<?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">AJPS</journal-id><journal-title-group><journal-title>American Journal of Plant Sciences</journal-title></journal-title-group><issn pub-type="epub">2158-2742</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ajps.2017.89144</article-id><article-id pub-id-type="publisher-id">AJPS-78304</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Study on Diversity of Undergrowth Plant Community in Cibagou Nature Reserve
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Wei</surname><given-names>Wang</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Zhen</surname><given-names>Xing</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Wenbo</surname><given-names>Li</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>Xiaolin</surname><given-names>Yang</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Xizang Agriculture and Animal Husbandry College, Nyingchi, China</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>358336312@qq.com(WW)</email>;<email>470382094@qq.com(ZX)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>02</day><month>08</month><year>2017</year></pub-date><volume>08</volume><issue>09</issue><fpage>2149</fpage><lpage>2158</lpage><history><date date-type="received"><day>July</day>	<month>23,</month>	<year>2017</year></date><date date-type="rev-recd"><day>Accepted:</day>	<month>August</month>	<year>7,</year>	</date><date date-type="accepted"><day>August</day>	<month>10,</month>	<year>2017</year></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>
 
 
  The forest community diversity along the altitudinal gradient was analyzed in the Cibagou National Nature Reserve.
   
  Results showed that the forest types of Cibagou Gorge could be divided into six types: 
  &lt;i&gt;
  Castanopsis
   
  hystrix
  &lt;/i&gt;
   forest; 
  &lt;i&gt;
  camphor
  &lt;/i&gt;
   and 
  &lt;i&gt;
  acer
  &lt;/i&gt;
   
  mixed forest, blue Japanese oak broad-leaved mixed forest, blue Japanese oak forest, 
  &lt;i&gt;
  Populus
   
  simonii
  &lt;/i&gt;
   
  mixed forest; 
  &lt;i&gt;
  Quercus
   
  aquifolioides
  &lt;/i&gt;
   forest. The total coverage of undergrowth vegetation altitude was the lowest at 1749 m, only 30%, and plant species numbers in the sample was only 5. The total coverage of the plant was the highest at 2327 m altitude, the value was 95%, and the number of species in experiment plot was 14. The species richness of Margalef increased first and then decreased with the increase of altitude gradient at 1749 m to 2880 m, and the Shannon-wiener species diversity index increased, but the difference was not significant, Pielou species evenness and Sheldon species evenness index decreased first and then increased with altitude.
 
</p></abstract><kwd-group><kwd>Cibagou National Nature Reserve</kwd><kwd> Undergrowth Plant</kwd><kwd> Plant Diversity</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Study of biological diversity has long been the concern of the ecology. Plant species diversity and species richness is the comprehensive reflection of the uniform distribution, the difference can not only reflect the characteristics of plant communities in composition, structure, characteristics of spatial and time characteristics, but also reflect the plant community [<xref ref-type="bibr" rid="scirp.78304-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref2">2</xref>] . Forest is one of the most important ecological systems of land types, the species diversity and spatial pattern has long been one of the hotspots in the research, forest vegetation as an important part of forest ecosystem, plays an important role in maintaining the function of forest ecosystems, forest ecosystems to maintain their stability [<xref ref-type="bibr" rid="scirp.78304-ref3">3</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref5">5</xref>] .