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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2023.1215191</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Nitrogen enrichment alters the resistance of a noninvasive alien plant species to <italic>Alternanthera philoxeroides</italic> invasion</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Wu</surname>
<given-names>Hao</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/574949"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Dong</surname>
<given-names>Sijin</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Wang</surname>
<given-names>Li</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Zhu</surname>
<given-names>Yuanyuan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Jia</surname>
<given-names>Shaoqi</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Rao</surname>
<given-names>Benqiang</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>College of Life Sciences, Xinyang Normal University</institution>, <addr-line>Xinyang</addr-line>, <country>China</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Henan Dabieshan National Field Observation and Research Station of Forest Ecosystem</institution>, <addr-line>Zhengzhou</addr-line>, <country>China</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Xinyang Academy of Ecological Research</institution>, <addr-line>Xinyang</addr-line>, <country>China</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Wuhan Botanical Garden, Chinese Academy of Sciences</institution>, <addr-line>Wuhan</addr-line>, <country>China</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Hongwei Yu, Henan University, China</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Yan Wang, Yunnan University, China; Jiamei Li, Henan Agricultural University, China</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Hao Wu, <email xlink:href="mailto:wuhao86868686@163.com">wuhao86868686@163.com</email>; Benqiang Rao, <email xlink:href="mailto:rbqxy@163.com">rbqxy@163.com</email>
</p>
</fn>
<fn fn-type="equal" id="fn003">
<p>&#x2020;These authors have contributed equally to this work and share first authorship</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>11</day>
<month>07</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>11</volume>
<elocation-id>1215191</elocation-id>
<history>
<date date-type="received">
<day>01</day>
<month>05</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>26</day>
<month>06</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Wu, Dong, Wang, Zhu, Jia and Rao</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Wu, Dong, Wang, Zhu, Jia and Rao</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Soil nitrogen can significantly affect the morphology, biomass, nutrient allocation, and photosynthesis of alien vs. native plants, thereby changing their coexistence patterns; however, the effect of soil nitrogen on the interspecific relationship between alien plants is currently unclear. We conducted a nitrogen addition experiment in a greenhouse to explore the effect of soil nitrogen on the interspecific relationship between invasive alien weed <italic>Alternanthera philoxeroides</italic> and the noninvasive alien horticultural plant <italic>Oxalis articulata.</italic> We set three experimental factors&#x2014;nitrogen treatment, planting type, and species and measured the morphology, biomass, carbon (C) and nitrogen (N) content, physiological traits, and photosynthetic fluorescence of the studied plant species. We then used multi-way ANOVA and multiple comparisons to examine the differences in the above indicators among treatment combinations. We found that, in mixed cultures, nitrogen addition significantly increased the root area of <italic>O</italic>. <italic>articulata</italic> by 128.489% but decreased the root length by 56.974% compared with the control, while it significantly increased the root length of <italic>A</italic>. <italic>philoxeroides</italic> by 130.026%. Nitrogen addition did not affect the biomass accumulation of these two plant species; however, the biomass and root/shoot ratio of <italic>O</italic>. <italic>articulata</italic> were significant higher than those of <italic>A</italic>. <italic>philoxeroides.</italic> Nitrogen addition significantly increased the N content of <italic>A</italic>. <italic>philoxeroides</italic> by 278.767% and decreased the C:N ratio by 66.110% in mixed cultures. Nitrogen addition caused a significant trade-off between flavonoid and anthocyanin in <italic>O</italic>. <italic>articulata</italic>, and decreased the initial fluorescence (F<sub>0</sub>) and maximal fluorescence (F<sub>m</sub>) of <italic>A</italic>. <italic>philoxeroides</italic> by 18.649 and 23.507%, respectively, in mixed cultures. These results indicate that nitrogen addition increased the N absorption and assimilation ability of <italic>A</italic>. <italic>philoxeroides</italic> in deep soil; furthermore, it significantly enhanced the advantages for <italic>O</italic>. <italic>articulata</italic> in terms of morphology, physiological plasticity, and photosynthetic efficiency. In addition, <italic>O</italic>. <italic>articulata</italic> had better individual and underground competitive advantages. Under intensified nitrogen deposition, the biotic replacement effect of <italic>O</italic>. <italic>articulata</italic> on <italic>A</italic>. <italic>philoxeroides</italic> in natural ecosystems could be further enhanced.</p>
</abstract>
<kwd-group>
<kwd>
<italic>Alternanthera philoxeroides</italic>
</kwd>
<kwd>carbon/nitrogen ratio</kwd>
<kwd>interspecific competition</kwd>
<kwd>nitrogen addition</kwd>
<kwd>
<italic>Oxalis articulata</italic>
</kwd>
<kwd>plant invasion</kwd>
<kwd>photosynthetic physiology</kwd>
</kwd-group>
<contract-sponsor id="cn001">National Natural Science Foundation of China<named-content content-type="fundref-id">10.13039/501100001809</named-content>
</contract-sponsor>
<counts>
<fig-count count="7"/>
<table-count count="5"/>
<equation-count count="0"/>
<ref-count count="74"/>
<page-count count="13"/>
<word-count count="6217"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Conservation and Restoration Ecology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Under rapid global environmental change, the negative effects of plant invasion on the environment, economic development, and human health continue to increase (<xref ref-type="bibr" rid="B64">Wu and Ding, 2019</xref>; <xref ref-type="bibr" rid="B12">Fantle-Lepczyk et&#xa0;al, 2022</xref>). In natural ecosystems, limited available resources cause intense bio-interactions among plant species that have similar resource requirements, thereby weakening their growth, survival, and reproduction, which leads to interspecific competition (<xref ref-type="bibr" rid="B42">Prass et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B55">Tumber-Davila et&#xa0;al., 2022</xref>). Invasive plants usually have higher rates of growth, diffusion, and reproduction than native plant species, which can make them easily become the dominant or even constructive species and thus enhance their competitive advantages, and this will strongly affect the community structure and interspecific competition patterns (<xref ref-type="bibr" rid="B18">Gu et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B2">Cai et&#xa0;al., 2022</xref>). Recent studies have found that the competitive relationship between invasive and native plants can also change with the invasion process and species coevolution (<xref ref-type="bibr" rid="B30">Liu et&#xa0;al, 2018</xref>). For instance, the negative effect of the invasive species <italic>Heracleum mantegazzianum</italic> has decreased over time (<xref ref-type="bibr" rid="B11">Dostal et&#xa0;al., 2013</xref>), while the native species <italic>Desmodium heterocarpon</italic> and <italic>Senna tora</italic> can replace the invasive species <italic>Mikania micrantha</italic> in the field due to their strong environmental tolerance (<xref ref-type="bibr" rid="B21">Jia et&#xa0;al., 2022</xref>). Exploring the competitive relationships among invasive plants and other plants under environmental changes can help in optimizing the biocontrol measures for plant invasions.</p>
