<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AJPS</journal-id><journal-title-group><journal-title>American Journal of Plant Sciences</journal-title></journal-title-group><issn pub-type="epub">2158-2742</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ajps.2021.127076</article-id><article-id pub-id-type="publisher-id">AJPS-110902</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  N/P/K Ratios and CO&lt;sub&gt;2&lt;/sub&gt; Concentration Change Nitrogen-Photosynthesis Relationships in Black Spruce
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Qing-Lai</surname><given-names>Dang</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Junlin</surname><given-names>Li</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Rongzhou</surname><given-names>Man</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Faculty of Natural Resources Management, Lakehead University, Thunder Bay, Canada</addr-line></aff><aff id="aff2"><addr-line>Ontario Ministry of Natural Resources, Ontario Forest Research Institute, Sault Ste. Marie, Ontario, Canada</addr-line></aff><pub-date pub-type="epub"><day>29</day><month>06</month><year>2021</year></pub-date><volume>12</volume><issue>07</issue><fpage>1090</fpage><lpage>1105</lpage><history><date date-type="received"><day>8,</day>	<month>June</month>	<year>2021</year></date><date date-type="rev-recd"><day>25,</day>	<month>July</month>	<year>2021</year>	</date><date date-type="accepted"><day>28,</day>	<month>July</month>	<year>2021</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  The relationship between photosynthesis and leaf nitrogen concentration is often used to model forest carbon fixation and ratios of different nutrient elements can modify this relationship. However, the effects of nutrient ratios on this important relationship are generally not well understood. To investigate whether N/P/K ratios and CO
  <sub>2</sub>
   concentration ([CO
  <sub>2</sub>
  ]) influence relationships between photosynthesis and nitrogen, we exposed one-year-old black spruce seedlings to two [CO
  <sub>2</sub>
  ] (370 and 720 μmol&amp;middot;mol
  <sup>-1</sup>
  ), two N/P/K ratio regimes (constant (CNR) and variable (VNR) nutrient ratio) at 6 N supply levels (10 to 360 μmol&amp;middot;mol
  <sup>-1</sup>
  ). It was found that photosynthesis (P
  <sub>n</sub>
  ) was more sensitive to nitrogen supply and N/P/K ratios under the elevated [CO
  <sub>2</sub>
  ] than under ambient [CO
  <sub>2</sub>
  ]; under the elevated [CO
  <sub>2</sub>
  ], P
  <sub>n</sub>
   declined with increases in N supplies above 150 μmol&amp;middot;mol
  <sup>-1</sup>
   in the CNR treatment but was relatively insensitive to N supplies of the same range in the VNR treatment. Further, our data suggest that the nutrient ratio and the CO
  <sub>2</sub>
   elevation effects on photosynthesis were via their effects on the maximum rate of carboxylation (V
  <sub>cmax</sub>
  ) but not electron transport (J
  <sub>max</sub>
  ) or triose phosphate utilization (TPU). The results suggest that the CO
  <sub>2</sub>
   elevation increased the demand for all three nutrient elements but the increase was greater for N than for P and K. The CO
  <sub>2</sub>
   elevation resulted in greater photosynthetic use efficiencies of N, P and K, but the increases varied with the nutrient ratio treatments. The results suggest that under elevated [CO
  <sub>2</sub>
  ], higher net photosynthetic rates demand different optimal N-P-K ratios than under the current [CO
  <sub>2</sub>
  ].
 
</p></abstract><kwd-group><kwd>Maximum Rate of Carboxylation</kwd><kwd> Photosynthetic Electron Transport</kwd><kwd> Triose Phosphate Utilization</kwd><kwd> Nutrient Use Efficiency</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The close relationship between photosynthesis and nitrogen in plants ( [<xref ref-type="bibr" rid="scirp.110902-ref1">1</xref>] - [<xref ref-type="bibr" rid="scirp.110902-ref8">8</xref>] is often used to predict photosynthesis and growth [<xref ref-type="bibr" rid="scirp.110902-ref9">9</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref13">13</xref>] as well as in ecosystem carbon flux models [<xref ref-type="bibr" rid="scirp.110902-ref9">9</xref>] - [<xref ref-type="bibr" rid="scirp.110902-ref14">14</xref>]. The relationship can explain much of the variation in plant performance even without considering the effects of other nutrient elements, such as phosphorus (P) and potassium (K) [<xref ref-type="bibr" rid="scirp.110902-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref16">16</xref>]. Plants are generally more sensitive to N than to other nutrient elements [<xref ref-type="bibr" rid="scirp.110902-ref17">17</xref>] because N is required in the greatest quantity and is more closely related to the amount and functioning of photosynthetic machines [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref19">19</xref>]. However, other elements can interact with N in affecting plant physiological processes and modify the N-photosynthesis relationship as well as affect N uptake [<xref ref-type="bibr" rid="scirp.110902-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>]. For instance, high N supply induces K deficiency [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>]; high N/K ratios reduce plant growth [<xref ref-type="bibr" rid="scirp.110902-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref23">23</xref>]; and high K supply negatively affects N and P uptake [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref24">24</xref>]. The N/P ratio influences the synthesis of photosynthetic enzymes and the shape of N-photosynthesis response curves [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref25">25</xref>]. The nature and consequence of interactions among different nutrient elements depend on the specific concentration of each element along the concentration ranges defined by the critical deficiency concentration (CDC) and the critical toxic concentration (CTC) [<xref ref-type="bibr" rid="scirp.110902-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>]. Too low a concentration will expose plants to the risk of growth suppression from CDC restraint while at too high concentration plants will face the risk of growth suppression from CTC [<xref ref-type="bibr" rid="scirp.110902-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref21">21</xref>]. Increasing nutrient supply between the CDC and CTC generally results in greater plant growth, but the pattern of the response varies with nutrient element [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref21">21</xref>]. For example, responses to P and K are generally steeper than to N, particularly in the lower portion of the range [<xref ref-type="bibr" rid="scirp.110902-ref3">3</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref26">26</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref27">27</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref28">28</xref>]. However, N-photosynthesis relationships are generally investigated with P and K concentrations maintained constant [<xref ref-type="bibr" rid="scirp.110902-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref32">32</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref33">33</xref>] with few exceptions where N/K and N/P ratios are kept constant [<xref ref-type="bibr" rid="scirp.110902-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref34">34</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref35">35</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref36">36</xref>].