</p><p>Cibagou nature reserve is located in the southeast of Tibet, and was typical Alpine Canyon terrain. Because of its unique geographical location and well- preserved primary forest ecosystem characteristics, natural academic research has been attracted attention of researchers in different research field for long- time, but limited by traffic infrastructure, only few researches has been conducted over the past few decades, such aslarge animal species research [<xref ref-type="bibr" rid="scirp.78304-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref8">8</xref>] , insect classification research [<xref ref-type="bibr" rid="scirp.78304-ref9">9</xref>] , study on the Characteristics of Actinomycetes [<xref ref-type="bibr" rid="scirp.78304-ref10">10</xref>] . The investigation of plant resources was only carried out the part of plant species investigation, and the plant species community diversity research has not been conducted and analyzed. In this study, we investigated the vegetation under different elevation gradients in the Cibagou National Nature Reserve, and analyzed species diversity by the commonly analysis method. The aim was to provide some references for the comprehensive management of vegetation, the protection and development of biodiversity in Cibagou Nature Reserve.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Natural Geography Characters</title><p>The Cibagou Nature Reserve is located in the southeastern part of the Qinghai- Tibet Plateau in the southeastern part of the Tibet Autonomous Region. It is the intersection of the Himalayas and the Hengduan Mountains. The geographical coordinates are North latitude 28˚34' - 29˚07', East latitude 96˚52' - 97˚10', attitude 2500 m. Cibagou Nature Reserve area annual precipitation of more than 1000 mm, the average annual temperature was range 10˚C - 20˚C, the average annual humidity was range 60% to 70%, frost-free period was more than 200 d. Cibagou Nature Reserve is 76 km long from north to south and 33 km from east to west. The total area is about 1 &#215; 10<sup>5</sup> hm<sup>2</sup>. The forest area of 5 &#215; 10<sup>4</sup> hm<sup>2</sup>, forest coverage rate of up to 54.6%, the total forest volume was about 1.6 &#215; 10<sup>8</sup> m<sup>3</sup>. According to the forest (vegetation) type classification system can be divided into mountain subtropical evergreen broad-leaved forest, mountain deciduous broad- leaved forest, temperate hardwood evergreen oak forest, mountain temperate pine forest, mountain Berlin, subalpine deciduous coniferous forest, subalpine Dark coniferous forest, shrub, meadow.</p></sec><sec id="s2_2"><title>2.2. Research Methods</title><sec id="s2_2_1"><title>2.2.1. Sample Selection Settings, and Forest Plant Community Survey</title><p>The experiment was carried out in the Cibagou Nature Reserve in July 2016, walked about 30 km along the cibagou gully. The vicinity of the Ciba Ditch Ecological Protection Station is the end of the survey. In the case of obvious division of forest vegetation, select the appropriate sample to investigate, set two 10 m &#215; 10 m quadrats, respectively, in the sample four corners and the center set 2 m &#215; 2 m small sample (a total of 10) for the investigation of forest Under vegetation. The height, coverage, quantity and other information of understory plant vegetation were determined according to the types of plant species, and the important values of different plant species were calculated. The calculation formula was as follows [<xref ref-type="bibr" rid="scirp.78304-ref11">11</xref>] :</p><disp-formula id="scirp.78304-formula27"><graphic  xlink:href="http://html.scirp.org/file/11-2603297x2.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.78304-formula28"><graphic  xlink:href="http://html.scirp.org/file/11-2603297x3.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.78304-formula29"><graphic  xlink:href="http://html.scirp.org/file/11-2603297x4.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.78304-formula30"><graphic  xlink:href="http://html.scirp.org/file/11-2603297x5.png"  xlink:type="simple"/></disp-formula></sec><sec id="s2_2_2"><title>2.2.2. Plant Diversity Calculation Method</title><p>The plant community was systematically analyzed by species richness, species diversity and species uniformity.