<p>The current amount of atmospheric nitrogen deposition around the globe has increased by four times compared to the 18th century, and China has become the third largest nitrogen deposition area in the world, following closely behind Europe and North America, with a maximum volume of 63.53&#xa0;kg N ha<sup>&#x2212;1</sup> yr<sup>&#x2212;1</sup> in South China (<xref ref-type="bibr" rid="B36">Lv and Tian, 2007</xref>; <xref ref-type="bibr" rid="B31">Liu et&#xa0;al., 2013</xref>). Nitrogen is a crucial element that limits plant growth and photosynthesis, and nitrogen supply levels significantly affect the plant invasion process (<xref ref-type="bibr" rid="B39">Pan et&#xa0;al, 2016</xref>; <xref ref-type="bibr" rid="B51">Slate et&#xa0;al., 2022</xref>). Invasive plants usually have higher nitrogen utilization efficiency due to their high nitrate reductase activity, and thus have higher growth rates than native plant species (<xref ref-type="bibr" rid="B44">Ren et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B45">Ren et&#xa0;al., 2022</xref>). Previous studies have found that nitrogen addition enhances the competitiveness of some invasive plants, such as <italic>Centaurea stoebe</italic>, <italic>Galinsoga quadriradiata</italic>, and <italic>Ambrosia artemisiifolia</italic> (<xref ref-type="bibr" rid="B30">Liu et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B45">Ren et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B51">Slate et&#xa0;al., 2022</xref>), and promote biomass accumulation in the invasive species <italic>Plantago virginica</italic>, but has no effect on its native congener <italic>P. asiatica</italic> (<xref ref-type="bibr" rid="B35">Luo et&#xa0;al., 2020</xref>). However, different nitrogen supply levels will change the competitive advantage of invasive plants. For example, the growth advantage of the invasive species <italic>Solidago canadensis</italic> compared to the native species <italic>Artemisia argyi</italic> was found to decrease with increasing soil nitrogen availability (<xref ref-type="bibr" rid="B46">Ren et&#xa0;al., 2021</xref>), and under low nitrogen levels, the invasive species <italic>Robinia pseudoacacia</italic> strongly inhibits the growth of native accompanying species <italic>Quercus acutissima</italic>, while high nitrogen levels reduce the competitiveness of <italic>R</italic>. <italic>pseudoacacia</italic> (<xref ref-type="bibr" rid="B33">Lou et&#xa0;al., 2014</xref>). Some studies have also found that nitrogen addition inhibits the growth of both invasive and native species (<xref ref-type="bibr" rid="B48">Ross et&#xa0;al., 2011</xref>). However, studies of interspecific competition between invasive plants and noninvasive alien plants are relatively rare (but see <xref ref-type="bibr" rid="B56">Wang et&#xa0;al., 2019a</xref>). Comparing the different responses of these two plant types to nitrogen addition can help to clarify plant invasion mechanisms and predict the succession dynamics of invaded communities.</p>
<p>
<italic>Alternanthera philoxeroides</italic>, a noxious weed native to South America with clonal growth, has widely invaded many countries including the United States, China, New Zealand, Australia, and India (<xref ref-type="bibr" rid="B62">Wu et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B63">Wu et&#xa0;al., 2017a</xref>). Due to its strong phenotypic plasticity, <italic>A. philoxeroides</italic> has invaded terrestrial and aquatic habitats in more than 20 provinces in China, causing serious damage to ecosystem function and native plant diversity (<xref ref-type="bibr" rid="B54">Tanveer et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B69">Yan et&#xa0;al., 2020</xref>). Previous studies have shown that <italic>A</italic>. <italic>philoxeroides</italic> has a strong allelopathic effect on the seed germination, seedling growth, and biomass accumulation of native plants, and the allelopathic effect of the underground parts is higher than that of the aboveground parts (<xref ref-type="bibr" rid="B6">Cui et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B19">Hu et&#xa0;al., 2023</xref>). Global warming increases the interspecific competitiveness of <italic>A</italic>. <italic>philoxeroides</italic> with the native co-occurring species <italic>Digitaria sanguinalis</italic> (<xref ref-type="bibr" rid="B65">Wu et&#xa0;al., 2017b</xref>). Nitrogen addition significantly increases the aboveground biomass accumulation of <italic>A</italic>. <italic>philoxeroides</italic>, which benefits its rapidly invasion in new habitats (<xref ref-type="bibr" rid="B58">Wang et&#xa0;al., 2015</xref>). A few studies have found that some native plants have a stronger resistance to <italic>A</italic>. <italic>philoxeroides</italic> invasion (<xref ref-type="bibr" rid="B59">Wang et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B73">Zhang et&#xa0;al., 2021</xref>). Like <italic>A</italic>. <italic>philoxeroides</italic>, <italic>Oxalis articulata</italic> is also native to South America; it has strong environmental tolerance and has been introduced into China as a horticultural and ornamental plant, and is now widely used in urban greening, landscape configuration, and ecological corridor construction (<xref ref-type="bibr" rid="B38">Oberlander et&#xa0;al., 2009</xref>). <italic>O</italic>. <italic>articulata</italic> is a typical noninvasive alien species in China; its strong tuber propagation capacity and developed root system enable it to quickly occupy vacant niches (<xref ref-type="bibr" rid="B49">Shiraishi et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B25">Li et&#xa0;al., 2021</xref>). In addition, <italic>O</italic>. <italic>articulata</italic> has a lower leaf construction cost and allocates more nitrogen to photosynthesis (<xref ref-type="bibr" rid="B14">Feng et&#xa0;al., 2008</xref>). In natural ecosystems, <italic>O</italic>. <italic>articulata</italic> can coexist with <italic>A</italic>. <italic>philoxeroides</italic> in large areas (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>). Based on niche theory, screening noninvasive plants with strong competitiveness to occupy vacant niches, thus controlling replacement by invasive plants, would be beneficial for achieving sustainable ecological management of bioinvasions (<xref ref-type="bibr" rid="B21">Jia et&#xa0;al., 2022</xref>).</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Single-dominant species community of <bold>(A)</bold> <italic>Alternanthera philoxeroides</italic>, <bold>(B)</bold> <italic>Oxalis articulata</italic>, and <bold>(C)</bold> their symbiotic communities in natural ecosystem. Photo: Hao Wu; location: roadside of Xinyang City, Henan Province, China.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g001.tif"/>
</fig>
<p>Currently, there are many studies on the competition between <italic>A</italic>. <italic>philoxeroides</italic> and native plants; however, competition between <italic>A</italic>. <italic>philoxeroides</italic> and noninvasive alien plants remains unclear, and it is crucial to understand this in order to predict situations of <italic>A</italic>. <italic>philoxeroides</italic> under increasing global nitrogen deposition. We conducted a greenhouse experiment to explore the effect of nitrogen addition on the performance of these two plants under different cultivation methods (monocultures and mixed cultures). We hypothesized that nitrogen would significantly affect their interspecific competitiveness. Specifically, we posed the following questions: (1) Do the biomass, nutritional, physiological, and photosynthetic traits of <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic> cause them to have heterogeneous responses to nitrogen addition? (2) Does nitrogen addition increase the resistance of <italic>O</italic>. <italic>articulata</italic> to <italic>A</italic>. <italic>philoxeroides</italic> invasion?</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Plant materials</title>
<p>In this study, an original population of <italic>A</italic>. <italic>philoxeroides</italic> and tubers of <italic>O</italic>. <italic>articulata</italic> were collected from a symbiotic community of these two plants in the field. The method of stem node cutting was used for <italic>A</italic>. <italic>philoxeroides</italic> propagation: we cut a 2&#xa0;cm stem of <italic>A</italic>. <italic>philoxeroides</italic> with the node and buried it in a plug for seedling cultivation (<xref ref-type="bibr" rid="B65">Wu et&#xa0;al., 2017b</xref>). Healthy tubers of <italic>O</italic>. <italic>articulate</italic> were selected from the soil of the symbiotic community for disinfection and sterilization, and we then sowed them in the plug for seedling cultivation (<xref ref-type="bibr" rid="B49">Shiraishi et&#xa0;al., 2005</xref>). After <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic> grew 2 true leaves, the seedlings of 2 plants that had similar growth were transplanted into plastic pots for experimental treatments.</p>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Experiment design</title>