</p><p>Elevations in atmospheric CO<sub>2</sub> concentration can also modify the N-photosynthesis relationship [<xref ref-type="bibr" rid="scirp.110902-ref37">37</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref38">38</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref39">39</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref40">40</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref41">41</xref>]. Global climate change models predict that the atmospheric CO<sub>2</sub> concentration will double from the level of 2000 by the end of this century [<xref ref-type="bibr" rid="scirp.110902-ref42">42</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref43">43</xref>]. While CO<sub>2</sub> elevations generally stimulate photosynthesis and enhance its nitrogen use efficiency, the stimulation may not sustain in the long term [<xref ref-type="bibr" rid="scirp.110902-ref44">44</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref45">45</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref46">46</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref47">47</xref>] because of photosynthetic acclimation or down-regulation [<xref ref-type="bibr" rid="scirp.110902-ref48">48</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref49">49</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref50">50</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref51">51</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref52">52</xref>]. The degree of photosynthetic down-regulation is closely correlated to N supply [<xref ref-type="bibr" rid="scirp.110902-ref53">53</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref54">54</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref55">55</xref>]. Most studies suggest that photosynthetic down regulation is a result of nutrient limitation [<xref ref-type="bibr" rid="scirp.110902-ref51">51</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref56">56</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref57">57</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref58">58</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref59">59</xref>]. Consequently, CO<sub>2</sub> elevations may be less beneficial to trees growing on nutrient-poor sites [<xref ref-type="bibr" rid="scirp.110902-ref30">30</xref>]. Conversely, fertilization can increase CO<sub>2</sub> stimulation of photosynthesis and growth [<xref ref-type="bibr" rid="scirp.110902-ref49">49</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref56">56</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref58">58</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref59">59</xref>]. CO<sub>2</sub> elevations generally increase nutrient demand [<xref ref-type="bibr" rid="scirp.110902-ref60">60</xref>] and the increase is generally greater for N than for P and K [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref26">26</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref27">27</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref28">28</xref>] because plants require a greater amount of N than P and K [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref26">26</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref27">27</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref28">28</xref>]. Elevated [CO<sub>2</sub>] and increased N supply can have synergistic effects on photosynthesis and biomass production [<xref ref-type="bibr" rid="scirp.110902-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref39">39</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref50">50</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref61">61</xref>]. However, other nutrient elements can also interact with [CO<sub>2</sub>]. For example, a low P supply can suppress the CO<sub>2</sub> stimulation of photosynthesis in some species [<xref ref-type="bibr" rid="scirp.110902-ref25">25</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref62">62</xref>]. Therefore, a good understanding of how CO<sub>2</sub> elevation, nutrient supply and nutrient ratios affect the relationship between N supply and the photosynthesis and growth of plants is critical for an accurate and reliable prediction of plant growth trends under future climate conditions [<xref ref-type="bibr" rid="scirp.110902-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref63">63</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref64">64</xref>].</p><p>Black spruce grows on sites with a wide range of N levels [<xref ref-type="bibr" rid="scirp.110902-ref65">65</xref>]. However, its physiological responses to CO<sub>2</sub> elevation are generally examined under optimal nutrient regimes [<xref ref-type="bibr" rid="scirp.110902-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref66">66</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref67">67</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref68">68</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref69">69</xref>]. The objective of this study was to investigate how elevated CO<sub>2</sub>, nitrogen supply and their interactions with P, K and N/P/K ratios affect the relationship between N and photosynthesis in black spruce. Since the increases in nutrient demand induced by CO<sub>2</sub> elevations are proportionally greater for N than for P and K, and CTC is reached faster for P and K than for N under elevated CO<sub>2</sub> when N/P/K ratios are maintained constant, we hypothesize that N/P/K ratios and CO<sub>2</sub> will interactively affect the N-photosynthetic relationship.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Plant Materials</title><p>One-year-old black spruce seedlings (Piceamariana [Mill.] B.S.P.) were obtained from the Hill’s Greenhouses Ltd. in Murillo (west of Thunder Bay). The seedlings were relatively uniform in size at the beginning of the experiment (H = 22.8 &#177; 0.16 cm, RCD = 2.05 &#177; 0.02 cm). The seedlings were transplanted into containers of 13 cm height and 12 cm diameter with a mixture of peat moss and vermiculite (1:1; v/v).</p></sec><sec id="s2_2"><title>2.2. Experiment Design</title><p>There were two CO<sub>2</sub> treatments (AC 370, EC 720 μmol&#183;mol<sup>−1</sup>), two nutrient ratio treatments within each CO<sub>2</sub> treatment (constant N/P/K ratio (CNR) vs. variable N/P/K ratio (VNR)), and six levels of Nsupplywithin each nutrient ratio treatment (10, 80, 150, 220, 290 and 360 μmol N mol<sup>−</sup><sup>1</sup>solution). The CO<sub>2</sub> treatments were implemented in four greenhouses with identical dimensions and design (two replicates for each CO<sub>2</sub>) in the Forest Ecology Complex of Lakehead University Thunder Bay campus. In the CNR treatment, the N/P/K ratios were 5/2/5 in all 6 N treatments; in the VNR treatment, P and K concentrations were the same in all 6 N treatments (60 μmol&#183;mol<sup>−1</sup> P, 150 μmol&#183;mol<sup>−1</sup> K). There were 4 seedlings per treatment combination (2 &#215; 6 &#215; 4 = 48 seedlings in each greenhouse).</p><p>The day/night air temperatures in the greenhouses were controlled at 25˚C- 26˚C/16˚C-17˚C and the photoperiod at 16 hours in all the greenhouses. The natural light was supplemented using high-pressure sodium lamps on shorter days. All the experiment conditions (temperature, [CO<sub>2</sub>] and light) were monitored and controlled using a computerized Argus environment control system (Argus Control Systems Ltd, Vancouver, BC, Canada). Seedlings were watered as needed (generally every two days) to maintain the volumetric water content of the growing medium above 30%, as determined using an HH2 Moisture Meter and ML2X ThetaProbe (Delta-T Devices, Cambridge, U.K.). The experiment lasted 3.5 months.</p></sec><sec id="s2_3"><title>2.3. Gas Exchange Measurement</title><p>Photosynthetic responses to [CO<sub>2</sub>] were measured at 50, 150, 250, 370, 550, 720, 1000 and 1400 μmol&#183;mol<sup>−1</sup> [CO<sub>2</sub>] using a PP CIRAS open gas exchange system with a conifer leaf cuvette (PP System Inc. Amesbury, MA, USA). Other environment conditions in the leaf chamber were 25˚C air temperature, 800 μmol&#183;m<sup>−2</sup>&#183;s<sup>−1</sup> photosynthetically active radiation (saturated) and 50% RH. The measurements were taken on the current year foliage on the terminal shoot. All measurements were made between 0730-1130 h in situ. Following the measurement, the foliage used forthe gas exchange measurement was harvested and scanned for projected leaf area using WinSEEDLE (Regent Instruments Inc., QuebecCity, Canada) and subsequently dried at 75˚C for 48 hours for calculating specific leaf area and nutrient analyses. The A/Ci data were analysed using the Plantecophys package of R 4.0.2 to determine the maximum rate of Rubisco carboxylation (V<sub>cmax</sub>) and light saturated rate of photosynthetic electron transport (J<sub>max</sub>).</p><p>Leaf concentrations of nitrogen, Phosphorus and potassium were determined as described in [<xref ref-type="bibr" rid="scirp.110902-ref70">70</xref>]. Photosynthetic N-use efficiency (PNUE), P-use efficiency (PPUE) and K-use efficiency (PKUE) were calculated by dividing the net photosynthetic rate measured at the corresponding growth [CO<sub>2</sub>] by the corresponding nutrient concentration.</p></sec><sec id="s2_4"><title>2.4. Statistical Analysis</title><p>The data were examined graphically for the normality of distribution (probability plots for residuals) and homogeneity of variance (scatter plots). Since both assumptions for the Analysis of variance (ANOVA) were met, no data transformation was necessary. When ANOVA showed a significant effect (p ≤ 0.05) for N supply or an interaction, Fisher’s Least Significant Difference (LSD) post hoc test was conducted. The analyses were conducted using the R software package.