</p><p>Margalef Richness Index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x6.png" xlink:type="simple"/></inline-formula></p><p>Menhinick Richness Index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x7.png" xlink:type="simple"/></inline-formula></p><p>Shannon-wiener diversity index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x8.png" xlink:type="simple"/></inline-formula></p><p>Simpion diversity index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x9.png" xlink:type="simple"/></inline-formula></p><p>Pielou evenness index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x10.png" xlink:type="simple"/></inline-formula></p><p>Sheldon Evenness Index: <inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/11-2603297x11.png" xlink:type="simple"/></inline-formula></p><p>where S is the number of species in the sample, N is the number of all species in the sample, and Pi is the important value of species i.</p></sec></sec></sec><sec id="s3"><title>3. Result</title><sec id="s3_1"><title>3.1. Analysis of Plant Community Composition and Important Value under Different Altitudinal Gradients</title><p>The difference of plant composition in understory reflects the habitat condition of forest land [<xref ref-type="bibr" rid="scirp.78304-ref12">12</xref>] . According to the investigation results, we can divide the Cibagou forest types were divided into Castanopsis forest, mixed forest, Acer green broad-leaved forest, oak forest, poplar and birch mixed forest, Quercusaquifolioide forest with 6 species. Can be seen from <xref ref-type="table" rid="table1">Table 1</xref>, at different altitudes in the forest, understory plant species have obvious differences, at an altitude of 1749 m Castanopsis forest, understory plant coverage was lowest, only 30% species numbers were only 3, the highest importance value was 0.518 for Lepisorusthunbergianus, followed by Campylotropis macrocarpa and Cymbidium hookerianum, important values were 0.255 and 0.172 respectively; at an altitude of 2327 m oak forest, understory plant total coverage was reached 95%, species number was 14, the highest importance value for the Impatiens linghziensis and Galium aparine Linn. var. echinospermum.</p><p>At an altitude of 1960 m mixed forest, plant community coverage was 80% and plots in the number of species was 13, significant higher values of the</p><table-wrap-group id="1"><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> The important values of plant species in different forest stands at different altitudes in Cibagou</title></caption><table-wrap id="1_1"><table><tbody><thead><tr><th align="center" valign="middle" >The coordinates of plot center</th><th align="center" valign="middle" >Forest Vegetation Types</th><th align="center" valign="middle" >Community total coverage</th><th align="center" valign="middle" >Latin name</th><th align="center" valign="middle" >Important values</th></tr></thead><tr><td align="center" valign="middle"  rowspan="5"  >97˚04'21.6''E, 28˚34'44.5''N, 1749 mH</td><td align="center" valign="middle"  rowspan="5"  >Castanopsis forest</td><td align="center" valign="middle"  rowspan="5"  >30%</td><td align="center" valign="middle" >Lepisorusthunbergianus</td><td align="center" valign="middle" >0.518</td></tr><tr><td align="center" valign="middle" >Campylotropis macrocarpa</td><td align="center" valign="middle" >0.255</td></tr><tr><td align="center" valign="middle" >Cymbidium hookerianum</td><td align="center" valign="middle" >0.172</td></tr><tr><td align="center" valign="middle" >Calanthe mannii</td><td align="center" valign="middle" >0.041</td></tr><tr><td align="center" valign="middle" >Galium bungei</td><td align="center" valign="middle" >0.015</td></tr><tr><td align="center" valign="middle"  rowspan="13"  >97˚04'03.1''E, 28˚35'95.9''N, 1960 mH</td><td align="center" valign="middle"  rowspan="13"  >mixed forest</td><td align="center" valign="middle"  rowspan="13"  >80%</td><td align="center" valign="middle" >Pteracanthus alatus</td><td align="center" valign="middle" >0.226</td></tr><tr><td align="center" valign="middle" >Impatiens cristata</td><td align="center" valign="middle" >0.208</td></tr><tr><td align="center" valign="middle" >Aster albescens</td><td align="center" valign="middle" >0.102</td></tr><tr><td align="center" valign="middle" >Polygonum capitatum</td><td