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<title cf:type="text"><![CDATA[ -->Special Subject of Karst Plants (2)]]></title>
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<title xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="text"><![CDATA[Dynamic changes of soil microbe quantity in reed 
vegetation of Huixian Karst Wetland,Guilin,China]]></title>
<link><![CDATA[http://gxzw.ijournals.cn/gxzwen/ch/reader/view_abstract.aspx?file_no=170602&flag=1]]></link>
<description xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="html"><![CDATA[Reed is one of the typical dominant plant communities in Huixian Karst Wetland. In order to investigate the dynamic distribution characteristics of soil microbes of reed plant community in Huixian Karst Wetland and to explore the response mechanism of soil microorganism on water and thermal seasonal change, different levels of soil samples(0-10, 10-20 and 20-30 cm)were collected, and the composition and distribution of bacteria, fungi and actinomycetes between rhizosphere and non-rhizosphere were studied during spring, summer, autumn and winter in reed vegetation, respectively. The results showed that the quantities of rhizosphere and non-rhizosphere microorganism were different at different seasons. Among all microbes, bacteria were the most numerous followed by actinomyces, with fungi the least numerous. The highest proportion of bacteria was 96.62%, actinomycetes was 35.38%, and fungi was very small. The soil vertical change of bacteria, fungi and actinomycetes were obviously. The microbial quantity decreased with the increasing of soil depth on the whole. The seasonal change of different soil levels of rhizosphere microorganism and non-rhizosphere microorganism were consistent in our study plot. The results indicated that the bacteria quantity in the same soil layer followed the way of summer &gt; autumn &gt; spring &gt; winter, but the fungi quantity showed autumn &gt; summer &gt; spring &gt; winter, the actinomycetes quantity was in an order of autumn &gt; spring &gt; summer &gt; winter. Meanwhile, the maximum values of bacteria, actinomycetes and fungi were 2.70&#215;10<sup>7</sup>, 1.92&#215;10<sup>6</sup> and 3.35&#215;10<sup>4</sup> cfu·g<sup>-1</sup> relatively. Microorganism in the soil of reed plant community had obvious rhizosphere effect to some extent. The microorganism and soil organic carbon, total nitrogen, total phosphorus, total potassium, available nitrogen, available phosphorus and available potassium had a significant positive correlation. The rhizosphere effect of microorganism associated with microbial type, soil depth, monthly average rainfall and temperature channges, and it was non-significantly in winter as a whole. It had significant seasonal variations as well. The content of soil nutrition may be a major factor for the change of soil microbial quantity in Huixian Karst Wetland. Meanwhile, the dynamic changes of the number of soil microorganism may reveal the environmental effects of wetlands. The scientific data for the wetland sustainable management policy would be suggested for Huixian Karst Wetland.]]></description>
<pubDate>2017/7/2 22:58:41</pubDate>
<category><![CDATA[Special Subject of Karst Plants (2)]]></category>
<author><![CDATA[ZHOU Long-Wu, HUANG Yu-Qing, WANG Xin-Gui, XU Guang-Ping<sup>*</sup>, 
SUN Ying-Jie, ZHANG De-Nan, YAO Yue-Feng, ZENG Dan-Juan]]></author>
<atom:author xmlns:atom="http://www.w3.org/2005/Atom">
<atom:name>ZHOU Long-Wu, HUANG Yu-Qing, WANG Xin-Gui, XU Guang-Ping<sup>*</sup>, 
SUN Ying-Jie, ZHANG De-Nan, YAO Yue-Feng, ZENG Dan-Juan</atom:name>
</atom:author>
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<title xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="text"><![CDATA[Relationship between the spatial distributions of dominant 
arbor species and environmental factors of <i>Excentrodendron 
