<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">GEP</journal-id><journal-title-group><journal-title>Journal of Geoscience and Environment Protection</journal-title></journal-title-group><issn pub-type="epub">2327-4336</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/gep.2015.310006</article-id><article-id pub-id-type="publisher-id">GEP-62050</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Hydrological Mann-Kendal Multivariate Trends Analysis in the Upper Yangtze River Basin
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Lei</surname><given-names>Ye</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Jianzhong</surname><given-names>Zhou</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Xiaofan</surname><given-names>Zeng</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Muhammad</surname><given-names>Tayyab</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>College of Hydropower and Information Engineering, Huazhong University of Science and Technology, Wuhan, China</addr-line></aff><pub-date pub-type="epub"><day>18</day><month>12</month><year>2015</year></pub-date><volume>03</volume><issue>10</issue><fpage>34</fpage><lpage>39</lpage><history><date date-type="received"><day>November</day>	<month>2015</month></date ></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
   Hydrological events should be described through several correlated variables, so multivariate HFA has gained popularity and become an active research field during recent years. However, at present multivariate HFA mainly focuses directly on fitting the frequency distribution without confirming whether the assumptions are satisfied. Neglecting testing these assumptions could get severely wrong frequency distribution. This paper uses multivariate Mann-Kendal testing to detect the multivariate trends of annual flood peak and annual maximum 15 day volume for four control hydrological stations in the Upper Yangtze River Basin. Results indicate that multivariate test could detect the trends of joint variables, whereas univariate tests can only detect the univariate trends. Therefore, it is recommended to jointly apply univariate and multivariate trend tests to capture all the existing trends. 
 
</p></abstract><kwd-group><kwd>Trend Analysis</kwd><kwd> Multivariate Mann-Kendal Test</kwd><kwd> Hydrological Variable</kwd><kwd> Upper Yangtze River Basin</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Hydrological frequency analysis (HFA), foundation of the hydraulic engineering design and water resources management, is mainly used for purposes of improving hydrological extreme events prediction. Researchers can estimate possible hydrological variable value of certain frequency through analyzing frequency distribution of the hydrological variable. [<xref ref-type="bibr" rid="scirp.62050-ref1">1</xref>] summarized the researches of HFA and concluded that HFA is composed of four main steps: 1) carrying out the descriptive and exploratory analysis and outlier detection, 2) checking the basic assumptions including stationarity, homogeneity and independence, 3) selecting a probability distribution model and estimating the parameters, and 4) risk evaluation and analysis. One of the most important steps is confirming whether the stationarity assumption of the hydrological variable is satisfied, which is the statistical property of hydrological variable remains the same in the past, present and future.</p><p>For univariate HFA, extensively studies have been devoted to treat the above steps [<xref ref-type="bibr" rid="scirp.62050-ref2">2</xref>]-[<xref ref-type="bibr" rid="scirp.62050-ref4">4</xref>]. Hydrological events generally need be described through several correlated characteristics, such as volume, peak for floods. The importance and justification of jointly considering all variables characterizing an event has been realized by the researchers and it has become an active and attractive research area in hydrology [<xref ref-type="bibr" rid="scirp.62050-ref5">5</xref>]. However, very limited attention has been paid to step b for multivariate HFA.</p><p>In fact, existing research has shown that, due to the impact of climate change and human activities, the physical mechanism of rainfall runoff process has changed a lot, the hydrological stationarity assumption has been challenged. Therefore, before step c it is necessary to apply trend analysis to the hydrological variables of interest. If the hydrological variables have significant tendency, researchers should use nonstationary HFA method, otherwise can go to step c directly.</p><p>For hydrological multivariate frequency analysis, if one only uses trend testing for each variable separately, he/she can only test whether there exists trend for the single variable and can’t check out whether there exists changing trend of the correlation between joint variables. Ignoring the testing step in multivariate HFA may lead to very inaccurate or wrong results and hence to inappropriate decisions. Therefore, this paper introduces the widely used multivariate trend testing method in water quality data to the multivariate hydrological events in order to test the stationarity of joint variables prior to selecting a probability distribution model and estimating the parameters.