</p></sec></sec><sec id="s3"><title>3. Results</title><sec id="s3_1"><title>3.1. Net Photosynthetic Rate (P<sub>n</sub>)</title><p>The response pattern of photosynthesis (P<sub>n</sub>) to N supply was affected by both [CO<sub>2</sub>] and nutrient ratio regime (significant 2- and 3-way interactions in <xref ref-type="table" rid="table1">Table 1</xref>). At the ambient [CO<sub>2</sub>], the general response patterns were similar in the two nutrient ratio regimes: P<sub>n</sub> increased with N increases from 10 to 150 μmol&#183;mol<sup>−1</sup> and then decreased with further increases in N supply (<xref ref-type="fig" rid="fig1">Figure 1</xref>). Under the elevated [CO<sub>2</sub>], however, the response patterns diverged between the two nutrient ratio regimes at N supplies above 150 μmol&#183;mol<sup>−1</sup>: P<sub>n</sub> in the CNR treatment decreased with further increases in N supply as in the ambient CO<sub>2</sub> treatment, but no such decreases occurred in the VNR treatment (<xref ref-type="fig" rid="fig1">Figure 1</xref>).</p></sec><sec id="s3_2"><title>3.2. Biochemical Parameters</title><p>Both [CO<sub>2</sub>] and nutrient ratio regime influenced the response of maximum rate of carboxylation (V<sub>cmax</sub>) to N supply but neither affected the response of light saturated rate of electron transport (J<sub>max</sub>) (<xref ref-type="table" rid="table1">Table 1</xref>). While V<sub>cmax</sub> increased with increasing N supply from 10 to 150 μmol&#183;mol<sup>−1</sup> in both [CO<sub>2</sub>] treatments, the response differed between the two CO<sub>2</sub> treatments at higher N levels: V<sub>cmax</sub> declined with further increases in N supply under the ambient [CO<sub>2</sub>] but it plateaued under the elevated [CO<sub>2</sub>] (<xref ref-type="fig" rid="fig2">Figure 2</xref>(a)). The response pattern of V<sub>cmax</sub> to N supply in the CNR nutrient ratio regime was similar to that in the ambient [CO<sub>2</sub>] treatment while the response in the VNR was similar to that under the elevated [CO<sub>2</sub>] (<xref ref-type="fig" rid="fig2">Figure 2</xref>(a) &amp; <xref ref-type="fig" rid="fig2">Figure 2</xref>(b)). J<sub>max</sub> generally increased with increasing N supply from 10 to 150 μmol&#183;mol<sup>−1</sup> and declined with further increases in N supply, but the difference between two adjacent N levels was not always statistically significant (<xref ref-type="fig" rid="fig2">Figure 2</xref>(c)). The CO<sub>2</sub> elevation significantly increased J<sub>max</sub><sub> </sub></p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> P values for the effects of CO<sub>2</sub> concentration (C), nutrient ratio (NR), nitrogen supply (N) and their interactions on physiological variables in black spruce seedlings</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Variable</th><th align="center" valign="middle"  colspan="7"  >Treatment effects</th></tr></thead><tr><td align="center" valign="middle" >C</td><td align="center" valign="middle" >NR</td><td align="center" valign="middle" >N</td><td align="center" valign="middle" >C &#215; NR</td><td align="center" valign="middle" >C &#215; N</td><td align="center" valign="middle" >NR &#215; N</td><td align="center" valign="middle" >C &#215; NR &#215; N</td></tr><tr><td align="center" valign="middle" >P<sub>n</sub></td><td align="center" valign="middle" >0.022</td><td align="center" valign="middle" >0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.003</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.013</td></tr><tr><td align="center" valign="middle" >V<sub>cmax</sub></td><td align="center" valign="middle" >0.021</td><td align="center" valign="middle" >0.084</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.132</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.027</td><td align="center" valign="middle" >0.566</td></tr><tr><td align="center" valign="middle" >J<sub>max</sub></td><td align="center" valign="middle" >0.050</td><td align="center" valign="middle" >0.626</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.513</td><td align="center" valign="middle" >0.109</td><td align="center" valign="middle" >0.383</td><td align="center" valign="middle" >0.357</td></tr><tr><td align="center" valign="middle" >TPU</td><td align="center" valign="middle" >0.039</td><td align="center" valign="middle" >0.886</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.930</td><td align="center" valign="middle" >0.103</td><td align="center" valign="middle" >0.341</td><td align="center" valign="middle" >0.293</td></tr><tr><td align="center" valign="middle" >g<sub>s</sub></td><td align="center" valign="middle" >0.100</td><td align="center" valign="middle" >0.274</td><td align="center" valign="middle" >0.314</td><td align="center" valign="middle" >0.746</td><td align="center" valign="middle" >0.250</td><td align="center" valign="middle" >0.229</td><td align="center" valign="middle" >0.427</td></tr><tr><td align="center" valign="middle" >NUE</td><td align="center" valign="middle" >0.024</td><td align="center" valign="middle" >0.299</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.028</td><td align="center" valign="middle" >0.476</td><td align="center" valign="middle" >0.159</td><td align="center" valign="middle" >0.324</td></tr><tr><td align="center" valign="middle" >PUE</td><td align="center" valign="middle" >0.052</td><td align="center" valign="middle" >0.364</td><td align="center" valign="middle" >0.012</td><td align="center" valign="middle" >0.012</td><td align="center" valign="middle" >0.103</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.003</td></tr><tr><td align="center" valign="middle" >KUE</td><td align="center" valign="middle" >0.014</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td></tr></tbody></table></table-wrap><p>Notes: P<sub>n</sub> = net photosynthetic rate, V<sub>cmax</sub> = maximum rate of carboxylation, J<sub>max</sub> = light saturated rate of electron transport, g<sub>s</sub> = stomatal conductance, NUE = photosynthetic nitrogen-use efficiency, PUE = phosphorus-use efficiency, KUE = potassium-use efficiency, N<sub>a</sub>, P<sub>a</sub> and K<sub>a</sub> are leaf area based foliar N, P and K concentrations. 1-year old seedlings were grown under two [CO<sub>2</sub>] (ambient [CO<sub>2</sub>] = 370 μmol&#183;mol<sup>−</sup><sup>1</sup>, elevated [CO<sub>2</sub>] = 720 μmol&#183;mol<sup>−</sup><sup>1</sup>), 6 N concentrations (10, 80, 150, 220, 290 and 360 μmol&#183;mol<sup>−</sup><sup>1</sup>), and two nutrient ratio regimes (CNR—constant N/P/K ratios at 5/2/5 and VNR where the concentration was 60 μmol&#183;mol<sup>−</sup><sup>1</sup> for P and 150 μmol&#183;mol<sup>−</sup><sup>1</sup> K at allsix N concentrations) for 3.5 months. Significant effects (p ≤ 0.05) were bold-faced.</p><p>(from 72.8 to 101.5 μmol CO<sub>2</sub> m<sup>−2</sup> s<sup>−1</sup>). However, neither nutrient ratio regime nor [CO<sub>2</sub>] had a significant effect on the response of J<sub>max</sub> to N supply (<xref ref-type="table" rid="table1">Table 1</xref>).</p></sec><sec id="s3_3"><title>3.3. Foliar Nutrient Use Efficiency</title><p>The CO<sub>2</sub> elevation significantly increased photosynthetic nitrogen-use efficiency (PNUE) and the increase was greater in the VNR than CNR treatment (<xref ref-type="table" rid="table1">Table 1</xref>, <xref ref-type="fig" rid="fig3">Figure 3</xref>(a)). Nutrient ratio regime had opposite effects on PNUE under different CO<sub>2</sub> treatments: under the ambient [CO<sub>2</sub>], PNUE was significantly lower in the VNR than in CNR; under the elevated [CO<sub>2</sub>], however, PNUE was significantly greater in the VNR than CNR (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="fig" rid="fig3">Figure 3</xref>(a)). PNUE generally decreased with the increasing N supply (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="fig" rid="fig3">Figure 3</xref>(b)).</p><p>The photosynthetic phosphorus-use efficiency (PPUE) was affected by both nutrient ratio and [CO<sub>2</sub>] (<xref ref-type="table" rid="table1">Table 1</xref>): under the elevated [CO<sub>2</sub>] and VNR, PPUE increased with increasing N supply from 10 to 80 μmol&#183;mol<sup>−1</sup> and then became relatively stable with further increases in N supply; under the elevated [CO<sub>2</sub>] and CNR, there was not much change in PPUE as N supply increased from 10 to 150 μmol mol<sup>−1</sup> N but it decreased with further increases in N supply; there was generally very little variation in PPUE under the ambient [CO<sub>2</sub>] either with nutrient ratio or N supply (<xref ref-type="fig" rid="fig3">Figure 3</xref>(c)).