institution-id institution-id-type="funder-id">http://dx.doi.org/10.13039/501100001809</institution-id>
<institution>National Natural Science Foundation of China</institution>
</institution-wrap>
</funding-source>
<award-id>41501221</award-id>
<principal-award-recipient>
<name>
<surname>Liu</surname>
<given-names>Wen</given-names>
</name>
</principal-award-recipient>
</award-group>
<funding-statement>This study was supported by the National Basic Research Program of China (No. 2012CB956100), West Light Foundation of the Chinese Academy of Sciences (2015-XBQN-B-18), and National Natural Science Foundation of China (41471173; 41501221). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.</funding-statement>
</funding-group>
<counts>
<fig-count count="5"></fig-count>
<table-count count="0"></table-count>
<page-count count="12"></page-count>
</counts>
<custom-meta-group>
<custom-meta id="data-availability">
<meta-name>Data Availability</meta-name>
<meta-value>All relevant data are within the paper and its Supporting Information files.</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
<notes>
<title>Data Availability</title>
<p>All relevant data are within the paper and its Supporting Information files.</p>
</notes>
</front>
<body>
<sec sec-type="intro" id="sec001">
<title>Introduction</title>
<p>Geochemical elements in lake sediments can be influenced by both natural and anthropogenic processes, and these element assemblages can be used to investigate the contributions of different forcing mechanisms to changes in sedimentary environments [
<xref rid="pone.0155819.ref001" ref-type="bibr">1</xref>
,
<xref rid="pone.0155819.ref002" ref-type="bibr">2</xref>
]. Based on studies examining long-term paleo-environmental changes in lacustrine environments, natural processes affect the transportation of geochemical elements from watersheds to lakes [
<xref rid="pone.0155819.ref003" ref-type="bibr">3</xref>
<xref rid="pone.0155819.ref005" ref-type="bibr">5</xref>
]. Over the past several decades, human activities have accelerated cycling of geochemical elements and resulted in elevated metal deliveries to water bodies [
<xref rid="pone.0155819.ref006" ref-type="bibr">6</xref>
<xref rid="pone.0155819.ref008" ref-type="bibr">8</xref>
]. Lacustrine sediments provide historic records of natural evolution and anthropogenic influences on lakes and their watersheds [
<xref rid="pone.0155819.ref009" ref-type="bibr">9</xref>
<xref rid="pone.0155819.ref012" ref-type="bibr">12</xref>
].</p>
<p>As part of the elemental composition of lake sediments, heavy metals are potentially toxic to ecological systems through the processes of bio-accumulation and bio-magnification [
<xref rid="pone.0155819.ref013" ref-type="bibr">13</xref>
<xref rid="pone.0155819.ref015" ref-type="bibr">15</xref>
]. It is therefore important to understand how climatic variations and anthropogenic activities influence the concentrations of geochemical constituents, especially heavy metals. Sediment cores can provide chronologies of metal concentrations in sedimentary sequences, and have been used to reveal human influences on heavy metal accumulation. However, the history of contamination in the arid environments of socially developing regions, particularly northwest China, has not been widely studied in comparison to developed regions.</p>
<p>Ebinur Lake is a closed lake situated in arid northwest China, which is sensitive to climatic and environmental changes [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
]. Using lake sediment cores, our goals are 1) to determine the concentrations of geochemical constituents that characterized the Ebinur Lake sediments prior to human activities, 2) to evaluate the enrichment trend of heavy metals and the degree of heavy-metal accumulation, and 3) to determine the possible geochemical sources that influenced metal concentrations in the Ebinur Lake sediments.</p>
<sec id="sec002">
<title>Study area</title>
<p>Ebinur Lake is a shallow, closed lake in northwest China (
<xref ref-type="fig" rid="pone.0155819.g001">Fig 1</xref>