align="center" valign="middle" >0.088</td></tr><tr><td align="center" valign="middle" >Microstegium nudum</td><td align="center" valign="middle" >0.079</td></tr><tr><td align="center" valign="middle" >Rubus subinopertus</td><td align="center" valign="middle" >0.059</td></tr><tr><td align="center" valign="middle" >Lecanthus peduncularis</td><td align="center" valign="middle" >0.050</td></tr><tr><td align="center" valign="middle" >Fragaria nubicola</td><td align="center" valign="middle" >0.040</td></tr><tr><td align="center" valign="middle" >Rheum australe</td><td align="center" valign="middle" >0.039</td></tr><tr><td align="center" valign="middle" >Adiantum fimbriatum</td><td align="center" valign="middle" >0.038</td></tr><tr><td align="center" valign="middle" >Bromus inermis</td><td align="center" valign="middle" >0.027</td></tr><tr><td align="center" valign="middle" >Arisaema erubescens</td><td align="center" valign="middle" >0.023</td></tr><tr><td align="center" valign="middle" >Tetrastigma napaulense</td><td align="center" valign="middle" >0.020</td></tr><tr><td align="center" valign="middle"  rowspan="9"  >97˚04'03.7''E, 28˚36'77.8''N, 2092 mH</td><td align="center" valign="middle"  rowspan="9"  >Acer green broad-leaved forest</td><td align="center" valign="middle"  rowspan="9"  >40%</td><td align="center" valign="middle" >Pteris cretica L. var. nervosa</td><td align="center" valign="middle" >0.279</td></tr><tr><td align="center" valign="middle" >Tetrastigma serrulatum</td><td align="center" valign="middle" >0.116</td></tr><tr><td align="center" valign="middle" >Campylotropis macrocarpa</td><td align="center" valign="middle" >0.068</td></tr><tr><td align="center" valign="middle" >Pteridium aquilinum (L.) Kuhn var. latiusculum</td><td align="center" valign="middle" >0.052</td></tr><tr><td align="center" valign="middle" >Smilacinahenryi</td><td align="center" valign="middle" >0.051</td></tr><tr><td align="center" valign="middle" >Hedera nepalensis K. Koch var. sinensis</td><td align="center" valign="middle" >0.050</td></tr><tr><td align="center" valign="middle" >Arisaema heterophyllum</td><td align="center" valign="middle" >0.026</td></tr><tr><td align="center" valign="middle" >Ophiopogon bodinieri</td><td align="center" valign="middle" >0.013</td></tr><tr><td align="center" valign="middle" >Impatiens linghziensis</td><td align="center" valign="middle" >0.013</td></tr><tr><td align="center" valign="middle"  rowspan="4"  >097˚03'86.4''E, 28˚37'97.8''N, 2327 mH</td><td align="center" valign="middle"  rowspan="4"  >Oak forest</td><td align="center" valign="middle"  rowspan="4"  >95%</td><td align="center" valign="middle" >Impatiens linghziensis</td><td align="center" valign="middle" >0.241</td></tr><tr><td align="center" valign="middle" >Galium aparine Linn. var. echinospermum</td><td align="center" valign="middle" >0.145</td></tr><tr><td align="center" valign="middle" >Smilacinahenryi</td><td align="center" valign="middle" >0.081</td></tr><tr><td align="center" valign="middle" >Oxalis acetosella L. ssp. leucolepis</td><td align="center" valign="middle" >0.075</td></tr></tbody></table></table-wrap><table-wrap id="1_2"><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="10"  ></th><th align="center" valign="middle"  rowspan="10"  ></th><th align="center" valign="middle"  rowspan="10"  ></th><th align="center" valign="middle" >Arisaema heterophyllum</th><th align="center" valign="middle" >0.075</th></tr></thead><tr><td align="center" valign="middle" >Viola szetschwanensis</td><td align="center" valign="middle" >0.074</td></tr><tr><td align="center" valign="middle" >Campylotropis macrocarpa</td><td align="center" valign="middle" >0.057</td></tr><tr><td align="center" valign="middle" >Smilax china</td><td align="center" valign="middle" >0.051</td></tr><tr><td align="center" valign="middle" >Pteridium aquilinum (L.) Kuhn var. latiusculum</td><td align="center" valign="middle" >0.035</td></tr><tr><td align="center" valign="middle" >Pteris cretica L. var. nervosa</td><td align="center" valign="middle" >0.032</td></tr><tr><td align="center" valign="middle" >Ophiopogon bodinieri</td><td align="center" valign="middle" >0.031</td></tr><tr><td