</p><p>The responses of photosynthetic potassium-use efficiency (PKUE) to [CO<sub>2</sub>], nutrient ratio and N supply were similar to those of PPUE with the exception that PKUE increased with increasing N up to 150 μmol mol<sup>−1</sup> under the elevated [CO<sub>2</sub>] and VNR as compared to 80 μmol mol<sup>−1</sup> N for PPUE (<xref ref-type="table" rid="table1">Table 1</xref>, <xref ref-type="fig" rid="fig3">Figure 3</xref>(c) and <xref ref-type="fig" rid="fig3">Figure 3</xref>(d)).</p></sec></sec><sec id="s4"><title>4. Discussions</title><p>The results of this study support the hypotheses that constant N/P/K ratios (CNR) would lead to reductions in photosynthetic rate at high N supplies (&gt;150 μmol mol<sup>−1</sup> N) under elevated [CO<sub>2</sub>] and that CO<sub>2</sub> elevations would modify nitrogen-photosynthesis relationships. The fact that photosynthesis in the variable N/P/K ratios (VNR) (or constant P &amp; K concentrations) did not show any sign of declines at higher N supply levels under the elevated CO<sub>2</sub> suggests that the decline in photosynthesis in the CNR treatment was attributed to toxic levels of P or K or both. Further, under the ambient [CO<sub>2</sub>], photosynthesis at high N (&gt;150 μmol mol<sup>−1</sup> N) declined in both CNR and VNR, suggesting that the decline in photosynthesis under the ambient CO<sub>2</sub> was probably attributed to nitrogen toxicity. The above results also suggest that the CO<sub>2</sub> elevation increased the demand for nitrogen to greater extents than for phosphorus and potassium. However, the CO<sub>2</sub> elevation modified the nitrogen-photosynthesis relationship only in the VNR treatment. Thus, it can be concluded that the highest nitrogen supply used in this study was not toxic to black spruce under the elevated CO<sub>2</sub> and that the phosphorus and/or potassium levels in the CNR were too high at nitrogen supplies greater than 150 μmol mol<sup>−1</sup> while those in the VNR was too low to maximize photosynthesis. This study suggests that neither P and K concentrations nor N/P/K ratios should be kept constant at the current optimums when increasing fertilization are used to increase plant productivity in the future. Instead the concentration combination of the three key nutrient elements should be considered as a single integrated factor. Further research is warranted to determine optimal combinations of these elements under the future doubled CO<sub>2</sub> environment. The results of this study are consistent with the concepts of critical deficiency concentration and critical toxic concentration as used by some other researchers [<xref ref-type="bibr" rid="scirp.110902-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref28">28</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref29">29</xref>]. Our data suggest that the nutrient ratios and the CO<sub>2 </sub>elevation affected photosynthesis via their effects on V<sub>cmax</sub> but not J<sub>max</sub>. These results are in agreement with the findings of [<xref ref-type="bibr" rid="scirp.110902-ref14">14</xref>], but contradicted the results of [<xref ref-type="bibr" rid="scirp.110902-ref71">71</xref>].<sub> </sub>The effects probably reflected specific performance of black spruce seedlings growing in our wide range of N supplies and various nutrient ratios.</p><p>The nutrient ratios modified the responses of photosynthetic use-efficiency of N, P and K (PNUE, PPUE and PKUE, respectively) to [CO<sub>2</sub>] and N supply. The CNR treatment suppressed PNUE under the elevated [CO<sub>2</sub>]. PPUE and PKUE, however, were suppressed by the CNR only at higher N supplies under elevated [CO<sub>2</sub>]. As discussed previously on the suppressions of CDC and CTC, the decreases in PPUE and PKUE were probably attributable to the CTC effect of K. The PKUE under the elevated [CO<sub>2</sub>] increased with increases of N supply in the VNR treatment (K availability remained equal across all N supply levels), indicating the enhanced effect of increasing N supply on PKUE; the reversed trend occurred to the PKUE in the CNR treatment (K supply increased with increases of N supply), indicating the high K availability decreased the PKUE, and this high K availability caused the seedlings passively absorbing K, which led [K] passing over the level of CTC of K. In addition, the CO<sub>2</sub> elevation in this study generally resulted in greater PNUE, PPUE and PKUE. The enhancing effect of CO<sub>2</sub> elevation on PNUE agreed with the findings of [<xref ref-type="bibr" rid="scirp.110902-ref72">72</xref>], and the negative relationship between PNUE and leaf [N] was consistent with the results of [<xref ref-type="bibr" rid="scirp.110902-ref35">35</xref>]. The changes of the PNUE provided evidence that the relationship between photosynthesis and nitrogen was modified by nutrient ratios.</p><p>The nutrient ratios changed the relationship between photosynthesis and leaf [N] in this study. [<xref ref-type="bibr" rid="scirp.110902-ref73">73</xref>] has pointed out that the effects of elevated [CO<sub>2</sub>] on V<sub>cmax</sub> are largely through the changes in leaf [N] [<xref ref-type="bibr" rid="scirp.110902-ref73">73</xref>]. The results in this study indicated that the relationship between V<sub>cmax</sub> and leaf [N] was also affected by N/P/K ratios. The high leaf N concentration at the high N supply levels resulted in greater V<sub>cmax</sub> with the VNR treatment, but not in the CNR treatment. The effect was probably due to the toxic effects of K. Elevated [CO<sub>2</sub>] decreases leaf [N] [<xref ref-type="bibr" rid="scirp.110902-ref49">49</xref>] [<xref ref-type="bibr" rid="scirp.110902-ref74">74</xref>] and reduces net photosynthetic rates measured at a common [CO<sub>2</sub>]. Cao et al. ( [<xref ref-type="bibr" rid="scirp.110902-ref3">3</xref>] ) reported that the magnitude of photosynthetic acclimation in white birch (Betulapapyrifera Marsh.) in response to CO<sub>2</sub> elevation decreases with greater leaf N concentrations. Zhang and Dang [<xref ref-type="bibr" rid="scirp.110902-ref70">70</xref>] found that no photosynthetic down-regulation occurs in white birch seedlings in response to CO<sub>2</sub> elevation at various levels of N supply when N/P/K ratios are maintained constant. However, in this current study, the N<sub>a</sub> increased with the increasing N supply, but this ascending trend of leaf [N] did not show consistent corresponding increases of net photosynthetic rate at the high N supply levels under the elevated [CO<sub>2</sub>], rather the trend was modified by the nutrient ratios, that the CNR decreased P<sub>n</sub> and the VNR increased it. [<xref ref-type="bibr" rid="scirp.110902-ref3">3</xref>] reports that CO<sub>2</sub> elevation increases P<sub>n</sub> with no significant effect on N<sub>a</sub>. The changes in leaf [K] due to the effect of nutrient ratio treatments also showed a positive effect on P<sub>n</sub>, indicating that photosynthetic responses were not only correlated to leaf [N], but also to leaf [K], supporting the conclusion of [<xref ref-type="bibr" rid="scirp.110902-ref3">3</xref>] that the relationship between photosynthesis and leaf [N] is influenced by nutrient ratio.</p></sec><sec id="s5"><title>Acknowledgements</title><p>We thank Dr. Chander Shahi for advice on statistics, Joan Lee for greenhouse support, Derek Lawrence, Elisabeth Fraser and Tim Sobey for leaf NPK analysis. This study was supported by NSERC Discovery grants to Q.L. Dang (203198-2008) and Lakehead University Graduate Assistantship to J.L. Li.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Dang, Q.-L., Li, J.L. and Man, R.Z. (2021) N/P/K Ratios and CO<sub>2</sub> Concentration Change Nitrogen-Photosynthesis Relationships in Black Spruce. American Journal of Plant Sciences, 12, 1090-1105. https://doi.org/10.4236/ajps.2021.127076</p></sec></body><back><ref-list><title>References</title><ref id="scirp.110902-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Bowman, W.D. and Conant, R.T. (1994) Shoot Growth Dynamics and Photosynthetic Response to Increased Nitrogen Availability in the Alpine Willow Salix glauca. Oecologia, 97, 93-99. https://doi.org/10.1007/BF00317912</mixed-citation></ref><ref id="scirp.110902-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Brady, N.C. and Weil, R.R. (2002) The Nature and Properties of Soils. Pearson Education, Upper Saddle River, 960 p.</mixed-citation></ref><ref id="scirp.110902-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Cao, B., Dang, Q.-L. and Zhang, S. (2007) Relationship between Photosynthesis and Leaf Nitrogen Concentration under Ambient and Elevated [CO&lt;SUB&gt;2&lt;/SUB&gt;] in White Birch (Betula papyrifera) Seedlings. Tree Physiology, 27, 891-899. 