), which belongs to the Ebinur Lake Wetland National Nature Reserve. It is also a rift lake, formed in the Himalayan orogeny, and deposited thick Quaternary unconsolidated sediments [
<xref rid="pone.0155819.ref017" ref-type="bibr">17</xref>
]. The lake drainage area is 50,321 km
<sup>2</sup>
, including 24,317 km
<sup>2</sup>
of mountainous terrain. Ala Mountain borders the lake in the north and northwest, Boer Tala Valley is to the west; the Jing River pluvial fan is to the south, and sand dunes around the Kuitun River are to the east [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
]. This lake receives surface runoff from the Boertala, Jing and Kuitun Rivers. The depth of the lake water averages 1.2 m, with a maximum depth of 3.5 m. Total dissolved solids in the lake range between 85 and 124 g/L
<sup>-1</sup>
. As part of a field investigation from 1987–1989 [
<xref rid="pone.0155819.ref018" ref-type="bibr">18</xref>
], Lake Ebinur was hydrochemically classified as a sulphate-sodium-II type lake. Based on a field survey conducted in 2009, it was shown that the major ions in Lake Ebinur were chlorine and sodium, and the hydrochemical classification subsequently changed from sulphate-sodium-II type to chloride-sodium-II type [
<xref rid="pone.0155819.ref019" ref-type="bibr">19</xref>
]. The annual total precipitation in Ebinur Lake watershed is approximately 95 mm, whereas annual evaporation totals for the watershed can reach 1315 mm [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
]. During the past half century, the economy in Ebinur Lake drainage has made rapid progress. It is an agriculture-based economy, and the small-scale enterprise becomes the main types of the secondary industry sector. From the economic data of Xinjiang economic statistics yearbooks [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
], gross domestic product (GDP) in Jinghe county (
<xref ref-type="fig" rid="pone.0155819.g001">Fig 1</xref>
) rose from about $ 410 000 in 1955 to $ 540 million in 2010. The primary industry increased from about $ 350 000 in 1955 to $ 300 million in 2010, and the secondary industry rose from about $10 000 in 1955 to $ 85 million in 2010. In the agriculture department, total sown area of farm crops enlarged from 5 720 ha in 1955 to 10
<sup>3</sup>
ha in 2010. The variation in the surface area of the lake is shown in
<xref ref-type="fig" rid="pone.0155819.g001">Fig 1</xref>
. The surface area of this lake was about 1070 km
<sup>2</sup>
in 1950, and then, experienced a rapid contraction. In 1972, the lake area decreased to 589 km
<sup>2</sup>
. In the late 1990s, Ebinur Lake started to expand; however, the lake area shrank sharply from 2004. The variation of Lake Ebinur area is jointly controlled by human activities and climate change. However, the human activity was mainly responsible for Ebinur Lake shrinking quickly over the past half century [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
].</p>
<fig id="pone.0155819.g001" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0155819.g001</object-id>
<label>Fig 1</label>
<caption>
<p>Sketch map of the geographic location of (a) the watershed of Ebinur Lake, (b) the sampling site, and (c) the Ebinur lake variation.</p>
</caption>
<graphic xlink:href="pone.0155819.g001"></graphic>
</fig>
</sec>
</sec>
<sec sec-type="materials|methods" id="sec003">
<title>Materials and Methods</title>
<p>In July 2011, with the support and permission of the Administrative Bureau of Ebinur Lake Wetland National Nature Reserve, a short sedimentary core (50-cm long) was obtained at the site (82.9603°E, 44.9113°N) with water depth of 2.4 m using a piston-percussion corer with a 60 mm inside-diameter Perspex tube. After collection, the core was vertically maintained and immediately sub-sampled at intervals of 1 cm. The age-depth relationship was determined by the dating of
<sup>210</sup>
Pb and
<sup>137</sup>
Cs, which were analyzed using an EG&G Ortec Gamma Spectrometer.</p>