align="center" valign="middle" >Parthenocissus semicordata</td><td align="center" valign="middle" >0.028</td></tr><tr><td align="center" valign="middle" >Panax pseudoginseng Wall. var. notoginseng</td><td align="center" valign="middle" >0.020</td></tr><tr><td align="center" valign="middle" >Hedera nepalensis K. Koch var. sinensis</td><td align="center" valign="middle" >0.012</td></tr><tr><td align="center" valign="middle"  rowspan="10"  >97˚04'95.2''E, 28˚71'80.0''N, 2670 mH</td><td align="center" valign="middle"  rowspan="10"  >poplar and birch mixed forest</td><td align="center" valign="middle"  rowspan="10"  >80%</td><td align="center" valign="middle" >Fargesia setosa</td><td align="center" valign="middle" >0.218</td></tr><tr><td align="center" valign="middle" >Oxalis acetosella L. ssp. leucolepis</td><td align="center" valign="middle" >0.209</td></tr><tr><td align="center" valign="middle" >Polygonum nepalense</td><td align="center" valign="middle" >0.181</td></tr><tr><td align="center" valign="middle" >Galium aparine Linn. var. echinospermum</td><td align="center" valign="middle" >0.063</td></tr><tr><td align="center" valign="middle" >Pilea notata</td><td align="center" valign="middle" >0.052</td></tr><tr><td align="center" valign="middle" >Impatiens linghziensis</td><td align="center" valign="middle" >0.051</td></tr><tr><td align="center" valign="middle" >Parthenocissus semicordata</td><td align="center" valign="middle" >0.050</td></tr><tr><td align="center" valign="middle" >Angelica paeoniifolia</td><td align="center" valign="middle" >0.043</td></tr><tr><td align="center" valign="middle" >Fragaria nubicola</td><td align="center" valign="middle" >0.043</td></tr><tr><td align="center" valign="middle" >Pteridium aquilinum (L.) Kuhn var. latiusculum</td><td align="center" valign="middle" >0.030</td></tr><tr><td align="center" valign="middle"  rowspan="7"  >97˚02'20.5''E, 28˚75'66.0''N, 2880 mH</td><td align="center" valign="middle"  rowspan="7"  >Quercus aquifolioides forest</td><td align="center" valign="middle"  rowspan="7"  >90%</td><td align="center" valign="middle" >Fragaria nubicola</td><td align="center" valign="middle" >0.332</td></tr><tr><td align="center" valign="middle" >Pteridium aquilinum (L.) Kuhn var. latiusculum</td><td align="center" valign="middle" >0.199</td></tr><tr><td align="center" valign="middle" >Panax pseudoginseng Wall. var. notoginseng</td><td align="center" valign="middle" >0.140</td></tr><tr><td align="center" valign="middle" >Impatiens linghziensis</td><td align="center" valign="middle" >0.107</td></tr><tr><td align="center" valign="middle" >Dysosma tsayuensis</td><td align="center" valign="middle" >0.050</td></tr><tr><td align="center" valign="middle" >Smilax china</td><td align="center" valign="middle" >0.045</td></tr><tr><td align="center" valign="middle" >Streptopus simplex</td><td align="center" valign="middle" >0.026</td></tr></tbody></table></table-wrap></table-wrap-group><p>Pteracanthus alatus, Impatiens cristata, Aster albescens, important values were 0.226, 0.208, 0.102; at an altitude of 2092 m Acer green broad-leaved forest, plant total the coverage was only 40% and species number was 9, the important value of Pteris cretica L. var. nervosa and Tetrastigma serrulatum, were 0.279 and 0.116; the elevation of 2670 m poplar and birch mixed forest, plant total coverage is 80%, the number of species was 10, higher important value for Fargesia setosa, Oxalis acetosella L. ssp. leucolepis, Polygonum nepalense, important values were 0.218, 0.209, 0.181; at an altitude of 2880 m in Quercus aquifolioides forest, plant total coverage is 90%, higher important value for Fragaria nubicola, Pteridium aquilinum (L.) Kuhnvar. latiusculum, Panax pseudoginseng Wall. var. notoginseng, Impatiens linghziensis, important values were 0.332, 0.199, 0.140, 0.107.