</p></sec><sec id="s2"><title>2. Methodologies</title><p>For the univariate trend analysis, Mann-Kendal test [<xref ref-type="bibr" rid="scirp.62050-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.62050-ref7">7</xref>] is the most widely used nonparametric hydro-me- teorological time series method and is highly recommended by the World Meteorological Organization as standard nonparametric procedures when testing for trend [<xref ref-type="bibr" rid="scirp.62050-ref8">8</xref>]. MK statistical test can detect any kind of monotonic trend, whether of linear or nonlinear behavior, and it is also not influenced by the interference of a few outliers, thus making it suitable for hydrological data which is usually not normal distributed. For multivariate trend analysis, this paper applies multivariate MK trend analysis to test whether there exist significant trends in joint variables.</p><sec id="s2_1"><title>2.1. Univariate Mann-Kendal Test</title><p>First the MK statistic S is calculated as:</p><disp-formula id="scirp.62050-formula26"><label>(1)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x5.png"  xlink:type="simple"/></disp-formula><p>where X<sub>j</sub> and X<sub>i</sub> are the hydrological data values in years j and i, respectively, with j &gt; i, N is the total number of years and sgn() is the sign function:</p><p>sgn(X) = 1 if X &gt; 0; =0 if X = 0; =−1 if X &lt; 0 (2)</p><p>The statistics S is approximately normally distributed, with mean zero and variance given by:</p><p>E[S] = 0 (3)</p><p>Var(S) = N(N − 1)(2N + 5)/18 (4)</p><p>The standard normal variable Z is then formulated as:</p><disp-formula id="scirp.62050-formula27"><label>(5)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x6.png"  xlink:type="simple"/></disp-formula><p>If Z is positive, the hydrological time series has an increase trend, otherwise it has a decrease trend. The null hypothesis is rejected at significance level α if |Z| &gt; Z<sub>1-α/2</sub>, indicating the hydrological time series has significant changing trend.</p></sec><sec id="s2_2"><title>2.2. Multivariate Mann-Kendal Test</title><p>[<xref ref-type="bibr" rid="scirp.62050-ref9">9</xref>] developed an improved the multivariate nonparametric MK test for trend detection in water quality time series, as the extension of univariable MK test. [<xref ref-type="bibr" rid="scirp.62050-ref1">1</xref>] firstly introduced the multivariate MK test to hydrology field and summarized the procedures of multivariate MK test calculation.</p><p>First univariate MK test statistic is calculated according to Equation (1) for each variable, then constructing a vector using these univariate MK test statistic as:</p><p>S<sub>multi</sub> = [S<sub>1</sub>, S<sub>2</sub>,&#188;, S<sub>d</sub>] (6)</p><p>where d is the total number of joint variables. S<sub>multi</sub> is asymptotically d-dimensional normal with zero mean and covariance matrix C<sub>M</sub> = (c<sub>u</sub><sub>,v</sub>)<sub> u,v=1,</sub><sub>&#188;,d</sub>, with c<sub>u</sub><sub>,v</sub> = cov(S<sub>u</sub>, S<sub>v</sub>). The covariance matrix is calculated as:</p><disp-formula id="scirp.62050-formula28"><label>(7)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x7.png"  xlink:type="simple"/></disp-formula><p>in which:</p><disp-formula id="scirp.62050-formula29"><label>(8)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x8.png"  xlink:type="simple"/></disp-formula><p>when u = v, the variance is calculated according to Equation (4).</p><sec id="s2_2_1"><title>2.2.1. The Covariance Inversion Test</title><p>The first multivariate extension of the MK test was proposed by [<xref ref-type="bibr" rid="scirp.62050-ref10">10</xref>]. Here we call it the Covariance Inversion Test (CIT) as proposed by [<xref ref-type="bibr" rid="scirp.62050-ref9">9</xref>]. C<sub>M</sub><sup>−1</sup> is the inverse matrix of C<sub>M</sub> when it has full rank, otherwise a generalized inverse of C<sub>M</sub>. The test statistic D is given as:</p><disp-formula id="scirp.62050-formula30"><label>(9)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x9.png"  xlink:type="simple"/></disp-formula><p>D is asymptotically c<sup>2</sup>(q)-distributed in which q is the rank of C<sub>M</sub>. if the value of D exceeds the significance level according to the c<sup>2</sup>(q) distribution quantile, the joint variables are considered have a significant trend.</p></sec><sec id="s2_2_2"><title>2.2.2. The Covariance Sum Test</title><p>[<xref ref-type="bibr" rid="scirp.62050-ref11">11</xref>] developed a generalization of the multivariate MK test similar to (9) in a model which assumed independent seasons, by considering each season as a variable and thus obtaining a multivariate setting [<xref ref-type="bibr" rid="scirp.62050-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.62050-ref9">9</xref>] call this modified seasonal MK test the Covariance Sum Test (CST), as it is referred to in this paper. The test statistic H is then:</p><disp-formula id="scirp.62050-formula31"><label>(10)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x10.png"  xlink:type="simple"/></disp-formula><p>The statistic H is approximately normally distributed, with mean zero and variance given by:</p><disp-formula id="scirp.62050-formula32"><label>(11)</label><graphic position="anchor" xlink:href="http://html.scirp.org/file/62050x11.png"  xlink:type="simple"/></disp-formula><p>in which c<sub>u</sub><sub>,v</sub> is calculated according to Equation (7). For a given significant level, the covariance sum test is the same as the univariate MK test, constructing standard normal variable and then comparing the value with the threshold value.