<p>Bulk sediments in ~0.125 g were dried at 105°C, ground to 200-μ mesh size, and then, they were totally digested with HF-HNO
<sub>3</sub>
-HClO
<sub>4</sub>
in a Berghof MWS-3 microwave digester, and prepared for the determination of elements with a Leeman Labs Profile Inductively Coupled Plasma Spectrometer (ICP-AES). The relative error was determined to be less than 5%. National Standard Reference material (GBW0731) was used to determine major and minor element standards. Magnetic susceptibility (MS) was measured using a Bartington MS2 susceptibility meter (Bartington Instruments, Oxford, England). Samples were pretreated with 10–20 ml of 30% H
<sub>2</sub>
O
<sub>2</sub>
to remove organic matter and with 10 ml of 10% HCl to remove carbonates, prior to particle size analysis. Particle size was determined with a Malvern Mastersizer 2000 analyzer with a measurement range of 0.02–2000 μm. The Mastersizer 2000 automatically determines size fractions with a measurement precision <1%. Carbonate content was determined by the volumetric calcimeter method [
<xref rid="pone.0155819.ref020" ref-type="bibr">20</xref>
], and the error in carbonate measurement was less than 5%. The above analyses were conducted in the State Key Laboratory of Lake Science and Environment, Chinese Academy of Sciences.</p>
<p>Correlation analysis was used to analyze the interrelationship and to assess geochemical associations among the major and trace elements [
<xref rid="pone.0155819.ref021" ref-type="bibr">21</xref>
]. Hierarchical cluster analysis (HCA) was used to reveal the similarity/dissimilarity between variables [
<xref rid="pone.0155819.ref022" ref-type="bibr">22</xref>
,
<xref rid="pone.0155819.ref023" ref-type="bibr">23</xref>
]. The element concentrations were standardized using z-score transformation, which converts all elements to a common scale. Z-scores can be calculated from the following formula, z = (X - μ) / σ, where z is the z-score, X is the value of the element, μ is the mean value, and σ is the standard deviation [
<xref rid="pone.0155819.ref024" ref-type="bibr">24</xref>
]. Pearson correlation distance was calculated and the weighted pair-group method using centroid approach (median linkage) was selected for cluster analysis. The above statistical analyses were conducted using the SPSS 15.0 for Windows.</p>
<p>Enrichment factors (EFs) were calculated as the elemental content to background content ratio [
<xref rid="pone.0155819.ref006" ref-type="bibr">6</xref>
,
<xref rid="pone.0155819.ref025" ref-type="bibr">25</xref>
]. In this work, background content was quantified by determining the average content in the bottom 10 cm of the core sample. Aluminum (Al) is usually chosen as a reference element to distinguish from anthropogenically introduced elements [
<xref rid="pone.0155819.ref021" ref-type="bibr">21</xref>
,
<xref rid="pone.0155819.ref026" ref-type="bibr">26</xref>
]. This is because aluminum is typically of terrigenous origin, and is geochemically stable in supergene environments [
<xref rid="pone.0155819.ref027" ref-type="bibr">27</xref>
,
<xref rid="pone.0155819.ref028" ref-type="bibr">28</xref>
]. Therefore, the EFs of the geochemical element were calculated using the equation, EF
<sub>s</sub>
= (C
<sub>GE</sub>
/C
<sub>Al</sub>
)/(B
<sub>GE</sub>
/B
<sub>Al</sub>
), where C
<sub>GE</sub>
was the elemental concentration in the core sediment; C
<sub>Al</sub>
was the aluminum content in the core sediment; B
<sub>GE</sub>
was the elemental concentration of natural background, and the B
<sub>Al</sub>
was the aluminum content in the natural background.</p>
</sec>
<sec sec-type="results" id="sec004">
<title>Results</title>
<p>The vertical distribution of
<sup>210</sup>
Pb and
<sup>137</sup>
Cs is shown in
<xref ref-type="fig" rid="pone.0155819.g002">Fig 2</xref>
. Based on the study findings,
<sup>137</sup>
Cs accumulation began at 25 cm depth with specific activity value of zero in 1954, with peak concentrations measured at 20 cm depth in 1963, corresponding to the fallout maximum from nuclear weapons testing at this time [