<p>Three factors were set in the <ext-link ext-link-type="uri" xlink:href="https://www.baidu.com/link?url=H7MO6VUoHa6leH5_4rCUTW1nBqNG4XqdcZCCJ96Pt1Ox74OIcrknsknN5SjDQfE4BkqFnSLftFalk4hSjEyTyzkNDAEAcUkf5qRY-dqs-q08EaVoEnJxjxZMDn-mRfnAcMiiiXOsGKjpslzp6lGhMioKCsrzrr1D-ado246PPjpj4Xa-I2A-SXLDfpc65VrGap4xC_wC8HANv9yE0j38-UiKbaspKjw9BPFaE_-_BRRB1QrAAhcwwCaSawsp2N3tDXNSRVc_z_oBSpqY7rpUlVw1zd5d2ENp7xXnVQPYDM3ejlpWvwXLXtDA5umpamH_Mzw9DRHmudu2Zl-NKYVBlq&amp;wd=&amp;eqid=96d3dee90002881a00000003643d1196">greenhouse experiment</ext-link>: nitrogen treatment (control, nitrogen addition), planting type (monocultures, mixed cultures), and species (<italic>A</italic>. <italic>philoxeroides</italic>, <italic>O</italic>. <italic>articulata</italic>). Each treatment combination was replicated 5 times. We collected field soil from the <italic>A</italic>. <italic>philoxeroides</italic>&#x2013;<italic>O</italic>. <italic>articulata</italic> symbiotic ecosystem (content of ammonium nitrogen, nitrate nitrogen, available phosphorus and available potassium was 103.029, 105.830, 125.724, and 44.667 mg&#xb7;kg<sup>&#x2212;1</sup>, respectively, and pH was 7.611) and mixed it with perlite and sand at a ratio of 4:2:1 to prepare the experimental soil. We sterilized the experimental soil by autoclaving it at 121&#xb0;C for 120&#xa0;min in a vertical sterilizer (BKQ-B12011, China) to eliminate the interference of soil microorganism and seeds from other plant species. Based on the de Wit replacement series experiment (<xref ref-type="bibr" rid="B65">Wu et&#xa0;al., 2017b</xref>), 2 individuals were planted in each plastic pot (20&#xa0;cm dia &#xd7; 17&#xa0;cm h), and the proportions of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic> in the pots were 1:0, 1:1, and 0:1.</p>
<p>All treatment combinations were cultured in a smart greenhouse to eliminate the interference of nitrogen from rainfall. After transplanting all plant seedlings, each pot was covered with a mesh net (30&#xa0;cm dia &#xd7; 50&#xa0;cm h) to prevent herbivores from feeding and to eliminate mutual interference between pots. The cultivation conditions in the greenhouse were set as 14&#xa0;h light with temperature, humidity, and light intensity of 27 &#xb0;C, 60%, and 70%, respectively, and 10&#xa0;h darkness with temperature, humidity, and light intensity of 20 &#xb0;C, 60%, and 0%, respectively.</p>
<p>We used ammonium nitrate (NH<sub>4</sub>NO<sub>3</sub>) for the nitrogen treatment in this study, and the nitrogen addition standard was the maximum deposition amount of 63.53&#xa0;kg N ha<sup>&#x2212;1</sup> yr<sup>&#x2212;1</sup> in South China (<xref ref-type="bibr" rid="B31">Liu et&#xa0;al., 2013</xref>); converted for our experiment, this was 0.570&#xa0;g NH<sub>4</sub>NO<sub>3</sub> per pot. The NH<sub>4</sub>NO<sub>3</sub> crystals were dissolved in distilled water to prepare the solution, and we added the solution to the experimental treatment pots 3 times (10th, 20th, and 30th day after plants were cultured in the greenhouse), while equal amounts of distilled water were added to the control pots. After nitrogen was added 3 times, we continued to cultivate the plants for 10 days and then measured their various indicators. The entire cultivation time in the greenhouse was 40 days (May 17 to June 27, 2022).</p>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Data collection</title>
<p>We randomly selected 3 healthy leaves from each plant and measured their nitrogen balance index (NBI), chlorophyll a index (Chla), flavonoid index (Flav), and anthocyanin index (Anth) using a handheld leaf-clip instrument (Dualex, France). After 15&#xa0;min of adaptation in the dark for the plants in each pot, we used a chlorophyll fluorescence imaging system (FluorCam, Czech Republic) to measure the fluorescence parameters of each plant, including initial fluorescence (F<sub>0</sub>), maximal fluorescence (F<sub>m</sub>), maximum photochemical quantum yield (QY_max), photochemical quenching coefficient (qP_Lss), steady-state fluorescence decay efficiency (Rfd_Lss), and steady-state photochemical quantum (QY_Lss).</p>
<p>We used a flexible ruler to measure the maximum stem length of each plant. We randomly selected 3 healthy leaves from each plant and used the ScanMaker i800 scanner (Microtek, China) to measure their area and took the average value. We dug out all plants from soil and washed them clean, and measured the total root length and area of each plant using the ScanMaker i800 scanner. We then placed the entire plants in a drying oven (Leirun 101-4A, China) at 75 &#xb0;C for 48&#xa0;h to constant weight, and measured their total biomass, stem biomass, and root biomass and calculated the root/shoot ratio. After grinding and crushing the plants and passing them through a 70 mesh sieve, we measured their total carbon (C) and total nitrogen (N) content using the vario TOC cube (Elementar, Germany), and calculated the carbon/nitrogen (C:N) ratio.</p>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>Statistical analysis</title>
<p>We conducted multi-way ANOVA using SPSS 16.0 software (SPSS Inc., USA) to examine the effects of nitrogen treatment, planting type, species, and their interactions on the various indicators of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic> that were measured. The normality and homogeneity of the data were verified by using the &#x201c;Homogeneity of variance test&#x201d;, and data with non-random distribution were square-root transformed before conducting the ANOVA. When the ANOVA indicated significant effects (<italic>P</italic> &lt; 0.05), the means of treatment combinations were compared using multiple comparisons with Fisher&#x2019;s protected least significant difference (LSD) test (subset for <italic>a</italic> = 0.05) in SPSS 16.0. We preferentially analyzed the results with significant three-factor and two-factor interactive effects between nitrogen and other factors and significant single effect of nitrogen treatment.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<sec id="s3_1">
<label>3.1</label>
<title>Effect of nitrogen addition on plant morphology</title>
<p>The interaction of nitrogen treatment, species, and planting type had a significant effect on maximum stem length (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 4.393, <italic>P</italic> = 0.044) and total root length (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 21.138, <italic>P</italic> &lt; 0.001). The interaction of nitrogen treatment and species had a significant effect on total root area (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 4.455, <italic>P</italic> = 0.043). Nitrogen treatment had a significant effect on leaf area (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 24.356, <italic>P</italic> &lt; 0.001) (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>).</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Multi-way ANOVA for effects of nitrogen treatment (N), planting type (P), and species (S) and their interactions on plant morphology.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center" rowspan="2">Source</th>
<th valign="middle" align="center" rowspan="2">
<italic>df</italic>
</th>
<th valign="middle" colspan="2" align="center">Maximum length of stem</th>
<th valign="middle" colspan="2" align="center">Total root length</th>
<th valign="middle" colspan="2" align="center">Total root area</th>
<th valign="middle" colspan="2" align="center">Average single leaf area</th>
</tr>
<tr>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">N</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">32.895</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">1.471</td>
<td valign="top" align="center">0.234</td>
<td valign="top" align="center">7.284</td>
<td valign="top" align="center">
<italic>0.011</italic>
</td>
<td valign="top" align="center">24.356</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.024</td>
<td valign="top" align="center">0.879</td>
<td valign="top" align="center">14.410</td>
<td valign="top" align="center">
<italic>0.001</italic>
</td>
<td valign="top" align="center">0.207</td>
<td valign="top" align="center">0.652</td>
<td valign="top" align="center">0.000</td>
<td valign="top" align="center">0.998</td>
</tr>
<tr>
<td valign="top" align="center">S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">237.062</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">36.893</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">47.136</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">89.968</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.152</td>
<td valign="top" align="center">0.291</td>
<td valign="top" align="center">7.507</td>
<td valign="top" align="center">
<italic>0.010</italic>
</td>
<td valign="top" align="center">1.647</td>
<td valign="top" align="center">0.209</td>
<td valign="top" align="center">0.012</td>
<td valign="top" align="center">0.913</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.607</td>
<td valign="top" align="center">0.442</td>
<td valign="top" align="center">7.604</td>
<td valign="top" align="center">
<italic>0.010</italic>
</td>
<td valign="top" align="center">4.455</td>
<td valign="top" align="center">
<italic>0.043</italic>
</td>
<td valign="top" align="center">0.149</td>
<td valign="top" align="center">0.702</td>
</tr>
<tr>