https://doi.org/10.1093/treephys/27.6.891</mixed-citation></ref><ref id="scirp.110902-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Crous, K.Y., Walters, M.B. and Ellsworth, D.S. (2008) Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Concentration Affects Leaf Photosynthesis-Nitrogen Relationships in Pinustaeda over Nine Years in FACE. Tree Physiology, 28, 607-614. https://doi.org/10.1093/treephys/28.4.607</mixed-citation></ref><ref id="scirp.110902-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Ellsworth, D.S., Reich, P.B., Naumburg, E.S., Koch, G.W., Kubiske, M.E. and Smith, S.D. (2004) Relationship between Photosynthesis and Leaf Nitrogen Concentration under Ambient and Elevated [CO&lt;SUB&gt;2&lt;/SUB&gt;] in White Birch (Betula papyrifera) Seedlings. Global Change Biology, 10, 2121-2138.  
https://doi.org/10.1111/j.1365-2486.2004.00867.x</mixed-citation></ref><ref id="scirp.110902-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Garnier, E., Salager, J.L., Laurent, G. and Sonie, L. (1999) Relationships between Photosynthesis, Nitrogen and Leaf Structure in 14 Grass Species and Their Dependence on the Basis of Expression. New Phytologist, 143, 119-129. 
https://doi.org/10.1046/j.1469-8137.1999.00426.x</mixed-citation></ref><ref id="scirp.110902-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Peterson, A.G., Field, C.B., Ball, J.T., Amthor, J.S., Drake, B., Emanuel, W.R., Johnson, D.W., Hanson, P.J., Luo, Y., McMurtrie, R.E., Norby, R.J., Oechel, W.C., Clenton, E.O., Parton, W.J., Pierce, L.L., Rastetter, E.B., Ruimy, A., Running, S.W. and Zak, D.R. (1999) Reconciling the Apparent Difference between Mass- and Area-Based Expressions of the Photosynthesis-Nitrogen Relationship. Oecologia, 118, 144-150.  
https://doi.org/10.1007/s004420050712</mixed-citation></ref><ref id="scirp.110902-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Peterson, A.G., Ball, J.T., Luo, Y., Field, C.B., Reich, P.B., Curtis, P.S., Griffin, K.L., Gunderson, C.A., Norby, R.J., Tissue, D.T., Forstreuter, M., Rey, A., Vogel, C.S., Participants, C. (1999) The Photosynthesis Leaf Nitrogen Relationship at Ambient and Elevated Atmospheric Carbon Dioxide: A Meta-Analysis. Global Change Biology, 5, 331-346. https://doi.org/10.1046/j.1365-2486.1999.00234.x</mixed-citation></ref><ref id="scirp.110902-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Dewar, R.C. and McMurtrie, R.E. (1996) Analytical Model of Stemwood Growth in Relation to Nitrogen Supply. Tree Physiology, 16, 161-171.  
https://doi.org/10.1093/treephys/16.1-2.161</mixed-citation></ref><ref id="scirp.110902-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Hirose, T. (1988) Modeling the Relative Growth-Rate as a Function of Plant Nitrogen Concentration. Physiologia Plantarum, 72, 185-189. 
https://doi.org/10.1111/j.1399-3054.1988.tb06641.x</mixed-citation></ref><ref id="scirp.110902-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">McMurtrie, R.E. (1991) Relationship of Forest Productivity to Nutrient and Carbon Supply—A Modeling Analysis. Tree Physiology, 9, 87-99. 
https://doi.org/10.1093/treephys/9.1-2.87</mixed-citation></ref><ref id="scirp.110902-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">McMurtrie, R.E., Norby, R.J., Medlyn, B.E., Dewar, R.C., Pepper, D.A., Reich, P.B. and Barton, C.V.M. (2008) Why Is Plant-Growth Response to Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Amplified When Water Is Limiting, but Reduced When Nitrogen Is Limiting? A Growth-Optimisation Hypothesis. Functional Plant Biology, 35, 521-534.  
https://doi.org/10.1071/FP08128</mixed-citation></ref><ref id="scirp.110902-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Verkroost, A.W.M. and Wassen, M.J. (2005) A Simple Model for Nitrogen-Limited Plant Growth and Nitrogen Allocation. Annals of Botany, 96, 871-876. 
https://doi.org/10.1093/aob/mci239</mixed-citation></ref><ref id="scirp.110902-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Springer, C.J., Delucia, E.H. and Thomas, R.B. (2005) Relationships between Net Photosynthesis and Foliar Nitrogen Concentrations in Loblolly Pine Forest Ecosystem Grown in Elevated Atmospheric Carbon Dioxide. Tree Physiology, 25, 385-394. 
https://doi.org/10.1093/treephys/25.4.385</mixed-citation></ref><ref id="scirp.110902-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Kellomaki, S. and Wang, K.Y. (1997) Effects of Long-Term CO&lt;SUB&gt;2&lt;/SUB&gt; and Temperature Elevation on Crown Nitrigen Distribution and Daily Photosynthetic Performace of Scots Pine. Forest Ecology and Management, 99, 309-326. 