hsienmu</i> community in Southwest Guangxi, China]]></title>
<link><![CDATA[http://gxzw.ijournals.cn/gxzwen/ch/reader/view_abstract.aspx?file_no=170603&flag=1]]></link>
<description xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="html"><![CDATA[Revealing the relationships between plant distributions and environmental factors is one focus of plant community ecology. <i>Excentrodendron hsienmu</i> is the endemic species in tropical limestone area, and the second national key protected plant of China, and it widely distributes in the karst mountains of Southwest Guangxi, China. Exploring factors effecting the domiant arbor trees distribution has significant implication for effectively protecting the <i>E. hsienmu</i> population in the study area. Important value of the main arbor species and eight environmental factors were measured based on field surveys in the karst mountains of Southwest Guangxi. And then, correlation analysis was used to detect the relationships between topographic and soil factors. Canonical correspondence analysis(CCA)was used to explore the effects of environmental factors on the distribution of dominant arbor species. A total of 176 woody plant species with diameter at breast height ≥1.0 cm, and tree height ≥1.5 m were recorded, belonging to 50 families, 128 genera. <i>E. hsienmu</i> was absolutely dominant in tree layer, while <i>Orophea anceps</i>, <i>Garcinia paucinervis</i>, <i>Walsura robusta</i>, and <i>Sterculia nobilis</i> were the main accompanying species. Correlation analysis showed elevation was very significantly positively related to soil organic matter and total nitrogen. Except for soil pH, relationships between all soil factorswere markedly positive. Result of CCA revealed that soil total potassium had the most significantly effect and the soil total phosphorus had the second on the distribution patterns of dominant arbor species, while slope aspect and degree also played important roles in the spatial patterns of them. This study revealed the main factors influencing on the spatial patterns of dominant arbor trees of <i>E. hsienmu</i> community, and provides scientific information for the vegetation restoration in the study area.]]></description>
<pubDate>2017/7/2 22:58:41</pubDate>
<category><![CDATA[Special Subject of Karst Plants (2)]]></category>
<author><![CDATA[SHEN Wen-Hui<sup>1</sup>, OU Zhi-Yang<sup>1*</sup>, PANG Shi-Long<sup>1</sup>, HE Qin-Fei<sup>1</sup>, LIANG Yan<sup>2</sup>]]></author>
<atom:author xmlns:atom="http://www.w3.org/2005/Atom">
<atom:name>SHEN Wen-Hui<sup>1</sup>, OU Zhi-Yang<sup>1*</sup>, PANG Shi-Long<sup>1</sup>, HE Qin-Fei<sup>1</sup>, LIANG Yan<sup>2</sup></atom:name>
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<title xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="text"><![CDATA[Plasticity of <i>Alternanthera philoxeroides</i> in 
response to three karst habitats]]></title>
<link><![CDATA[http://gxzw.ijournals.cn/gxzwen/ch/reader/view_abstract.aspx?file_no=170604&flag=1]]></link>
<description xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="html"><![CDATA[Since the invasion of <i>Alternanthera philoxeroides</i> around in our country since the widely spread, has an important impact on the production and life of the people. Plasticity is an important feature of invasive plants, we studied indexs of plasticity <i>A. philoxeroides</i> providing scientific basis for the prevention and cure in different habitats. The results were as follows:(1)There were obvious differences in internode length, leaf area per plant, total weight and leaf dry weight of <i>A. philoxeroides</i> in rock environment, road and aquatic habitats.(2)Asexual reproduction organs of stem biomass was the largest in rock environment, followed by the road and the river habitat.(3)Internode and leaf area of <i>A. philoxeroides</i> increased with the rock, road and aquatic environment.(4)In the lack of water rocks environment, <i>A. philoxeroides</i> increased reproduction by short internode and increase the mass.]]></description>