<td valign="top" align="center">P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.126</td>
<td valign="top" align="center">0.725</td>
<td valign="top" align="center">14.453</td>
<td valign="top" align="center">
<italic>0.001</italic>
</td>
<td valign="top" align="center">0.039</td>
<td valign="top" align="center">0.845</td>
<td valign="top" align="center">0.426</td>
<td valign="top" align="center">0.519</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">4.393</td>
<td valign="top" align="center">
<italic>0.044</italic>
</td>
<td valign="top" align="center">21.138</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">0.187</td>
<td valign="top" align="center">0.668</td>
<td valign="top" align="center">0.034</td>
<td valign="top" align="center">0.855</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Multiple comparisons showed that nitrogen addition significantly increased the maximum stem length of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic> in monocultures by 43.682 and 131.828%, and in mixed cultures by 8.406 and 225.350%, respectively (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2A</bold>
</xref>). In monocultures, nitrogen addition significantly decreased the root length of <italic>A</italic>. <italic>philoxeroides</italic> by 7.510%, while in mixed cultures, nitrogen addition significantly decreased the root length of <italic>O</italic>. <italic>articulata</italic> by 56.974% but increased the root length of <italic>A</italic>. <italic>philoxeroides</italic> by 130.026% (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2B</bold>
</xref>). Nitrogen addition significantly increased the total root area of <italic>O</italic>. <italic>articulata</italic> by 47.331 and 128.489% in the monocultures and mixed cultures, respectively (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2C</bold>
</xref>). Nitrogen addition significantly increased the leaf area of plants by 59.110% compared to the control (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2D</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Multiple comparisons of <bold>(A)</bold> maximum length of stem, <bold>(B)</bold> total root length, <bold>(C)</bold> total root area, and <bold>(D)</bold> average single leaf area among treatments. Different capital letters indicate the significant three-factor interactive effects among nitrogen treatment, planting type, and species (<italic>P</italic> &lt; 0.05), different lowercase letters indicate significant two-factor interactive effects between nitrogen treatment and other factors (<italic>P</italic> &lt; 0.05), and stars indicate significant differences between single factors (<italic>P</italic> &lt; 0.05). The same applies below.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g002.tif"/>
</fig>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Effect of nitrogen addition on plant biomass</title>
<p>Nitrogen treatment and its interaction with other factors had no significant effect on plant biomass; the differences in biomass mainly came from the effect of species (<xref ref-type="table" rid="T2">
<bold>Table&#xa0;2</bold>
</xref>). Multiple comparisons showed that the total biomass, shoot biomass, root biomass, and root/shoot ratio of <italic>O</italic>. <italic>articulata</italic> were significantly higher than those of <italic>A</italic>. <italic>philoxeroides</italic> by 301.887, 35.289, 563.960, and 469.917%, respectively (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>).</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Multi-way ANOVA for effects of nitrogen treatment (N), planting type (P), and species (S) and their interactions on plant biomass.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center" rowspan="2">Source</th>
<th valign="middle" align="center" rowspan="2">
<italic>df</italic>
</th>
<th valign="top" colspan="2" align="center">Total biomass</th>
<th valign="top" colspan="2" align="center">Shoot biomass</th>
<th valign="top" colspan="2" align="center">Root biomass</th>
<th valign="top" colspan="2" align="center">Root/Shoot ratio</th>
</tr>
<tr>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">N</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.957</td>
<td valign="top" align="center">0.335</td>
<td valign="top" align="center">3.310</td>
<td valign="top" align="center">0.078</td>
<td valign="top" align="center">0.452</td>
<td valign="top" align="center">0.506</td>
<td valign="top" align="center">0.035</td>
<td valign="top" align="center">0.852</td>
</tr>
<tr>
<td valign="top" align="center">P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.705</td>
<td valign="top" align="center">0.407</td>
<td valign="top" align="center">0.661</td>
<td valign="top" align="center">0.422</td>
<td valign="top" align="center">0.864</td>
<td valign="top" align="center">0.359</td>
<td valign="top" align="center">0.070</td>
<td valign="top" align="center">0.794</td>
</tr>
<tr>
<td valign="top" align="center">S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">106.688</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">100.421</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">71.629</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">19.115</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.150</td>
<td valign="top" align="center">0.701</td>
<td valign="top" align="center">0.052</td>
<td valign="top" align="center">0.821</td>
<td valign="top" align="center">0.115</td>
<td valign="top" align="center">0.736</td>
<td valign="top" align="center">0.314</td>
<td valign="top" align="center">0.579</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.606</td>
<td valign="top" align="center">0.442</td>
<td valign="top" align="center">1.023</td>
<td valign="top" align="center">0.319</td>
<td valign="top" align="center">0.360</td>
<td valign="top" align="center">0.553</td>
<td valign="top" align="center">0.129</td>
<td valign="top" align="center">0.722</td>
</tr>
<tr>
<td valign="top" align="center">P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.942</td>
<td valign="top" align="center">0.339</td>
<td valign="top" align="center">0.342</td>
<td valign="top" align="center">0.563</td>
<td valign="top" align="center">1.044</td>
<td valign="top" align="center">0.315</td>
<td valign="top" align="center">0.228</td>
<td valign="top" align="center">0.636</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.118</td>
<td valign="top" align="center">0.734</td>
<td valign="top" align="center">0.026</td>
<td valign="top" align="center">0.872</td>
<td valign="top" align="center">0.094</td>
<td valign="top" align="center">0.761</td>
<td valign="top" align="center">0.367</td>
<td valign="top" align="center">0.549</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Multiple comparisons of <bold>(A)</bold> total biomass, <bold>(B)</bold> shoot biomass, <bold>(C)</bold> root biomass, and <bold>(D)</bold> root/shoot ratio among treatments. &#x201c;*&#x201d; indicates the significant differences between species (<italic>P</italic> &lt; 0.05).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g003.tif"/>
</fig>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>Effect of nitrogen addition on plant nutrients</title>
<p>Nitrogen treatment and its interaction with other factors had no significant effect on total C in plants (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4A</bold>
</xref>). The interaction of nitrogen treatment and species had a significant effect on the total N (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 5.157, <italic>P</italic> = 0.030) and C:N ratio (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 28.780, <italic>P</italic> &lt; 0.001) (<xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>). Multiple comparisons showed that nitrogen addition significantly increased the total N in <italic>A</italic>. <italic>philoxeroides</italic> by 278.767% compared to the control, and caused <italic>A</italic>. <italic>philoxeroides</italic> to have 60.134% more total N than <italic>O</italic>. <italic>articulata</italic> the mixed cultures (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4B</bold>
</xref>). Compared to the control, nitrogen addition significantly decreased the C:N ratio of <italic>A</italic>. <italic>philoxeroides</italic> by 52.263 and 66.110% in monocultures and mixed cultures, respectively (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4C</bold>
</xref>).</p>
<table-wrap id="T3" position="float">
<label>Table&#xa0;3</label>
<caption>
<p>Multi-way ANOVA for effects of nitrogen treatment (N), planting type (P), and species (S) and their interactions on plant nutrients.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center" rowspan="2">Source</th>
<th valign="middle" align="center" rowspan="2">
<italic>df</italic>
</th>
<th valign="top" colspan="2" align="center">Total carbon (C)</th>
<th valign="top" colspan="2" align="center">Total nitrogen (N)</th>