<xref rid="pone.0155819.ref029" ref-type="bibr">29</xref>
,
<xref rid="pone.0155819.ref030" ref-type="bibr">30</xref>
]. The unsupported
<sup>210</sup>
Pb activity (
<sup>210</sup>
Pb
<sub>ex</sub>
) decreased to zero at close to 49 cm depth (
<xref ref-type="fig" rid="pone.0155819.g002">Fig 2</xref>
). A constant rate of supply model [
<xref rid="pone.0155819.ref030" ref-type="bibr">30</xref>
] was used to calculate the date of samples, which was consistent with the
<sup>137</sup>
Cs chronology.</p>
<fig id="pone.0155819.g002" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0155819.g002</object-id>
<label>Fig 2</label>
<caption>
<title>The specific activity of
<sup>137</sup>
Cs,
<sup>226</sup>
Ra and total
<sup>210</sup>
Pb activity in Ebinur Lake core sediment and the profiles for elemental concentrations in Ebinur Lake core sediment.</title>
</caption>
<graphic xlink:href="pone.0155819.g002"></graphic>
</fig>
<p>The average contents of the fractions of <4 μm, 4–16 μm, 16–64 μm and > 64μm are 31%, 47%, 21% and 1%, respectively (
<xref ref-type="fig" rid="pone.0155819.g002">Fig 2</xref>
). The Ebinur Lake core sediments are composed of relatively uniform fine-grained materials. The elemental content in Ebinur Lake sediments are presented in
<xref ref-type="supplementary-material" rid="pone.0155819.s001">S1 Table</xref>
and
<xref ref-type="fig" rid="pone.0155819.g002">Fig 2</xref>
. The HCA dendrogram categorizes these elements into several branches (
<xref ref-type="fig" rid="pone.0155819.g003">Fig 3</xref>
). The elements within a sub-cluster have more similarity than those not in sub-clusters. The results show that: (1) most elements, including Al, potassium (K), beryllium (Be), barium (Ba), titanium (Ti), sodium (Na), magnesium (Mg), zinc (Zn), vanadium (V), lead (Pb), cobalt (Co), chromium (Cr), nickel (Ni) and iron (Fe), had a similar distribution pattern which generally increased with depth. The observed time evolution of the zonal anomalies illustrates the apparently increase from the 1950s onwards. (2) Na and Mg had a negative correlation with Al. (3) In general, calcium (Ca) and strontium (Sr) also increased with depth, similar to Al; however, the wave direction of Ca and Sr was opposite to that of Al. (4) The trends of total phosphorus (P) and Ti were similar to Al; however at the sediment surface the trend of these elements was inconsistent with that of Al.</p>
<fig id="pone.0155819.g003" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0155819.g003</object-id>
<label>Fig 3</label>
<caption>
<title>Hierarchical clustering of geochemical elements in the Ebinur Lake sediment core.</title>
</caption>
<graphic xlink:href="pone.0155819.g003"></graphic>
</fig>
</sec>
<sec sec-type="conclusions" id="sec005">
<title>Discussion</title>
<p>Various factors influenced the distribution and accumulation of geochemical elements, including sedimentary texture, mineral composition, oxidation/reduction state, adsorption/desorption processes and physical transportation [
<xref rid="pone.0155819.ref013" ref-type="bibr">13</xref>
,
<xref rid="pone.0155819.ref031" ref-type="bibr">31</xref>
<xref rid="pone.0155819.ref033" ref-type="bibr">33</xref>
]. Profiles of representative elements are generally used to characterize the depositional environment [
<xref rid="pone.0155819.ref034" ref-type="bibr">34</xref>
,
<xref rid="pone.0155819.ref035" ref-type="bibr">35</xref>
].</p>
<p>From the dendrogram of HCA (
<xref ref-type="fig" rid="pone.0155819.g003">Fig 3</xref>
), we found three primary element assemblages. The first element assemblage (C1) included Al, K, Fe, Mg, Be, etc. The positive relationships among the elements Al, K, Mg, Fe, and manganese (Mn) were observed with relatively high correlation coefficient (
<xref ref-type="supplementary-material" rid="pone.0155819.s002">S2 Table</xref>
), which suggests the same origin for them. Aluminum is extremely immobile, usually held in the lattice of aluminosilicate minerals and regarded as a typical lithogenic element [
<xref rid="pone.0155819.ref036" ref-type="bibr">36</xref>