</p></sec><sec id="s3_2"><title>3.2. Species Diversity of Plant Species in Different Elevations of the Cibagou Nature Reserve</title><p>Using Menhinick richness index and Margalef abundance index to analysis, the evaluation of richness from <xref ref-type="fig" rid="fig1">Figure 1</xref>, you can see, at an altitude of 1749 m to 2880 m range, species richness are low, the overall showed a trend of rise before they are lower; The Shannon-wiener index and Simpson index of different elevation gradient undergrowth species diversity were analyzed (see <xref ref-type="fig" rid="fig2">Figure 2</xref>), the results show no obvious difference change with altitude gradient, only at an altitude of 2327 m diversity is relative taller; The Pielou evenness and Sheldon index of different elevation gradient plant species evenness were analyzed (see <xref ref-type="fig" rid="fig3">Figure 3</xref>), the results show kindness and ditch undergrowth evenness first decreases after rising trend on the whole. Overall, at an altitude of 2327 m and an altitude of 2670 m in plant species richness is relatively high, at an altitude of 2327 m in species diversity is relatively high, at an altitude of 2670 m species evenness, lowest possible reasons for the actual survey, at an altitude of 2327 m and 2670 m number appears more rare species.</p><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> Plant richness in different altitude gradients</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/11-2603297x12.png"/></fig><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Diversity of plant species at different altitudes</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/11-2603297x13.png"/></fig><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Plant species uniformity at different altitudes</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/11-2603297x14.png"/></fig></sec></sec><sec id="s4"><title>4. Discussion</title><p>Community as an important part of biodiversity, species diversity is the very important content in community ecology; altitude is one of the main plant community species composition control mountains natural gradient, elevation gradient change will lead to the change of factors such as temperature, precipitation, light conditions, thus affecting species distribution. Species diversity and the relationship between the altitude gradient has no unified conclusion, species diversity gradually lower approximation with altitude in the change of latitude gradient model has been proved in many mountains [<xref ref-type="bibr" rid="scirp.78304-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref14">14</xref>] . The species diversity of zonal plant communities in western Yunnan was studied and results showed that the density of species decreased with the increasing of altitude gradient [<xref ref-type="bibr" rid="scirp.78304-ref15">15</xref>] , Zhang [<xref ref-type="bibr" rid="scirp.78304-ref16">16</xref>] also has a consistent conclusion based on Luya Mountain plant community diversity in Shanxi province. However, there are many studies have shown that the temperature and humidity of the elevation in the range has most species survival conditions, thus presents the species richness increased with altitude showed a trend of unimodal curve change [<xref ref-type="bibr" rid="scirp.78304-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.78304-ref18">18</xref>] , namely lower after rising first. Grytnes [<xref ref-type="bibr" rid="scirp.78304-ref19">19</xref>] found that high species richness values appeared at an altitude of 1500 - 2500 min the Himalayas or Nepal. In the study of plant community pattern in Haba Snow Mountain, Yunnan, the peak of herbaceous plant abundance appeared at an altitude of 3000 m - 3500 m [<xref ref-type="bibr" rid="scirp.78304-ref20">20</xref>] . The study of the Altai Mountains in Xinjiang also showed that the abundance and diversity of herbaceous plants showed a single peak Curve increases [<xref ref-type="bibr" rid="scirp.78304-ref21">21</xref>] . The reason may be that the study did not include a complete elevation gradient, that is, the peak of the species diversity was not studied in the study of altitudinal gradient [<xref ref-type="bibr" rid="scirp.78304-ref22">22</xref>] . Su [<xref ref-type="bibr" rid="scirp.78304-ref23">23</xref>] have shown that the Tibetan Sejila Mountain herbal plant richness was a double peak curve; about 3500 m above sea level and an altitude of 4500 m are high.