<th valign="top" colspan="2" align="center">C/N ratio</th>
</tr>
<tr>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">N</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.255</td>
<td valign="top" align="center">0.271</td>
<td valign="top" align="center">9.707</td>
<td valign="top" align="center">
<italic>0.004</italic>
</td>
<td valign="top" align="center">84.395</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.179</td>
<td valign="top" align="center">0.675</td>
<td valign="top" align="center">0.013</td>
<td valign="top" align="center">0.910</td>
<td valign="top" align="center">1.807</td>
<td valign="top" align="center">0.188</td>
</tr>
<tr>
<td valign="top" align="center">S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.736</td>
<td valign="top" align="center">0.197</td>
<td valign="top" align="center">2.851</td>
<td valign="top" align="center">0.101</td>
<td valign="top" align="center">23.421</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.909</td>
<td valign="top" align="center">0.347</td>
<td valign="top" align="center">1.657</td>
<td valign="top" align="center">0.207</td>
<td valign="top" align="center">2.918</td>
<td valign="top" align="center">0.097</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.704</td>
<td valign="top" align="center">0.408</td>
<td valign="top" align="center">5.157</td>
<td valign="top" align="center">
<italic>0.030</italic>
</td>
<td valign="top" align="center">28.780</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">3.272</td>
<td valign="top" align="center">0.080</td>
<td valign="top" align="center">3.681</td>
<td valign="top" align="center">0.064</td>
<td valign="top" align="center">1.482</td>
<td valign="top" align="center">0.232</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.549</td>
<td valign="top" align="center">0.222</td>
<td valign="top" align="center">3.408</td>
<td valign="top" align="center">0.074</td>
<td valign="top" align="center">3.068</td>
<td valign="top" align="center">0.089</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Multiple comparisons of <bold>(A)</bold> total carbon, <bold>(B)</bold> total nitrogen, and <bold>(C)</bold> carbon/nitrogen ratio among treatments. Different lowercase letters indicate significant two-factor interactive effects between nitrogen treatment and species (<italic>P</italic> &lt; 0.05), and &#x201c;ns&#x201d; indicates no significant difference.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g004.tif"/>
</fig>
</sec>
<sec id="s3_4">
<label>3.4</label>
<title>Effects of nitrogen addition on plant physiology</title>
<p>Nitrogen treatment had a significant effect on NBI (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 7.522, <italic>P</italic> = 0.011). The interaction of nitrogen treatment and species had a significant effect on Flav (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 14.299, <italic>P</italic> = 0.001) and Anth (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 12.551, <italic>P</italic> = 0.001). The interaction of nitrogen treatment and other factors had no significant effect on Chla (<xref ref-type="table" rid="T4">
<bold>Table&#xa0;4</bold>
</xref>; <xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5B</bold>
</xref>). Multiple comparisons showed that nitrogen addition significantly increased the NBI of plants by 113.526% compared to the control (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5A</bold>
</xref>). Nitrogen addition significantly decreased the Flav of <italic>O</italic>. <italic>articulata</italic> by 69.361 and 60.671% in monocultures and mixed cultures, respectively (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5C</bold>
</xref>). Nitrogen addition significantly increased the Anth of <italic>O</italic>. <italic>articulata</italic> by 37.931 and 39.091% in monocultures and mixed cultures, respectively (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5D</bold>
</xref>).</p>
<table-wrap id="T4" position="float">
<label>Table&#xa0;4</label>
<caption>
<p>Multi-way ANOVA for effects of nitrogen treatment (N), planting type (P), and species (S) and their interactions on plant physiology.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center" rowspan="2">Source</th>
<th valign="middle" align="center" rowspan="2">
<italic>df</italic>
</th>
<th valign="top" colspan="2" align="center">NBI</th>
<th valign="top" colspan="2" align="center">Chla</th>
<th valign="top" colspan="2" align="center">Flav</th>
<th valign="top" colspan="2" align="center">Anth</th>
</tr>
<tr>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">N</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">7.522</td>
<td valign="top" align="center">
<italic>0.011</italic>
</td>
<td valign="top" align="center">2.533</td>
<td valign="top" align="center">0.123</td>
<td valign="top" align="center">8.508</td>
<td valign="top" align="center">
<italic>0.007</italic>
</td>
<td valign="top" align="center">18.786</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.393</td>
<td valign="top" align="center">0.248</td>
<td valign="top" align="center">0.215</td>
<td valign="top" align="center">0.647</td>
<td valign="top" align="center">6.411</td>
<td valign="top" align="center">
<italic>0.017</italic>
</td>
<td valign="top" align="center">0.001</td>
<td valign="top" align="center">0.974</td>
</tr>
<tr>
<td valign="top" align="center">S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">2.093</td>
<td valign="top" align="center">0.159</td>
<td valign="top" align="center">1.850</td>
<td valign="top" align="center">0.185</td>
<td valign="top" align="center">0.372</td>
<td valign="top" align="center">0.547</td>
<td valign="top" align="center">25.009</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.039</td>
<td valign="top" align="center">0.845</td>
<td valign="top" align="center">0.650</td>
<td valign="top" align="center">0.427</td>
<td valign="top" align="center">1.000</td>
<td valign="top" align="center">0.326</td>
<td valign="top" align="center">0.001</td>
<td valign="top" align="center">0.980</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.933</td>
<td valign="top" align="center">0.342</td>
<td valign="top" align="center">0.269</td>
<td valign="top" align="center">0.608</td>
<td valign="top" align="center">14.299</td>
<td valign="top" align="center">
<italic>0.001</italic>
</td>
<td valign="top" align="center">12.551</td>
<td valign="top" align="center">
<italic>0.001</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">2.627</td>
<td valign="top" align="center">0.116</td>
<td valign="top" align="center">0.937</td>
<td valign="top" align="center">0.341</td>
<td valign="top" align="center">3.694</td>
<td valign="top" align="center">0.065</td>
<td valign="top" align="center">8.969</td>
<td valign="top" align="center">
<italic>0.006</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.045</td>
<td valign="top" align="center">0.834</td>
<td valign="top" align="center">0.079</td>
<td valign="top" align="center">0.781</td>
<td valign="top" align="center">0.002</td>
<td valign="top" align="center">0.963</td>
<td valign="top" align="center">0.363</td>
<td valign="top" align="center">0.552</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Multiple comparisons of <bold>(A)</bold> nitrogen balance index (NBI), <bold>(B)</bold> chlorophyll a index (Chla), <bold>(C)</bold> flavonoid index (Flav), and <bold>(D)</bold> anthocyanin index (Anth) among treatments. Different lowercase letters indicate significant two-factor interactive effects between nitrogen treatment and species (<italic>P</italic> &lt; 0.05), and &#x201c;*&#x201d; indicates the significant differences between nitrogen treatment (<italic>P</italic> &lt; 0.05).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g005.tif"/>
</fig>
</sec>
<sec id="s3_5">
<label>3.5</label>
<title>Effect of nitrogen addition on plant photosynthetic fluorescence</title>
<p>Photosynthetic fluorescence imaging is shown in <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6</bold>
</xref>. The interaction of nitrogen treatment and planting type (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 4.630, <italic>P</italic> = 0.039) and of nitrogen treatment and species (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 5.618, <italic>P</italic> = 0.024) had a significant effect on F<sub>0</sub>. The interaction of nitrogen treatment and species had a significant effect on F<sub>m</sub> (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 13.880, <italic>P</italic> = 0.001). Nitrogen treatment had a significant effect on both QY_ max(<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 5.818, <italic>P</italic> = 0.022) and QY_ Lss (<italic>F</italic>
<sub>1, 32&#xa0;</sub>= 4.411, <italic>P</italic> = 0.044). The interaction of nitrogen treatment and other factors had no significant effect on qP_ Lss and Rfd_ Lss (<xref ref-type="table" rid="T5">
<bold>Table&#xa0;5</bold>