]. Al and K are major constituents of common silicate minerals and originated from the weathering release of parent materials in the local bedrock [
<xref rid="pone.0155819.ref037" ref-type="bibr">37</xref>
]. The EFs for heavy metals and P were used to identify and quantify anthropogenic interference; however, the EFs showed inconspicuous variations with a mean value of approximately one (
<xref ref-type="fig" rid="pone.0155819.g004">Fig 4</xref>
). This suggests that the influences of human activity on the enrichments of heavy metals and P in this region was not severe over the past century. It must be noted, however, that P and Ti were strongly correlated (r = 0.811, p<0.01) (
<xref ref-type="supplementary-material" rid="pone.0155819.s002">S2 Table</xref>
). From the
<xref ref-type="fig" rid="pone.0155819.g004">Fig 4</xref>
, from ca. 2000 AD, we observed a relatively significant variation for the EFs of Ti and P, however, the EFs for both of them didn’t exceed to 1.24. The results inferred the differences of source regions for terrigenous detrital material led to this change around ca. 2000AD.</p>
<fig id="pone.0155819.g004" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0155819.g004</object-id>
<label>Fig 4</label>
<caption>
<title>Representative enrichment factors for major and trace elements in the Ebinur Lake sediment core.</title>
</caption>
<graphic xlink:href="pone.0155819.g004"></graphic>
</fig>
<p>The second assemblage (C2,
<xref ref-type="fig" rid="pone.0155819.g003">Fig 3</xref>
) (Ca and Sr) was found to have a strong positive relationship (r = 0.928, p<0.001). Due to similar ionic radii (r
<sub>Sr</sub>
= 0.113 nm vs. r
<sub>Ca</sub>
= 0.099 nm) and charge [
<xref rid="pone.0155819.ref038" ref-type="bibr">38</xref>
], the element assemblage of Ca and Sr is believed to behave similarly with each other, with Sr typically found in calcium-bearing minerals such as plagioclase [
<xref rid="pone.0155819.ref039" ref-type="bibr">39</xref>
]. On the whole, all the elements in first and second assemblages had downward trends, which were opposite to the ones in third group, but no significant correlation was present between the first and second assemblages. However, after conduct a detrend analysis with subtracting the trend estimated from the linear regression model, there was a strong negative correlation between Ca and Al (r = -0.592, p<0.001), suggesting a dissolved terrigenous bicarbonate input, which was deposited in the lake as solid carbonate.</p>
<p>The third element assemblage (Na and Mg) consisted of autogenetic evaporative minerals that were influenced by the lacustrine environment and deposited in the Ebinur depression. In the process of arid closed lake evolution, the dominated sedimentary minerals were following the carbonates–sulfates—chlorides sequence [
<xref rid="pone.0155819.ref040" ref-type="bibr">40</xref>
]. In the earlier evolutionary stage, Calcium-magnesium carbonates reign supreme over the mineral sedimentation. Meanwhile, natron (Na
<sub>2</sub>
CO
<sub>3</sub>
•10H
<sub>2</sub>
O) and trona(Na
<sub>2</sub>
CO
<sub>3</sub>
•NaHCO
<sub>3</sub>
•2H
<sub>2</sub>
O) will be deposited with a small amount. In the latter period, the lake water salinity increases as the depth decreased, sulfates (e.g. Na
<sub>2</sub>
SO
<sub>4</sub>
•10H
<sub>2</sub>
O, Na
<sub>2</sub>
SO
<sub>4</sub>
) with greater solubility will be precipitate before halite can form [
<xref rid="pone.0155819.ref040" ref-type="bibr">40</xref>
]. From the carbonate content of Ebinur Lake sediments (
<xref ref-type="fig" rid="pone.0155819.g005">Fig 5</xref>
), although it shows a trend of temporal decrease, the carbonate content in lake sediment fluctuated in a narrow range, which indicated that Ebinur Lake had already undergone the carbonate evolutionary stage since 1880 AD. In recent years, the shrinking trend of Ebinur Lake exacerbated. Sodium can be considered as a water level indicator. Subsequently, as lake levels dropped, salinity concentrations measured in the sediment core increased. A mass of sodium salt precipitated from aqueous solution, which induced the concentration of Na had the opposite trend with the lake level. The third assemblage (C3) included sodium and magnesium, were influenced by the underwater lake environment and deposited in the Ebinur depression.</p>