https://doi.org/10.1016/S0378-1127(97)00059-5</mixed-citation></ref><ref id="scirp.110902-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Murthy, R., Dougherty, P.M., Zarnoch, S.J. and Allen, H.L. (1996) Effects of Carbon Dioxide, Fertilization, and Irrigation on Photosynthetic Capacity of Loblolly Pine Trees. Tree Physiology, 16, 537-546. https://doi.org/10.1093/treephys/16.6.537</mixed-citation></ref><ref id="scirp.110902-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Saidana, D., Braham, M., Boujnah, D., Mariem, F.B., Ammari, S. and El Hadj, S.B. (2009) Nutrient Stress, Ecophysiological, and Metabolic Aspects of Olive Tree Cultivars. Journal of Plant Nutrition, 32, 129-145.  
https://doi.org/10.1080/01904160802608999</mixed-citation></ref><ref id="scirp.110902-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Marschner, H. (1995) Mineral Nutrition of Higher Plants. San Academic Press, Diego, 889 p.</mixed-citation></ref><ref id="scirp.110902-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Nicodemus, M.A., Salifu, F.K. and Jacobs, D.F. (2008) Growth, Nutrition, and Photosynthetic Response of Black Walnut to Varying Nitrogen Sources and Rates. Journal of Plant Nutrition, 31, 1917-1936.  
https://doi.org/10.1080/01904160802402856</mixed-citation></ref><ref id="scirp.110902-ref20"><label>20</label><mixed-citation publication-type="book" xlink:type="simple">Chapin III, F.S. (1991) Effects of Multiple Environmental Stresses on Nutrient Availability and Use. In: Mooney, H.A., Wiiner, W.E. and Pell, E.J., Eds., Response of Plants to Multiple Stresses, Academic Press, San Diego, 67-88.  
https://doi.org/10.1016/B978-0-08-092483-0.50008-6</mixed-citation></ref><ref id="scirp.110902-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">Timmer, V.R., et al. (1991) Steady-State Nutrient Preconditioning and Early Outplanting Performance of Containerized Black Spruce Seedlings. Canadian Journal of Forest Research, 21, 585-594. https://doi.org/10.1139/x91-080</mixed-citation></ref><ref id="scirp.110902-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">van den Driessche, R. and Ponsford, D. (1995) Nitrogen Induced Potassium Deficiency in White Spruce (Picea glauca) and Engelmann Spruce (Piceaengelmannii) Seedlings. Canadian Journal of Forest Research, 25, 1445-1454. 
https://doi.org/10.1139/x95-157</mixed-citation></ref><ref id="scirp.110902-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Barbosa, J.G., Kampf, A.N., Martinez, H.E.P., Koller, O.C. and Bohnen, H. (2000) Chrysanthemum Cultivation in Expanded Clay. I. Effect of the Nitrogen-Phosphorus-Potassium Ratio in the Nutrient Solution. Journal of Plant Nutrition, 23, 1327-1336. https://doi.org/10.1080/01904160009382103</mixed-citation></ref><ref id="scirp.110902-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">Egilla, J.N. and Davies, F.T. (1995) Response of Hibiscus-rosa-sinensis L. to Varying Levels of Potassium Fertilization—Growth, Gas-Exchange and Mineral Element Concentration. Journal of Plant Nutrition, 18, 1765-1783. 
https://doi.org/10.1080/01904169509365022</mixed-citation></ref><ref id="scirp.110902-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Campbell, C.D. and Sage, R.F. (2006) Interactions between the Effects of Atmospheric CO&lt;SUB&gt;2&lt;/SUB&gt; Content and P Nutrition on Photosynthesis in White Lupin (Lupinus albus L.). Plant, Cell and Environment, 29, 844-853. 
https://doi.org/10.1111/j.1365-3040.2005.01464.x</mixed-citation></ref><ref id="scirp.110902-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Epstein, E. (1972) Mineral Nutrition of Plants: Principles and Perspectives. John Wiley and Sons, Inc., New York, 412 p.</mixed-citation></ref><ref id="scirp.110902-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">Epstein, E. and Bloom, A.J. (2005) Mineral Nutrition of Plants: Principles and Perspectives. Sinauer Associates, Sunderland, 400 p.</mixed-citation></ref><ref id="scirp.110902-ref28"><label>28</label><mixed-citation publication-type="other" xlink:type="simple">Timmer, V.R. (1991) Interpretation of Seedling Analysis and Visual Symptoms. In: van den Driessche R, Editors. Mineral Nutrition of Conifer Seedlings. CRC Press, Boca Raton, 113-134.</mixed-citation></ref><ref id="scirp.110902-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Ingestad, T. (1979) Mineral Nitrient Requirements of Pinus silvestris and Piceaabies Seedlings. Physiol Plant, 45, 373-380.  
https://doi.org/10.1111/j.1399-3054.1979.tb02599.x</mixed-citation></ref><ref id="scirp.110902-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">Brown, K. and Higginbotham, K.O. (1986) Effects of Carbon Dioxide Enrichment and Nitrogen Supply on Growth of Boreal Tree Seedlings. Tree Physiology, 2, 223-232. https://doi.org/10.1093/treephys/2.1-2-3.223</mixed-citation></ref><ref id="scirp.110902-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Griffin, K.L., Thomas, R.B. and Strain, B.R. (1993) Effects of Nitrogen Supply and Elevated Carbon Dioxide on Construction Cost in Leaves of Pinus taeda (L) Seedlings. Oecologia, 95, 575-580. https://doi.org/10.1007/BF00317443</mixed-citation></ref><ref id="scirp.110902-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">Gavito, M.E., Curtis, P.S., Mikkelsen, T.N. and Jakobsen, I. (2001) Interactive Effects of Soil Temperature, Atmospheric Carbon Dioxide and Soil N on Root Development, Biomass and Nutrient Uptake of Winter Wheat during Vegetative Growth. Journal of Experimental Botany, 52, 1913-1923.  
https://doi.org/10.1093/jexbot/52.362.1913</mixed-citation></ref><ref id="scirp.110902-ref33"><label>33</label><mixed-citation publication-type="other" xlink:type="simple">Cao, B., Dang, Q.L., Yu, X. and Zhang, S. (2008) Effects of [CO&lt;SUB&gt;2&lt;/SUB&gt;] and Nitrogen on Morphological and Biomass Traits of White Birch (Betula papyrifera) Seedlings. Forest Ecology and Management, 254, 217-224.  
https://doi.org/10.1016/j.foreco.2007.08.002</mixed-citation></ref><ref id="scirp.110902-ref34"><label>34</label><mixed-citation publication-type="other" xlink:type="simple">Ambebe, T.F., Dang, Q.L. and Li, J. (2010) Low Soil Temperature Inhibits the Effect of High Nutrient Supply on Photosynthetic Response to Elevated Carbon Dioxide Concentration in White Birch Seedlings. Tree Physiology, 30, 234-243. 
https://doi.org/10.1093/treephys/tpp109</mixed-citation></ref><ref id="scirp.110902-ref35"><label>35</label><mixed-citation publication-type="other" xlink:type="simple">Ripullone, F.G.G.M. and La, J.B. (2003) Photosynthesis-Nitrogen Relationships: Interpretation of Different Patterns between Pseudotruga menziesii and Populus x euroamericana in a Mini-Stand Experiment. Tree Physiology, 23, 137-144. 