</xref>).</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Use of chlorophyll fluorescence imaging in different treatment combinations: <bold>(A&#x2013;C)</bold> <italic>Alternanthera philoxeroides</italic> in monocultures, <italic>Oxalis articulata</italic> in monocultures, and <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic> in mixed cultures under control treatment; <bold>(D&#x2013;F)</bold> <italic>A</italic>. <italic>philoxeroides</italic> in monocultures, <italic>O</italic>. <italic>articulata</italic> in monocultures, and <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic> in mixed cultures under nitrogen addition. Images of leaves of <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic> show spatiotemporal variation in chlorophyll fluorescence at steady state of induction curve with actinic illumination of 200 &#x3bc; mol photons m<sup>&#x2212;2</sup> s<sup>&#x2212;1</sup> after 15&#xa0;min dark adaptation. Color scale to the right of each image indicates range of fluorescence values (from black to pink), with brighter color indicating higher value.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g006.tif"/>
</fig>
<table-wrap id="T5" position="float">
<label>Table&#xa0;5</label>
<caption>
<p>Multi-way ANOVA for effects of nitrogen treatment (N), planting type (P), and species (S) and their interactions on plant photosynthetic fluorescence.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center" rowspan="2">Source</th>
<th valign="middle" align="center" rowspan="2">
<italic>df</italic>
</th>
<th valign="top" colspan="2" align="center">F<sub>0</sub>
</th>
<th valign="top" colspan="2" align="center">F<sub>m</sub>
</th>
<th valign="top" colspan="2" align="center">QY_max</th>
<th valign="top" colspan="2" align="center">qP_Lss</th>
<th valign="top" colspan="2" align="center">Rfd_Lss</th>
<th valign="top" colspan="2" align="center">QY_Lss</th>
</tr>
<tr>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
<th valign="top" align="center">
<italic>F</italic>
</th>
<th valign="top" align="center">
<italic>P</italic>
</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">N</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.052</td>
<td valign="top" align="center">0.820</td>
<td valign="top" align="center">5.836</td>
<td valign="top" align="center">
<italic>0.022</italic>
</td>
<td valign="top" align="center">5.818</td>
<td valign="top" align="center">
<italic>0.022</italic>
</td>
<td valign="top" align="center">0.900</td>
<td valign="top" align="center">0.350</td>
<td valign="top" align="center">0.738</td>
<td valign="top" align="center">0.397</td>
<td valign="top" align="center">4.411</td>
<td valign="top" align="center">
<italic>0.044</italic>
</td>
</tr>
<tr>
<td valign="top" align="center">P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">2.019</td>
<td valign="top" align="center">0.165</td>
<td valign="top" align="center">1.459</td>
<td valign="top" align="center">0.236</td>
<td valign="top" align="center">3.240</td>
<td valign="top" align="center">0.081</td>
<td valign="top" align="center">1.030</td>
<td valign="top" align="center">0.318</td>
<td valign="top" align="center">8.499</td>
<td valign="top" align="center">
<italic>0.006</italic>
</td>
<td valign="top" align="center">0.355</td>
<td valign="top" align="center">0.556</td>
</tr>
<tr>
<td valign="top" align="center">S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">5.541</td>
<td valign="top" align="center">
<italic>0.025</italic>
</td>
<td valign="top" align="center">2.327</td>
<td valign="top" align="center">0.137</td>
<td valign="top" align="center">0.784</td>
<td valign="top" align="center">0.382</td>
<td valign="top" align="center">3.049</td>
<td valign="top" align="center">0.090</td>
<td valign="top" align="center">26.910</td>
<td valign="top" align="center">
<italic>&lt;0.001</italic>
</td>
<td valign="top" align="center">0.932</td>
<td valign="top" align="center">0.342</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">4.630</td>
<td valign="top" align="center">
<italic>0.039</italic>
</td>
<td valign="top" align="center">0.305</td>
<td valign="top" align="center">0.584</td>
<td valign="top" align="center">1.823</td>
<td valign="top" align="center">0.186</td>
<td valign="top" align="center">3.012</td>
<td valign="top" align="center">0.092</td>
<td valign="top" align="center">0.453</td>
<td valign="top" align="center">0.506</td>
<td valign="top" align="center">0.160</td>
<td valign="top" align="center">0.692</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">5.618</td>
<td valign="top" align="center">
<italic>0.024</italic>
</td>
<td valign="top" align="center">13.880</td>
<td valign="top" align="center">
<italic>0.001</italic>
</td>
<td valign="top" align="center">1.352</td>
<td valign="top" align="center">0.254</td>
<td valign="top" align="center">0.436</td>
<td valign="top" align="center">0.514</td>
<td valign="top" align="center">0.610</td>
<td valign="top" align="center">0.440</td>
<td valign="top" align="center">0.025</td>
<td valign="top" align="center">0.875</td>
</tr>
<tr>
<td valign="top" align="center">P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">0.857</td>
<td valign="top" align="center">0.362</td>
<td valign="top" align="center">4.976</td>
<td valign="top" align="center">
<italic>0.033</italic>
</td>
<td valign="top" align="center">7.271</td>
<td valign="top" align="center">
<italic>0.011</italic>
</td>
<td valign="top" align="center">0.663</td>
<td valign="top" align="center">0.422</td>
<td valign="top" align="center">0.124</td>
<td valign="top" align="center">0.728</td>
<td valign="top" align="center">0.924</td>
<td valign="top" align="center">0.344</td>
</tr>
<tr>
<td valign="top" align="center">N &#xd7; P &#xd7; S</td>
<td valign="top" align="center">1, 32</td>
<td valign="top" align="center">1.681</td>
<td valign="top" align="center">0.204</td>
<td valign="top" align="center">1.115</td>
<td valign="top" align="center">0.299</td>
<td valign="top" align="center">0.299</td>
<td valign="top" align="center">0.588</td>
<td valign="top" align="center">0.041</td>
<td valign="top" align="center">0.841</td>
<td valign="top" align="center">0.021</td>
<td valign="top" align="center">0.886</td>
<td valign="top" align="center">0.669</td>
<td valign="top" align="center">0.419</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Multiple comparisons showed that nitrogen addition significantly decreased the F<sub>0</sub> of <italic>A</italic>. <italic>philoxeroides</italic> by 18.649% compared to control in mixed cultures (<xref ref-type="fig" rid="f7">
<bold>Figure&#xa0;7A</bold>
</xref>). Compared to control, nitrogen addition significantly decreased the F<sub>m</sub> of <italic>A</italic>. <italic>philoxeroides</italic> by 16.234 and 23.507% in monocultures and mixed cultures, respectively (<xref ref-type="fig" rid="f7">
<bold>Figure&#xa0;7B</bold>
</xref>). Nitrogen addition significantly decreased the QY_max and QY_Lss by 15.551 and 26.830% compared to control, respectively (<xref ref-type="fig" rid="f7">
<bold>Figures&#xa0;7C&#x2013;F</bold>
</xref>). The Rfd_Lss of <italic>A</italic>. <italic>philoxeroides</italic> was significantly higher than that of <italic>O</italic>. <italic>articulata</italic> by 128.368%, and the Rfd_Lss of plants in mixed cultures was significantly higher than that in monocultures by 56.312% (<xref ref-type="fig" rid="f7">
<bold>Figure&#xa0;7E</bold>
</xref>).</p>
<fig id="f7" position="float">
<label>Figure&#xa0;7</label>
<caption>
<p>Multiple comparisons of <bold>(A)</bold> initial fluorescence (F<sub>0</sub>), <bold>(B)</bold> maximal fluorescence (F<sub>m</sub>), <bold>(C)</bold> maximum photochemical quantum yield (QY_max), <bold>(D)</bold> photochemical quenching coefficient (qP_Lss), <bold>(E)</bold> steady-state fluorescence decay efficiency (Rfd_Lss), and <bold>(F)</bold> steady-state photochemical quantum (QY_Lss) among treatments. Different lowercase letters indicate significant two-factor interactive effects between nitrogen treatment and species (<italic>P</italic> &lt; 0.05), &#x201c;*&#x201d; indicates significant differences between single factors (<italic>P</italic> &lt; 0.05), and &#x201c;ns&#x201d; indicates no significant difference.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1215191-g007.tif"/>