<fig id="pone.0155819.g005" orientation="portrait" position="float">
<object-id pub-id-type="doi">10.1371/journal.pone.0155819.g005</object-id>
<label>Fig 5</label>
<caption>
<title>Geochemical evolution of the Ebinur Lake sediment core compared with the lake surface area change with axis scale in reverse, and meteorological data in the surrounding area.</title>
</caption>
<graphic xlink:href="pone.0155819.g005"></graphic>
</fig>
<p>
<xref ref-type="fig" rid="pone.0155819.g005">Fig 5</xref>
shows the climatic data around the Ebinur Lake. The data of annual total precipitation (ATP) from 1955–2013 at Jinghe weather station (location showed in
<xref ref-type="fig" rid="pone.0155819.g001">Fig 1</xref>
) were provided by the National Meteorological Administration of China (
<ext-link ext-link-type="uri" xlink:href="http://data.cma.cn/">http://data.cma.cn</ext-link>
), and the ATP data at Ucharal station (E 80.93°, N 46.17°) are from the reference [
<xref rid="pone.0155819.ref041" ref-type="bibr">41</xref>
]. There are no sudden changes around 1960s, which inferred that the climate variation was not enough to induce the significant change in geochemical compositions of Ebinur Lake core sediments. Corresponding to local economic development, an increase in agricultural water demand began in the 1960s, the Ebinur Lake experienced a rapid contraction due to the sustained increase of irrigation water requirements and decreased annual precipitations. In the late 1990s, Ebinur Lake area expanded due to the reduced agricultural water consumption with increased annual precipitations, and the lake area peaks to 903 km
<sup>2</sup>
in 2003[
<xref rid="pone.0155819.ref042" ref-type="bibr">42</xref>
,
<xref rid="pone.0155819.ref043" ref-type="bibr">43</xref>
]. Nevertheless, the Ebinur Lake shrank sharply from 2004 with the combination of reduced rainfall and increased farmland under irrigation [
<xref rid="pone.0155819.ref044" ref-type="bibr">44</xref>
]. Prior to the 1960s, Na was present at relatively constant lower values, suggesting a stable lacustrine environment with higher water levels. With lake surface area experiencing a constantly change, the Na concentration in lake sediments varied accordingly (
<xref ref-type="fig" rid="pone.0155819.g005">Fig 5</xref>
).</p>
<p>Following the above-mentioned discussion, the first element assemblage (C1) was predominantly terrigenous clastic. The climate has the important influence on the chemical weathering process. Due to the extreme arid climate in Ebinur watershed with weak chemical weathering, the Al come from the earth surface are not in free state. Among these elements in the first assemblage, the K [
<xref rid="pone.0155819.ref045" ref-type="bibr">45</xref>
], Al [
<xref rid="pone.0155819.ref046" ref-type="bibr">46</xref>
], and Fe [
<xref rid="pone.0155819.ref047" ref-type="bibr">47</xref>
] have been commonly chosen as conservative lithogenic elements due to their immobile behavior during weathering and pedogenesis. For the dry climate dominated on the Ebinur Lake watershed, the earth surface materials experience the incipient stage of chemical weathering characterized by leaching of Ca and Na, and not reached the secondary process characterized by the removal of K [
<xref rid="pone.0155819.ref048" ref-type="bibr">48</xref>
]. The second assemblage (C2) was from dissolved terrigenous bicarbonate inputs, which was deposited in the lake as solid carbonate. And then, the concentration ratio of C1/(C1+C2) can be used as an indicator for denudation amount of detrital materials. Meanwhile, the interpretation for our ratio’s environmental meaning was supported by the values of magnetic susceptibility (
<xref ref-type="fig" rid="pone.0155819.g005">Fig 5</xref>