https://doi.org/10.1093/treephys/23.2.137</mixed-citation></ref><ref id="scirp.110902-ref36"><label>36</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, S. and Dang, Q.L. (2006) Effects of Carbon Dioxide Concentration and Nutrition on Photosynthetic Functions of White Birch Seedlings. Tree Physiology, 26, 1457-1467. https://doi.org/10.1093/treephys/26.11.1457</mixed-citation></ref><ref id="scirp.110902-ref37"><label>37</label><mixed-citation publication-type="other" xlink:type="simple">Ainsworth, E.A. and Rogers, A. (2007) The Response of Photosynthesis and Stomatal Conductance to Rising [CO&lt;SUB&gt;2&lt;/SUB&gt;]: Mechanisms and Environmental Interactions. Plant Cell Environ, 30, 258-270. https://doi.org/10.1111/j.1365-3040.2007.01641.x</mixed-citation></ref><ref id="scirp.110902-ref38"><label>38</label><mixed-citation publication-type="other" xlink:type="simple">Long, S.P., Elizabith, A.A., Rogers, A. and Ort, D.R. (2004) Rising Atmospheric Carbon Dioxide: Plants FACE the Future. Annual Review of Plant Biology, 55, 591-628. https://doi.org/10.1146/annurev.arplant.55.031903.141610</mixed-citation></ref><ref id="scirp.110902-ref39"><label>39</label><mixed-citation publication-type="other" xlink:type="simple">Nowak, R.S., Ellsworth, D.S. and Smith, S.D. (2004) Functional Responses of Plants to Elevated Atmospheric CO&lt;SUB&gt;2&lt;/SUB&gt;—Do Photosynthetic and Productivity Data from FACE Experiments Support Early Predictions? New Phytologist Foundation, 162, 253-280. https://doi.org/10.1111/j.1469-8137.2004.01033.x</mixed-citation></ref><ref id="scirp.110902-ref40"><label>40</label><mixed-citation publication-type="other" xlink:type="simple">Roberntz, P. and Stockfors, J. (1998) Effects of Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Concentration and Nutriention on Net Photosynthesis, Stomatal Conductance and Needle Respiration of Field-Grown Norway Spruce Trees. Tree Physiology, 18, 233-241. 
https://doi.org/10.1093/treephys/18.4.233</mixed-citation></ref><ref id="scirp.110902-ref41"><label>41</label><mixed-citation publication-type="other" xlink:type="simple">Tognetti, R. and Johnson, J.D. (1999) The Effect of Elevated Atmospheric CO&lt;SUB&gt;2&lt;/SUB&gt; Concentration and Nutrient Supply on Gas Exchange, Carbohydrates and Foliar Phenolic Concentration in Live Oak (Quercus virginiana Mill.) Seedlings. Annals of Forest Science, 56, 379-389. https://doi.org/10.1051/forest:19990503</mixed-citation></ref><ref id="scirp.110902-ref42"><label>42</label><mixed-citation publication-type="other" xlink:type="simple">Bigras, F.J. and Bertrand, A. (2006) Responses of Piceamariana to Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Concentration during Growth, Cold Hardening and Dehardening: Phenology, Cold Tolerance, Photosynthesis and Growth. Tree Physiology, 26, 875-888. 
https://doi.org/10.1093/treephys/26.7.875</mixed-citation></ref><ref id="scirp.110902-ref43"><label>43</label><mixed-citation publication-type="other" xlink:type="simple">IPCC (2007) Climate change 2007: The Physical Science Basis. Cambridge University Press, Cambridge, 996 p.</mixed-citation></ref><ref id="scirp.110902-ref44"><label>44</label><mixed-citation publication-type="other" xlink:type="simple">Norby, R.J. and Iversen, C.M. (2006) Nitrogen Uptake, Distribution, Turnover, and Efficiency of Use in a CO&lt;SUB&gt;2&lt;/SUB&gt;-Enriched Sweetgum Forest. Ecology, 87, 5-14. 
https://doi.org/10.1890/04-1950</mixed-citation></ref><ref id="scirp.110902-ref45"><label>45</label><mixed-citation publication-type="other" xlink:type="simple">Norby, R.J., Warren, J.M., Iversen, C.M., Medlyn, B.E. and McMurtrie, R.E. (2010) CO&lt;SUB&gt;2&lt;/SUB&gt; Enhancement of Forest Productivity Constrained by Limited Nitrogen Availability. Nature Precedings. https://doi.org/10.1038/npre.2009.3747.1</mixed-citation></ref><ref id="scirp.110902-ref46"><label>46</label><mixed-citation publication-type="other" xlink:type="simple">Poorter, H. (1998) Do Slow-Growing Species and Nutrient-Stressed Plants Respond Relatively Strongly to Elevated CO&lt;SUB&gt;2&lt;/SUB&gt;? Global Change Biology, 4, 693-697.  
https://doi.org/10.1046/j.1365-2486.1998.00177.x</mixed-citation></ref><ref id="scirp.110902-ref47"><label>47</label><mixed-citation publication-type="other" xlink:type="simple">Rogers, A. and Ellsworth, D.S. (2002) Photosynthetic Acclimation of Pinus taeda (loblolly pine) to Long-Term Growth in Elevated pCO&lt;SUB&gt;2&lt;/SUB&gt; (FACE). Plant, Cell and Environment, 25, 851-858. https://doi.org/10.1046/j.1365-3040.2002.00868.x</mixed-citation></ref><ref id="scirp.110902-ref48"><label>48</label><mixed-citation publication-type="other" xlink:type="simple">Davey, P.A., Olcer, H., Zakhleniuk, O., Bernacchi, C.J., Calfapietra, C., Long, S.P. and Raines, C.A. (2006) Can Fast-Growing Plantation Trees Escape Biochemical Down-Regulation of Photosynthesis When Grown throughout Their Complete Production Cycle in the Open Air under Elevated Carbon Dioxide? Plant, Cell and Environment, 29, 1235-1244. https://doi.org/10.1111/j.1365-3040.2006.01503.x</mixed-citation></ref><ref id="scirp.110902-ref49"><label>49</label><mixed-citation publication-type="other" xlink:type="simple">Lewis, J.D., Lucash, M., Olszyk, D.M. and Tingey, D.T. (2004) Relationships between Needle Nitrogen Concentration and Photosynthetic Responses of Douglas-Fir Seedlings to Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; and Temperature. New Phytologist, 162, 355-364. 