</p></sec></sec></sec><sec id="s3"><title>3. Case Study</title><sec id="s3_1"><title>3.1. Study Area and Data</title><p>This paper analyzes the annual flood peak (Q) and annual maximum 15 d flood volume (V) multivariate trend in the Upper Yangtze River Basin by taking four control hydrological stations (Pingshan, Lijiawan, Beibei and Yichang stations) into consideration. Data series of flood peak and flood volume (V) are available for the period 1955-2005 corresponding to the four stations. <xref ref-type="fig" rid="fig1">Figure 1</xref> presents the locations of the upper Yangtze River basin and the control hydrological stations</p></sec><sec id="s3_2"><title>3.2. Univariate MK Test Analysis</title><p>Time series of the two hydrological variables Q and V corresponding to the selected four hydrological stations</p><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> Locations of the upper Yangtze River basin and the controlling hydrological stations</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x12.png"/></fig><p>for the period 1955-2005 altogether 8 time series data are plotted in <xref ref-type="fig" rid="fig2">Figure 2</xref>. <xref ref-type="fig" rid="fig2">Figure 2</xref> also presents the linear regression line of the time series data.</p><p>According to the univariate MK test described in Section 2.1, we applied the trend analysis for the Q and V corresponding to the four stations. Given the significant level α = 0.05, the threshold value is 1.96. When the absolute Z value for the variable is higher than 1.96, the variable has a significant changing trend. The results are shown in <xref ref-type="table" rid="table1">Table 1</xref>.</p><p>It can be seen from <xref ref-type="table" rid="table1">Table 1</xref> that the absolute Z values of both the Q and V for Pingshan and Yichang stations did not reach 1.96, indicating no significant changing trend for the both variables. The absolute Z value of only V for Beibei station passed 1.96 and meanwhile the Z value was negative, which showed significant decreasing trend for V. For Lijiawan station, Z values for both Q and V passed the threshold value, indicating significant decreasing trend for both variables.</p></sec><sec id="s3_3"><title>3.3. Multivariate MK Test Analysis</title><p>According to the multivariate MK test described in Section 2.3, we applied the CIT and CST trend analysis for the joint variables (Q and V) corresponding to the four stations. Given the significant level α = 0.05, when the absolute Z value for the variable is higher than threshold, the joint variables have a significant changing trend. The results are presented in <xref ref-type="table" rid="table2">Table 2</xref>.</p><p>It can be seen from <xref ref-type="table" rid="table2">Table 2</xref> that both the CIT and CST values did not pass the threshold values for Pingshan and Yichang stations, indicating no significant changing trend for the joint variables. For Beibei station, the CIT value passed threshold and the CST value did not pass the threshold. The differences generated by two different multivariate MK test methods encourage us to combine univariate test results to judge the change trend of Beibei station. Both multivariate tests detected significant decreasing bivariate trend for Lijiawan station.</p></sec><sec id="s3_4"><title>3.4. Discussion</title><p>From the results of univariate and multivariate MK test we can find that the no significant change trend existed in annual flood peak, annual maximum 15 d flood volume and the joint variables for Pingshan and Yichang stations. Therefore, traditional HFA method could be used to fit the frequency distribution function of annual flood peak, annual maximum 15 d flood volume and the joint variables.</p><p>The annual maximum 15 d flood volume for Beibei station has significant decreasing trend while no significant trend was detected for annual flood peak. Meanwhile, only the CIT test detected significant change trend for joint variables, which indicated that 15 d flood volume dominated the changing trend of multivariate, but the correlation between annual flood peak and annual maximum 15 d flood volume has not changed significantly. Therefore, traditional HFA method could be used to fit the frequency distribution function of annual flood peak and the joint variables. As to annual maximum 15 d flood volume, nonstational HFA method should be applied.</p><p>The annual flood peak, annual maximum 15 d flood volume and the joint variables for Lijiawan station have</p><fig-group id="fig2"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Scatterplot of annual peak and maximum 15 day flood volume as well as linear regression line. (a) Peak from Pingshan station; (b) Volume from Pingshan station; (c) Peak from Lijiawan station; (d) Volume from Lijiawan station; (e) Peak from Beibei station; (f) Volume from Beibei station; (g) Peak from Yichang station; (h) Volume from Yichang station.