). Magnetic minerals in lake sediments mainly come from surface materials of lake watershed. Land reclamation and vegetation deterioration will increase surface erosion. Higher values of magnetic susceptibility over the past few decades indicate greater erosion in the lake drainage basin resulting from human activity [
<xref rid="pone.0155819.ref049" ref-type="bibr">49</xref>
]. In addition to falling lake water levels [
<xref rid="pone.0155819.ref016" ref-type="bibr">16</xref>
], eroded material was transported via fluvial processes and deposited in the lake, resulting in further intensification of clastic deposits. In general, the anthropogenic factors have influence on geochemical composition of lake sediments through the means of strengthening the lake area change and surface erosion.</p>
</sec>
<sec sec-type="conclusions" id="sec006">
<title>Conclusions</title>
<p>Using enrichment factors and multivariate statistical techniques, geochemical responses of Ebinur Lake sediments to anthropogenic and natural influences were determined. Most elements (including Al, K, Fe, Mg and Be) originated mainly from terrigenous detrital inputs. Ca and Sr originated mainly from terrigenous bicarbonate inputs and were deposited in the lake as solid carbonate. Na and Mg are autogenetic evaporative minerals that were influenced by the lacustrine environment and deposited in the Ebinur depression. The EFs for heavy metals and total phosphorus showed inconspicuous variations with a mean value of approximately one, which suggested that the influences of human activity on heavy metal accumulation in this region were not severe over the past century.</p>
<p>Since the 1960s, agricultural water demand has increased considerably, and a rapid decrease in the lake water level was inferred from the higher sodium concentrations in the sediments closest to the surface. With an increase in the surface erosion rate due to human activities, fluvial activity deposited a considerable amount of eroded material in the lake, which increased the relative content of clastic deposits.</p>
<p>Overall, the intensity of human activity in this region was not severe over the past century, which referred to the influences on heavy metal enrichment. The human activities had the deep impacts on geochemical composition of lake sediments through the means of influencing the lake area change and surface erosion.</p>
</sec>
<sec sec-type="supplementary-material" id="sec007">
<title>Supporting Information</title>
<supplementary-material content-type="local-data" id="pone.0155819.s001">
<label>S1 Table</label>
<caption>
<title>The geochemical data of elemental compositions in Ebinur Lake sediments.</title>
<p>(PDF)</p>
</caption>
<media xlink:href="pone.0155819.s001.pdf">
<caption>
<p>Click here for additional data file.</p>
</caption>
</media>
</supplementary-material>
<supplementary-material content-type="local-data" id="pone.0155819.s002">
<label>S2 Table</label>
<caption>
<title>Pearson correlation matrix for element concentration in Ebinur Lake sediments.</title>
<p>(PDF)</p>
</caption>
<media xlink:href="pone.0155819.s002.pdf">
<caption>
<p>Click here for additional data file.</p>
</caption>
</media>
</supplementary-material>
</sec>
</body>
<back>
<ack>
<p>This study was supported by the National Basic Research Program of China (No. 2012CB956100), West Light Foundation of the Chinese Academy of Sciences (2015-XBQN-B-18), and National Natural Science Foundation of China (41471173; 41501221), and. The authors gratefully acknowledge the support of the Youth Innovation Promotion Association CAS and the High-level Talents Introduction Project in Xinjiang Uygur Autonomous Region, China (2015)</p>
</ack>
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,
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<given-names>AF</given-names>
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,
<name>
<surname>Ohlendorf</surname>
<given-names>C</given-names>
</name>
,
<name>
<surname>Sturm</surname>
<given-names>M</given-names>
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