<pubDate>2017/7/2 22:58:41</pubDate>
<category><![CDATA[Special Subject of Karst Plants (2)]]></category>
<author><![CDATA[ZHANG Bao-Cheng, PENG Yan, ZANG Ling-Fei, QIN Kai-Nan, 
LI Xian-Bi, SUI Chang-Ling]]></author>
<atom:author xmlns:atom="http://www.w3.org/2005/Atom">
<atom:name>ZHANG Bao-Cheng, PENG Yan, ZANG Ling-Fei, QIN Kai-Nan, 
LI Xian-Bi, SUI Chang-Ling</atom:name>
</atom:author>
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<title xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="text"><![CDATA[Effects of different calcium concentrations on seedling 
growth and enzyme activities of two karst plant species]]></title>
<link><![CDATA[http://gxzw.ijournals.cn/gxzwen/ch/reader/view_abstract.aspx?file_no=170605&flag=1]]></link>
<description xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="html"><![CDATA[Calcium(Ca)is an essential nutrient for plant growth; however, high Ca concentrations have detrimental effects on several plant species, while a few plant species have adapted to high levels of Ca via multiple mechanisms. The limestone soils of karst regions in southwest China are characterized by high levels of Ca, which have substantial influences on plant physiological characteristics and distribution. High Ca concentrations influence photosynthesis and might even destroy organelles resulting in death of the plant. Adaptation mechanisms of plants to high concentrations of Ca are very complex processes and are relative to all aspects of plant growth. Selection of suitable tree species plays a key role in ecological restoration. In order to investigate the physiological adaptation mechanisms of plants to high calcium conditions in the karst region of Southwest China, a pot experiment was conducted with seedlings of two species, i.e., <i>Swida wilsoniana</i> and <i>Choerospondias axillaris</i>. To exclude the influences from other confounding factors, each pot was filled with sand instead of soil. The seedlings were treated with five Ca levels, i.e., 5, 35, 70, 150, 300 mmol·L<sup>-1</sup>. The growth and enzyme activities of the two plant species were measured. The results showed that the both species were the highest at 5 mmol·L<sup>-1</sup>, and tended to decrease with the increase in Ca concentration. The biomass of roots, branches, leaf and total biomass of both species demonstrated a downward trend as Ca concentration increase, but those of <i>C. axillaris </i>showed a tendency to increase for the 300 mmol·L<sup>-1</sup> treatment. The biomass allocation ratio was in the order of root &gt; branch &gt; leaf for <i>Swida wilsoniana</i>, and root &gt; branch &gt; leaf for<i> S. wilsoniana</i> at 35 mmol·L<sup>-1</sup>. The biomass allocation at other Ca levels showed a variation pattern of branch &gt; root &gt; leaf for both species. MDA content was the greatest at 150 mmol·L<sup>-1</sup> for both species. MDA content of <i>Choeropondias axillaris</i> was lower than that of <i>Swida wilsoniana</i>. The soluble sugar content and CAT activity of <i>S. wilsoniana</i> under calcium stress were higher than those of <i>Choerospondis axillaris</i>. The physiological indices reached optimum levels at the Ca concentrations of 5 and 150 mmol·L<sup>-1</sup> for both species, while were inhibited at the concentration 300 mmol·L<sup>-1</sup>, which led to a decline of photosynthetic capacity. Our results also revealed that <i>S. wilsoniana</i> had better adaptability to high Ca concentrations relative to <i>C. axillaris</i>.]]></description>
<pubDate>2017/7/2 22:58:41</pubDate>
<category><![CDATA[Special Subject of Karst Plants (2)]]></category>