</title></caption><fig id ="fig2_1"><label> (b)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x13.png"/></fig><fig id ="fig2_2"><label> (c)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x14.png"/></fig><fig id ="fig2_3"><label>(d)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x15.png"/></fig><fig id ="fig2_4"><label> (e)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x16.png"/></fig><fig id ="fig2_5"><label> (f)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x17.png"/></fig><fig id ="fig2_6"><label>(g)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x18.png"/></fig><fig id ="fig2_7"><label> (h)</label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x19.png"/></fig><fig id ="fig2_8"><label></label><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/62050x20.png"/></fig></fig-group><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Results of univariate MK testing</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Station</th><th align="center" valign="middle" >Variable</th><th align="center" valign="middle" >Z value</th></tr></thead><tr><td align="center" valign="middle"  rowspan="2"  >Pingshan</td><td align="center" valign="middle" >Q</td><td align="center" valign="middle" >0.93</td></tr><tr><td align="center" valign="middle" >V</td><td align="center" valign="middle" >1.13</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Lijiawan</td><td align="center" valign="middle" >Q</td><td align="center" valign="middle" >−3.14</td></tr><tr><td align="center" valign="middle" >V</td><td align="center" valign="middle" >−3.60</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Beibei</td><td align="center" valign="middle" >Q</td><td align="center" valign="middle" >−1.09</td></tr><tr><td align="center" valign="middle" >V</td><td align="center" valign="middle" >−2.28</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Yichang</td><td align="center" valign="middle" >Q</td><td align="center" valign="middle" >−1.01</td></tr><tr><td align="center" valign="middle" >V</td><td align="center" valign="middle" >−0.35</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Results of multivariate MK testing</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Stations</th><th align="center" valign="middle" >CIT</th><th align="center" valign="middle" >Threshold</th><th align="center" valign="middle" >CST</th><th align="center" valign="middle" >Threshold</th></tr></thead><tr><td align="center" valign="middle" >Pingshan</td><td align="center" valign="middle" >1.35</td><td align="center" valign="middle" >5.99</td><td align="center" valign="middle" >1.05</td><td align="center" valign="middle" >1.96</td></tr><tr><td align="center" valign="middle" >Lijiawan</td><td align="center" valign="middle" >13.03</td><td align="center" valign="middle" >5.99</td><td align="center" valign="middle" >−3.52</td><td align="center" valign="middle" >1.96</td></tr><tr><td align="center" valign="middle" >Beibei</td><td align="center" valign="middle" >7.73</td><td align="center" valign="middle" >5.99</td><td align="center" valign="middle" >−1.75</td><td align="center" valign="middle" >1.96</td></tr><tr><td align="center" valign="middle" >Yichang</td><td align="center" valign="middle" >1.35</td><td align="center" valign="middle" >5.99</td><td align="center" valign="middle" >−0.73</td><td align="center" valign="middle" >1.96</td></tr></tbody></table></table-wrap><p>been detected with significant decreasing trend. Therefore, nonstationarity should be taken into consideration when applying HFA to Lijiawan Station including the nonsationarity for univariate and the correlation (described by copula function).</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>This paper highlights the importance of testing for trend in multivariate hydrological event and briefly introduces two multivariate Mann-Kendal test methods. Four control hydrological stations in the Upper Yangtze River basin are selected for univariate and multivariate MK test for flood event. Results indicate that significant changing trends exist in some stations including univariate or multivariate trend. For the stations with only univariate trend, we could apply nonstational hydrological frequency analysis method, while still using the traditional copula function. But for the stations with both univariate and multivariate trends, we should consider the nonsationarity for the univariate and the correlation between the variables. These tests insure the validity of the HFA results and can help to guide the selection of the appropriate multivariate distribution (margins and copula).</p></sec><sec id="s5"><title>Acknowledgements</title><p>This work was supported by the State Key Program of National Natural Science of China (No. 51239004) and the National Natural Science Foundation of China (No. 51309105).</p></sec><sec id="s6"><title>Cite this paper</title><p>Lei Ye,Jianzhong Zhou,Xiaofan Zeng,Muhammad Tayyab, (2015) Hydrological Mann-Kendal Multivariate Trends Analysis in the Upper Yangtze River Basin. Journal of Geoscience and Environment Protection,03,34-39. doi: 10.4236/gep.2015.310006</p></sec><sec id="s7"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.62050-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Hirsch, R.M. and Slack, J.R. (1984) A Nonparametric Trend Test for Seasonal Data with Serial Dependence. 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