</fig>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<p>Soil N enrichment could significantly alter the structure of ecosystems and considered as the third largest killer seriously threatening species diversity, after land-use changes and biotic exchanges (<xref ref-type="bibr" rid="B40">Phoenix et&#xa0;al., 2006</xref>). We found that nitrogen addition significantly increased the maximum stem length and leaf area of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic> in this study, indicating that it could relieve the constraints of limited resources on the growth of exotic plants and thus benefit their aboveground growth, as well as expand their living space and improve light utilization efficiency (<xref ref-type="bibr" rid="B47">Rickey and Anderson, 2004</xref>; <xref ref-type="bibr" rid="B39">Pan et&#xa0;al, 2016</xref>; <xref ref-type="bibr" rid="B60">Wang et&#xa0;al, 2020</xref>). However, nitrogen addition could also intensify the competition between coexisting plants for light resources (<xref ref-type="bibr" rid="B67">Xiao et&#xa0;al., 2021</xref>). The root is an important organ for plants to absorb soil nutrients (<xref ref-type="bibr" rid="B68">Xu et&#xa0;al., 2017</xref>), nitrogen addition decreased the root length but increased the root area of <italic>O</italic>. <italic>articulata</italic> in mixed cultures, which might be because nitrogen addition increases the availability of nitrogen in deep soil to the plant&#x2019;s root system thus the plant reduces its resource investment in root length but increases the contact areas between the root and the soil to absorb more nitrogen (<xref ref-type="bibr" rid="B68">Xu et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B60">Wang et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B74">Zhang et&#xa0;al., 2020a</xref>). Overall, nitrogen addition led to greater advantages for morphological traits of <italic>O</italic>. <italic>articulata</italic>, but also increased the root length of <italic>A</italic>. <italic>philoxeroides</italic> in mixed cultures, indicating that <italic>A</italic>. <italic>philoxeroides</italic> tends to absorb more nitrogen in deep soils to resist the competition of <italic>O</italic>. <italic>articulata</italic>.</p>
<p>Intuitive impact of interspecific competition on plant growth was preferentially reflected in biomass change (<xref ref-type="bibr" rid="B41">Poorter et&#xa0;al., 2012</xref>). Previous studies found that nitrogen addition could significantly promote the biomass accumulation of alien plants and thus rapidly accelerate their invasion process (<xref ref-type="bibr" rid="B8">Davis and Pelsor, 2001</xref>; <xref ref-type="bibr" rid="B7">Daehler, 2003</xref>). However, in our study we found that nitrogen addition did not increase the biomass of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic>. The reason for this might be that although invasive plants usually have higher nitrogen utilization rates, once invaded, they tend to evolve similar nitrogen adaptability to the co-occurring native plant species (<xref ref-type="bibr" rid="B16">Godoy et&#xa0;al., 2012</xref>). Particularly, the two plant species in this study were both alien species, thus the effect of nitrogen addition on their biomass allocation was not significant. Similar studies also showed that nitrogen addition did not increase the biomass of some invasive weeds (e.g., <italic>Centaurea diffusa</italic>) in North America (<xref ref-type="bibr" rid="B24">LeJeune et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B5">Cleland et&#xa0;al., 2011</xref>). However, we found that the biomass and root/shoot ratio of <italic>O</italic>. <italic>articulata</italic> were significantly higher than those of <italic>A</italic>. <italic>philoxeroides</italic>, which demonstrates the strong individual and underground competitive advantages of <italic>O</italic>. <italic>articulata</italic>.</p>
<p>The C:N ratio reflects the resource utilization strategy and efficiency of plants (<xref ref-type="bibr" rid="B71">Zhang et&#xa0;al., 2020b</xref>; <xref ref-type="bibr" rid="B28">Liu et&#xa0;al, 2021a</xref>). We found that nitrogen addition significantly increased the N content of <italic>A</italic>. <italic>philoxeroides</italic> in mixed cultures, making it higher than that of <italic>O</italic>. <italic>articulata</italic>, indicating that <italic>A</italic>. <italic>philoxeroides</italic> has stronger N accumulation ability than <italic>O</italic>. <italic>articulata</italic>. This is because nitrogen addition increases soil N enrichment and thus might alleviate the interspecific competition between plants (<xref ref-type="bibr" rid="B27">Liu et&#xa0;al., 2020</xref>). Moreover, the growth of invasive plants can usually better accumulate the increased soil nutrient pool, which makes them more capable of obtaining N under fluctuating resources (<xref ref-type="bibr" rid="B29">Liu et&#xa0;al., 2019</xref>). The C:N ratio of <italic>A</italic>. <italic>philoxeroides</italic> was higher than that of <italic>O</italic>. <italic>articulata</italic> in the control treatments, indicating that <italic>A</italic>. <italic>philoxeroides</italic> tends to evolve higher N utilization efficiency in an N-limited environment. Nitrogen addition decreased the C:N ratio of <italic>A</italic>. <italic>philoxeroides</italic>, suggesting that this plant might enhance protein synthesis <italic>in vivo</italic> at the cost of reducing N utilization efficiency. This trade-off of N utilization in <italic>A</italic>. <italic>philoxeroides</italic> in our study strongly supports the adaptive growth hypothesis (AGH), which is that maintaining a high C:N ratio in a low N environment will help invasive plants to improve their nutrient utilization efficiency and prioritize survival, while maintaining a low C:N ratio in a high N environment will enable invasive plants to obtain more resources and achieve rapid growth (<xref ref-type="bibr" rid="B53">Sun et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B71">Zhang et&#xa0;al., 2020b</xref>; <xref ref-type="bibr" rid="B15">Geng et&#xa0;al., 2023</xref>). However, a high N content in plants will increase their palatability and thus their susceptibility to herbivores by changing the interactions with high-trophic-level organisms; this might weaken the defensive ability of <italic>A</italic>. <italic>philoxeroides</italic> to resist insect feeding compared to <italic>O</italic>. <italic>articulata</italic> in their symbiotic communities (<xref ref-type="bibr" rid="B34">Lu et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B30">Liu et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B61">Waterton et&#xa0;al., 2022</xref>).</p>
<p>NBI, the chlorophyll/flavonoid ratio of plants, is an important indicator for evaluating plant growth (<xref ref-type="bibr" rid="B20">Ilyas et&#xa0;al., 2022</xref>). In this study, nitrogen addition led to an increase in NBI, which increased the chlorophyll content of the plants and benefitted their absorption and transformation of light energy, thus enhancing their growth (<xref ref-type="bibr" rid="B9">Deng et&#xa0;al., 2019</xref>). Flavonoids are secondary polyphenolic metabolites that exist widely in plants and have strong antibacterial, insect-resistant, and free radical scavenging activity, which can significantly increase the stress resistance and defense ability of plants (<xref ref-type="bibr" rid="B1">Agati et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B3">Cesco et&#xa0;al., 2012</xref>). Flav is usually used as an important indicator for evaluating the level of plant chemical defense (<xref ref-type="bibr" rid="B1">Agati et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B23">Landi et&#xa0;al., 2015</xref>). Nitrogen addition significantly decreased the Flav of <italic>O</italic>. <italic>articulata</italic>, possibly because the vegetative growth of <italic>O</italic>. <italic>articulata</italic> prioritizes its secondary metabolism to obtain more resources when growing in high-nutrient environment, that is, it reduces its chemical defense ability but enhances its growth to resist <italic>A</italic>. <italic>philoxeroides</italic> invasion in high-N soil. This also supports the growth-differentiation balance hypothesis (GDBH) regarding plant defense (<xref ref-type="bibr" rid="B32">Liu et&#xa0;al., 2022</xref>). In addition, significantly increased rates of plant growth and development and protein synthesis will also inhibit the secondary metabolic pathway of phenylalanine and thus reduce flavonoid synthesis (<xref ref-type="bibr" rid="B70">Zaghdoud et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B26">Liu et&#xa0;al., 2021b</xref>).</p>