<author><![CDATA[ZHANG Fang<sup>1,2,5</sup>, SONG Min<sup>1,2,3</sup>, PENG Wan-Xia<sup>1,2*</sup>, ZENG Fu-Ping<sup>1,2</sup>, 
DU Hu<sup>1,2</sup>, HU Fang<sup>1,2,5</sup>, CHEN Li<sup>1,2,4</sup>, SU Liang<sup>1,2,4</sup>]]></author>
<atom:author xmlns:atom="http://www.w3.org/2005/Atom">
<atom:name>ZHANG Fang<sup>1,2,5</sup>, SONG Min<sup>1,2,3</sup>, PENG Wan-Xia<sup>1,2*</sup>, ZENG Fu-Ping<sup>1,2</sup>, 
DU Hu<sup>1,2</sup>, HU Fang<sup>1,2,5</sup>, CHEN Li<sup>1,2,4</sup>, SU Liang<sup>1,2,4</sup></atom:name>
</atom:author>
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<title xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="text"><![CDATA[Effects of water stress and rewatering on eco-
physiological characteristics of <i>Illicicum difengpi</i>]]></title>
<link><![CDATA[http://gxzw.ijournals.cn/gxzwen/ch/reader/view_abstract.aspx?file_no=170606&flag=1]]></link>
<description xmlns:cf="http://www.microsoft.com/schemas/rss/core/2005" cf:type="html"><![CDATA[In order to understand the eco-physiological adaptability to water stress of karst plant, the experiments were carried out with 4-year-old <i>Illicicum difengpi </i>K. I. B. et K. I. M plants, which was a karst endemic medicinal plant. We investigated the photosynthetic variables, chlorophyll fluorescence variables and photosynthetic pigment content of <i>I. difengpi</i> under water stress and rewatering conditions. The results showed that withholding water for 10 d, the net photosynthetic rate(<i>P</i><sub>n</sub>), intercellular CO<sub>2</sub> concentration(<i>C</i><sub>i</sub>), stomatal limitation value(<i>L</i><sub>s</sub>)and stomatal conductance(<i>G</i><sub>s</sub>)of <i>I. difengpi</i> leaves decreased significantly under water stress, and stomatal limitation was the main reason for the decrease of <i>P</i><sub>n</sub>. Withholding water for 15 d, under water stress, the diurnal variation of <i>P</i><sub>n</sub> showed a gradual downward trend and the <i>P</i><sub>n</sub> values were close to zero after 9:30 am, which suggested that the depression of photosynthesis might be due to non-stomatal limitation. While the diurnal variation of <i>P</i><sub>n</sub> was dual-peaked in the leaves of control, and stomatal limitation was still the main reason for the decrease of <i>P</i><sub>n</sub>. The decrease of chlorophyll content and the increased of <i>Chl </i><sub>(a/b </sub><sub>)</sub>under water stress conditions, which reduced the binding proteins(LHC Ⅱ)content, the captured light energy, and the risk of photosynthetic apparatus damage. Under water stress condition, the initial fluorescence(<i>F</i><sub>o</sub>)increased significantly, the maximum fluorescence(<i>F</i><sub>m</sub>), potential activity of photo-system Ⅱ(<i>F</i><sub>v</sub>/<i>F</i><sub>o</sub>)and maximal photochemical efficiency of photo-system Ⅱ(<i>F</i><sub>v</sub>/<i>F</i><sub>m</sub>)decreased significantly, which indicating that water stress could cause a certain degree of damage or fracture to its PS Ⅱ reaction center, therefore, the potential activity and maximal photochemical efficiency of PS Ⅱ were reduced. After re-watering for 5 d, the above-mentioned physiological and ecological parameters of <i>I. difengpi</i> could recover to the control level, indicated that the physiological repair capability of which is very strong after rehydration.]]></description>
<pubDate>2017/7/2 22:58:41</pubDate>
<category><![CDATA[Special Subject of Karst Plants (2)]]></category>
<author><![CDATA[WANG Man-Lian<sup>1</sup>, TANG Hui<sup>1*</sup>, HAN Yu<sup>1,2</sup>, ZHANG Jun-Jie<sup>1,3</sup>, LIANG Hui-Ling<sup>1</sup>]]></author>
<atom:author xmlns:atom="http://www.w3.org/2005/Atom">
<atom:name>WANG Man-Lian<sup>1</sup>, TANG Hui<sup>1*</sup>, HAN Yu<sup>1,2</sup>, ZHANG Jun-Jie<sup>1,3</sup>, LIANG Hui-Ling<sup>1</sup></atom:name>
</atom:author>
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