</p><p>The results showed that the species richness of understory plants in Cibagou Nature Reserve increased first and then decreased with the increase of altitude gradient, showing a trend of single peak curve and peak appeared between the attitude 2327 m - 2670 m, Shannon-wiener diversity index peak appeared at an altitude of 2327 m. The diversity of plant species in different forest plants is relatively large, but the variation of plant diversity varies with altitude and is generally low. Possible reason was the primeval forest nature reserves is relatively complete, tall trees and high shrubs level obviously, lead to light in a certain extent become limiting factors of the growth of undergrowth, at an altitude of 1749 m is most obvious, the undergrowth only 30% of the total coverage, with altitude gradient rise, different forest types of forest thinning, forest light penetration enhancement, undergrowth coverage increased significantly, species richness and diversity were slightly rising trend, and with the higher altitude, temperature may become a limiting factor of plant growth, thereby limiting the part of the plant’s growth.</p></sec><sec id="s5"><title>Acknowledgements</title><p>This study was financially supported by follow fund: Collection and utilization of medicinal flower resources in Tibet; Research on Tibet resources plant information system based on Android (2015XZ01G28); Fund of Tibet science and Technology Department (2016ZR-NQ-09); Humanities and social science projects in Universities in Tibet (sk2015-36).</p></sec><sec id="s6"><title>Cite this paper</title><p>Wang, W., Xing, Z., Li, W.B. and Yang, X.L. (2017) Study on Diversity of Undergrowth Plant Community in Cibagou Nature Reserve. American Journal of Plant Sciences, 8, 2149-2158. https://doi.org/10.4236/ajps.2017.89144</p></sec></body><back><ref-list><title>References</title><ref id="scirp.78304-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Gao, X., Ma, K. and Chen, L. (2001) Species Diversity of Some Deciduous Broad-Leaved Forests in the Warm-Temperate Zone and Its Relations to Community Stability. Acta Phytoecologica Sinica, 25, 283-290.</mixed-citation></ref><ref id="scirp.78304-ref2"><label>2</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Lan</surname><given-names> S. </given-names></name>,<etal>et al</etal>. (<year>2003</year>)<article-title>Plant Species Diversity in Wuyishan National Nature Reserve</article-title><source> Scientia Silvaesinicae</source><volume> 39</volume>,<fpage> 36</fpage>-<lpage>43</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.78304-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Hao, Z., Zhao, S. and Tao, D. (1994) Species Diversity and Its Seasonal Dynamics or Herbs in a Broad-Leaved Korean Pine Forest on the Northern Slope of the Changbai Mountain. Chinese Biodiversity, 2, 125-132.</mixed-citation></ref><ref id="scirp.78304-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Hao, Z., Zhang, J., Song, B., et al. (2007) Vertical Structure and Spatial Associations of Dominant Tree Species in an Old-Growth Temperate Forest. Forest Ecology &amp; Management, 252, 1-11. https://doi.org/10.1016/j.foreco.2007.06.026</mixed-citation></ref><ref id="scirp.78304-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Condit, R., Ashton, P., Bunyavejchewin, S., et al. (2006) The Importance of Demographic Niches to Tree Diversity. Science, 313, 98. https://doi.org/10.1126/science.1124712</mixed-citation></ref><ref id="scirp.78304-ref6"><label>6</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Wu</surname><given-names> P. </given-names></name>,<etal>et al</etal>. (<year>2003</year>)<article-title>Large and Medium-Sized Animals in the Cibagou Nature Reserve</article-title><source> Chinese Journal of Wildlife</source><volume> 24</volume>,<fpage> 44</fpage>-<lpage>46</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.78304-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Wu, P. and Zhang, E. (2006) Habitat Selection of takin (Budorcastaxicolor) in Cibagou Nature Reserve of Tibet, China. Acta Theriologica Sinica, 26, 152-158. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Wu, P.J., Zhang, H. and Zhang, E.D. (2007) Vertical Distribution and Habitat Differentiation of Main Artiodactyls in Tibet Cibagou Nature Reserve of China in Spring. Chinese Journal of Ecology, 26, 1569-1573.</mixed-citation></ref><ref id="scirp.78304-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Tang, X. and Lu, J. (2011) Diversity and Faunal Analysis of Known Insect Species in Cibagou National Nature Reserve. Journal of Mountain Agriculture and Biology, 30, 487-491. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">He, J., Yue, H. and Zhang, G. (2010) Diversity and Bioactivity Analysis of Actinomycetes Isolated from Cibagou Nature Reserve Soil. Journal of Northwest A&amp;F University, No. 8, 83-89. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, J. (2004) Quantitative Ecology. The Science Publishing Company, Beijing, 77-96.</mixed-citation></ref><ref id="scirp.78304-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Deng, L. and Zhang, W. (2010) Natural Development Pattern of Robinia pseudoacacia Plantations in Loess Hilly Region. Scientia Silvaesinicae, 46, 15-22. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Wilson, J.B., Lee, W.G. and Mark, A.F. (1990) Species Diversity in Relation to Ultramafic Substrate and to Altitude in Southwestern New Zealand. Plant Ecology, 86, 15-20. https://doi.org/10.1007/BF00045131</mixed-citation></ref><ref id="scirp.78304-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Wang, Z. and Tang, Z.J. (2007) Altitudinal Patterns of Seed Plant Richness in the Gaoligong Mountains, South-East Tibet, China. Diversity &amp; Distributions, 13, 845-854. https://doi.org/10.1111/j.1472-4642.2007.00335.x</mixed-citation></ref><ref id="scirp.78304-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Feng, J. and Xu, C. (2009) Geographical Distribution Patterns of Zonal Plant Community Species Diversity in West Yunnan, China. Chinese Journal of Ecology, 28, 595-600. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, L., Zhang, F. and Shang, G. (2000) Vegetation Diversity of Luya Mountains. Chinese Biodiversity, 8, 361-369. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Sanchez-Gonzalez, A. and Lopez-Mata, L. (2005) Plant Species Richness and Diversity along an Altitudinal Gradient in the Sierra Nevada, Mexico. Diversity &amp; Distributions, 11, 567-575. https://doi.org/10.1111/j.1366-9516.2005.00186.x</mixed-citation></ref><ref id="scirp.78304-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Zhao, C.M., Chen, W.L., Tian, Z.Q., et al. (2005) Altitudinal Pattern of Plant Species Diversity in Shennongjia Mountains, Central China. Journal of Integrative Plant Biology, 47, 1431-1449. https://doi.org/10.1111/j.1744-7909.2005.00164.x</mixed-citation></ref><ref id="scirp.78304-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Grytnes, J.A. and Vetaas, O.R. (2002) Species Richness and Altitude: A Comparison between Null Models and Interpolated Plant Species Richness along the Himalayan Altitudinal Gradient, Nepal. The American Naturalist, 159, 294.</mixed-citation></ref><ref id="scirp.78304-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">Tao, J., Zan, G. and Yu, C. (2011) Altitudinal Patterns of Plant Communities and Species Diversity in the Habaxueshan Mountains, Yunnan, China. Scientia Silvae Sinicae, 47, 1-6. (In Chinese)</mixed-citation></ref><ref id="scirp.78304-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">Jing, X., Zang, R. and Ding, Y. (2010) Distribution Pattern of Species Diversity along Altitudinal Gradient in the Northern Slope of Xiaodonggou in Altai Mountains, Xinjiang. Scientia Silvae Sinicae, 46, 23-28.</mixed-citation></ref><ref id="scirp.78304-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">Rahbek, C. (2006) The Elevational Gradient of Species Richness: A Uniform Pattern? Ecography, 18, 200-205. https://doi.org/10.1111/j.1600-0587.1995.tb00341.x</mixed-citation></ref><ref id="scirp.78304-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Su, J., Liu, W. and Zhang, W. (2011) Species Diversity of Plant Communities along an Altitudinal Gradient on the West Slope of Sejila Mountains, Tibet. Scientia Silvae Sinicae, 47, 12-19. (In Chinese)</mixed-citation></ref></ref-list></back></article>