<p>Anthocyanin, a water-soluble glycoside derivative that is widely distributed in plants, plays a crucial role in plants&#x2019; resistance to exogenous abiotic stresses (e.g., ultraviolet radiation) and biotic stresses (e.g., insect feeding and interspecific competition) (<xref ref-type="bibr" rid="B17">Gonzalez-Teuber et&#xa0;al., 2017</xref>). <xref ref-type="bibr" rid="B23">Landi et&#xa0;al. (2015)</xref> found that nitrogen addition can significantly increase the content of anthocyanins, which will absorb excess light energy and dissipate it in the form of heat energy, thus protecting the photosynthetic membrane of plants. In this study, we also found that nitrogen addition significantly increased the Anth of <italic>O</italic>. <italic>articulata</italic>, indicating that this alien species could synthesize a large amount of anthocyanins in an N-enriched environment to increase its environmental tolerance, thereby effectively responding to the interspecific competition caused by <italic>A</italic>. <italic>philoxeroides</italic> invasion (<xref ref-type="bibr" rid="B72">Zhang et&#xa0;al., 2017</xref>). In addition, nitrogen addition caused a significant trade-off between the Flav and Anth of <italic>O</italic>. <italic>articulata</italic>, indicating that soil nitrogen enrichment can enhance the physiological plasticity of alien plants and thus increase their competitiveness (<xref ref-type="bibr" rid="B66">Wu et&#xa0;al., 2023</xref>). However, nitrogen addition did not have a significant effect on the Flav and Anth of <italic>A</italic>. <italic>philoxeroides</italic> in our study, which might be due to its high internal eco-stoichiometric stability (<xref ref-type="bibr" rid="B52">Sun et&#xa0;al., 2019</xref>), and this may help <italic>A</italic>. <italic>philoxeroides</italic> rapidly evolve suitable growth strategies in environments with different nutrient levels (<xref ref-type="bibr" rid="B15">Geng et&#xa0;al., 2023</xref>). Furthermore, global climate changes have exacerbated the escape of <italic>A</italic>. <italic>philoxeroides</italic> from the bio-control of its natural enemy <italic>Agasicles hygrophila</italic>, and it can thus utilize the resources it originally used to resist natural enemies to eliminate the interference of soil N fluctuations on its growth (<xref ref-type="bibr" rid="B34">Lu et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B62">Wu et&#xa0;al., 2016</xref>).</p>
<p>Chlorophyll fluorescence imaging can comprehensively reflect the primary reaction processes of photosynthesis in plants, such as light energy absorption, excitation energy transfer, and photochemical reactions (<xref ref-type="bibr" rid="B10">Dong et&#xa0;al., 2019</xref>). Previous studies showed that applying appropriate amounts of N can increase the chlorophyll content and promote photosynthesis, while N stress (including its concentration and morphology) will lead to a decline in photosynthesis (<xref ref-type="bibr" rid="B4">Chen et&#xa0;al., 2023</xref>). In addition, different plants have different levels of energy consumption in the process of absorbing, transporting, and assimilating N, which might lead to excess light energy and accumulation of reactive oxygen (ROS) and thus damage the photosynthetic electron transport chain (<xref ref-type="bibr" rid="B23">Landi et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B57">Wang et&#xa0;al., 2019b</xref>). F<sub>0</sub> and F<sub>m</sub> represent the fluorescence yield when the PS II reaction center of plants is fully opened and closed, respectively, and they characterize the relationship between the plant&#x2019;s physiological status and habitat (<xref ref-type="bibr" rid="B37">Noor et&#xa0;al., 2022</xref>). We found that nitrogen addition decreased both F<sub>0</sub> and F<sub>m</sub> of <italic>A</italic>. <italic>philoxeroides</italic> in mixed cultures, and significantly weakened the advantage of F<sub>0</sub> and F<sub>m</sub> of <italic>A</italic>. <italic>philoxeroides</italic> over <italic>O</italic>. <italic>articulata</italic> compared with the control, indicating that nitrogen addition reduced the light absorption capacity of <italic>A</italic>. <italic>philoxeroides</italic> in interspecific competition. This might be due to the high soil N inhibiting the electron transfer of the plant&#x2019;s PS II reaction center (<xref ref-type="bibr" rid="B3">Cesco et&#xa0;al., 2012</xref>), whereas the PS II reaction center of <italic>O</italic>. <italic>articulata</italic> might be more sensitive to irritation, and can effectively respond to high soil N stress by increasing the anthocyanin content to absorb the excess energy that is dissipated in the form of heat and fluorescence under nitrogen addition (<xref ref-type="bibr" rid="B23">Landi et&#xa0;al., 2015</xref>).</p>
<p>QY_max represents the maximum potential photochemical quantum efficiency and utilization efficiency of the PS II reaction center, and is an important indicator for evaluating the effect of environmental stress on photosynthesis, while QY_Lss represents the light harvesting ability of plants, which reflects the actual photochemical efficiency of chloroplasts (<xref ref-type="bibr" rid="B13">Fei et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B73">Zhang et&#xa0;al., 2021</xref>). In our study, nitrogen addition significantly decreased both the QY_max and QY-Lss of plants compared with control, indicating that high soil N weakened the potential vitality of leaves and the electron transfer chain was interrupted due to decreased PS II activity, and the site of injury may be located at the PS II reaction center or primary electron receptor (<xref ref-type="bibr" rid="B50">Singh et&#xa0;al., 2017</xref>). qP_Lss represents the portion of light energy absorbed by the PSII reaction center that is actually used for photochemical electron transfer, which reflects the level of plant photosynthetic activity, and Rfd_Lss is used to evaluate the resistance of plants under environmental stress (<xref ref-type="bibr" rid="B22">Kramer et&#xa0;al., 2004</xref>). Nitrogen addition did not affect the qP_Lss and Rfd_Lss of <italic>O</italic>. <italic>articulata</italic> and <italic>A</italic>. <italic>philoxeroides</italic>, indicating that alien plants might have a more stable photosynthetic regulation strategy than native plants under soil nutrient fluctuations (<xref ref-type="bibr" rid="B43">Qing et&#xa0;al., 2012</xref>).</p>
</sec>
<sec id="s5" sec-type="conclusions">
<label>5</label>
<title>Conclusions</title>
<p>We found that nitrogen addition significantly increased the maximum stem length, root area, and leaf area of both <italic>A</italic>. <italic>philoxeroides</italic> and <italic>O</italic>. <italic>articulata</italic>, which was benefitical for enhancing their competitiveness. Nitrogen addition alleviated the nitrogen limitation in soil, leading to increased root length of <italic>A</italic>. <italic>philoxeroides</italic> but decreased root length of <italic>O</italic>. <italic>articulata</italic> in mixed cultures; however, <italic>O</italic>. <italic>articulata</italic> met the demand for nutrients and water by expanding its root area. Nitrogen addition significantly increased the total N content but decreased the C:N ratio of <italic>A</italic>. <italic>philoxeroides.</italic> Nitrogen addition significantly decreased Flav but increased Anth of <italic>O</italic>. <italic>articulata</italic> in mixed cultures. Nitrogen addition significantly decreased both F<sub>0</sub> and F<sub>m</sub> in mixed cultures, which relatively the increased photosynthetic efficiency of <italic>O</italic>. <italic>articulata</italic>. These results indicate that nitrogen addition significantly affects the nutrient absorption and competition patterns of <italic>A</italic>. <italic>philoxeroides</italic> vs. <italic>O</italic>. <italic>articulata</italic>, in high soil N environment, <italic>A</italic>. <italic>philoxeroides</italic> achieves higher nitrogen enrichment capacity by increasing its root length and rapid growth by reducing its C:N ratio, while <italic>O</italic>. <italic>articulata</italic> has higher biomass accumulation and root/shoot ratios, and nitrogen addition relatively increased its root area and photosynthetic fluorescence. Moreover, nitrogen addition also promoted the physiological plasticity in the Flav&#x2013;Anth trade-off for <italic>O</italic>. <italic>articulata</italic>. Therefore, under intensified global nitrogen deposition, the biotic resistance of <italic>O</italic>. <italic>articulata</italic> to <italic>A</italic>. <italic>philoxeroides</italic> invasion might be further enhanced.</p>
</sec>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>HW and BR: conceptualization. HW and SD: methodology and formal analysis. SD, LW, YZ, and SJ: investigation and data curation. HW and SD: writing&#x2014;original draft preparation and writing&#x2014;review and editing. HW and BR: funding acquisition. All authors contributed to the article and approved the submitted version.</p>
</sec>
</body>
<back>
<sec id="s8" sec-type="funding-information">
<title>Funding</title>
<p>This work was supported by the National Natural Science Foundation of China (31800460), the Xinyang Academy of Ecological Research Open Foundation (2023XYMS16), the Science and Technology Research Project of Henan Province (232102110062), and the Nanhu Scholars Program for Young Scholars of Xinyang Normal University (XYNU) (2023A017).</p>
</sec>
<sec id="s9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="s10" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
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