https://doi.org/10.1111/j.1469-8137.2004.01036.x</mixed-citation></ref><ref id="scirp.110902-ref50"><label>50</label><mixed-citation publication-type="other" xlink:type="simple">Johnsen, K.H. (1993) Growth and Ecophysiological Responses of Black Spruce Seedlings to Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; under Varied Water and Nutrient Additions. Canadian Journal of Forest Research, 23, 1033-1042. https://doi.org/10.1139/x93-132</mixed-citation></ref><ref id="scirp.110902-ref51"><label>51</label><mixed-citation publication-type="other" xlink:type="simple">Gunderson, C.A. and Wullschleger, S.D. (1994) Photosynthetic Acclimation in Trees to Rising Atmospheric CO&lt;SUB&gt;2&lt;/SUB&gt;: A Broader Perspective. Photosynthesis Research, 39, 369-388. https://doi.org/10.1007/BF00014592</mixed-citation></ref><ref id="scirp.110902-ref52"><label>52</label><mixed-citation publication-type="other" xlink:type="simple">Kitaoa, M., Koike, T., Tobita, H. and Maruyama, Y. (2005) Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; and Limited Nitrogen Nutrition Can Restrict Excitation Energy Dissipation in Photosystem II of Japanese White Birch (Betula platyphylla var. japonica) Leaves. Physiologia Plantarum, 125, 64-73. https://doi.org/10.1111/j.1399-3054.2005.00540.x</mixed-citation></ref><ref id="scirp.110902-ref53"><label>53</label><mixed-citation publication-type="other" xlink:type="simple">Isopp, H., Frehner, M., Long, S.P. and Nosberger, J. (2000) Sucrose-Phosphate Synthase Responds Differently to Source-Sink Relations and to Photosynthetic Rates: Lolium perenne L. Growing at Elevated pCO&lt;SUB&gt;2&lt;/SUB&gt; in the Field. Plant, Cell and Environment, 23, 597-607. https://doi.org/10.1046/j.1365-3040.2000.00583.x</mixed-citation></ref><ref id="scirp.110902-ref54"><label>54</label><mixed-citation publication-type="other" xlink:type="simple">Stitt, M. and Krapp, A. (1999) The Interaction between Elevated Carbon Dioxide and nitrogen Nutrition: The Physiological and Molecular Background. Plant, Cell and Environment, 22, 583-621. https://doi.org/10.1046/j.1365-3040.1999.00386.x</mixed-citation></ref><ref id="scirp.110902-ref55"><label>55</label><mixed-citation publication-type="other" xlink:type="simple">Oren, R., Ellsworth, D.S., Johnsen, K.H., Phillips, N., Ewers, B.E., Maier, C., Schafer, K.V.R., McCarthy, H., Hendrey, G., McNulty, S.G. and Katul, G.G. (2001) Soil Fertility Limits Carbon Sequestration by Forest Ecosystems in a CO&lt;SUB&gt;2&lt;/SUB&gt;-Enriched Atmosphere. Nature, 411, 469-472. https://doi.org/10.1038/35078064</mixed-citation></ref><ref id="scirp.110902-ref56"><label>56</label><mixed-citation publication-type="other" xlink:type="simple">Saxe, H., Ellsworth, D.S. and Heath, J. (1998) Tree and Forest Functioning in an Enriched CO&lt;SUB&gt;2&lt;/SUB&gt; Atmosphere, Tansley Review No. 98. New Phytologist, 139, 395-436. 
https://doi.org/10.1046/j.1469-8137.1998.00221.x</mixed-citation></ref><ref id="scirp.110902-ref57"><label>57</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, S., Dang, Q.L. and Yu, X. (2006) Nutrient and [CO&lt;SUB&gt;2&lt;/SUB&gt;] Elevation Had Synergistic Effects on Biomass Production but not on Biomass Allocation of White Birch Seedlings. Forest Ecology and Management, 234, 238-244. 
https://doi.org/10.1016/j.foreco.2006.07.017</mixed-citation></ref><ref id="scirp.110902-ref58"><label>58</label><mixed-citation publication-type="other" xlink:type="simple">Reich, P.B., Hobbie, S.E., Lee, T., Ellsworth, D.S., West, J.B., Tilman, D., Knops, J.M.H., Naeem, S. and Trost, J. (2006) Nitrogen Limitation Constrains Sustainability of Ecosystem Response to CO&lt;SUB&gt;2&lt;/SUB&gt;. Nature, 440, 922-925.  
https://doi.org/10.1038/nature04486</mixed-citation></ref><ref id="scirp.110902-ref59"><label>59</label><mixed-citation publication-type="other" xlink:type="simple">Finzi, A.C., Moore, D.J.P., De Lucia, E.H., Lichter, J., Hofmockel, K.S., Jackson, R.B., Kim, H.S., Matamala, R., McCarthy, H.R., Oren, R., Pippen, J.S. and Schlesinger, W.H. (2006) Progressive Nitrogen Limitation of Ecosystem Processes under Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; in a Warm-Temperate Forest. Ecology, 87, 15-25.  
https://doi.org/10.1890/04-1748</mixed-citation></ref><ref id="scirp.110902-ref60"><label>60</label><mixed-citation publication-type="other" xlink:type="simple">Finzi, A.C., De Lucia, E.H., Jason, G.H,, Richter, D.D. and Schlesinger, W.H. (2002) The Nitrogen Budget of a Pine Forest under Free Air CO&lt;SUB&gt;2&lt;/SUB&gt; Enrichment. Oecologia, 132, 567-578. https://doi.org/10.1007/s00442-002-0996-3</mixed-citation></ref><ref id="scirp.110902-ref61"><label>61</label><mixed-citation publication-type="other" xlink:type="simple">Elkohen, A. and Mousseau, M. (1994) Interactive Effects of Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; and Mineral Nutrition on Growth and CO&lt;SUB&gt;2&lt;/SUB&gt; Exchange of Sweet Chestnut Seedlings (Castanea sativa). Tree Physiology, 14, 679-690. https://doi.org/10.1093/treephys/14.7-8-9.679</mixed-citation></ref><ref id="scirp.110902-ref62"><label>62</label><mixed-citation publication-type="other" xlink:type="simple">Tissue, D.T. and Lewis, J.D. (2010) Photosynthetic Responses of Cottonwood Seedlings Grown in Glacial through Future Atmospheric [CO&lt;SUB&gt;2&lt;/SUB&gt;] Vary with Phosphorus Supply. Tree Physiology, 30, 1361-1372.  
https://doi.org/10.1093/treephys/tpq077</mixed-citation></ref><ref id="scirp.110902-ref63"><label>63</label><mixed-citation publication-type="other" xlink:type="simple">Peterson, A.G., Ball, J.T., Luo, Y., Field, C.B., Curtis, P.S., Griffin, K.L., Gunderson, C.A., Norby, R.J., Tissue, D.T., Forstreuter, M., Rey, A. and Vogel, C.S. (1999) Quantifying the Response of Photosynthesis to Changes in Leaf Nitrogen Content and Leaf Mass Per Area in Plants Grown under Atmospheric CO&lt;SUB&gt;2&lt;/SUB&gt; Enrichment. Plant Cell and Environment, 22, 1109-1119.  
https://doi.org/10.1046/j.1365-3040.1999.00489.x</mixed-citation></ref><ref id="scirp.110902-ref64"><label>64</label><mixed-citation publication-type="other" xlink:type="simple">Reich, P.B., Hungate, B.A. and Luo, Y. (2006) Carbon-Nitrogen Interactions in Terrestrial Ecosystems in Response to Rising Atmospheric Carbon Dioxide. Annual Review of Ecology, Evolution, and Systematics, 37, 611-636.  
https://doi.org/10.1146/annurev.ecolsys.37.091305.110039</mixed-citation></ref><ref id="scirp.110902-ref65"><label>65</label><mixed-citation publication-type="other" xlink:type="simple">Viereck, L.A. and Johnston, W.F. (1990) Black Spruce. In, Silvics of North America. Forest Service, Washington DC, 227-237.  
https://doi.org/10.1016/S0195-5616(90)50012-1</mixed-citation></ref><ref id="scirp.110902-ref66"><label>66</label><mixed-citation publication-type="other" xlink:type="simple">Morrison, I.K. (1974) Mineral Nutrition of Conifers with Special Reference to Nutrient Status Interpretation: A Review of Literature. 1-74.</mixed-citation></ref><ref id="scirp.110902-ref67"><label>67</label><mixed-citation publication-type="book" xlink:type="simple">Landis, T.D. (1989) Mineral Nutrients and Fertilization. In: Landis, T.D., Tinus, R.W., McDonald, S.E. and Barnett, J.P., Eds., The Container Tree Nursery Manual, Department of Agriculture, Forest Service, Washington DC, 1-67.</mixed-citation></ref><ref id="scirp.110902-ref68"><label>68</label><mixed-citation publication-type="other" xlink:type="simple">Ingestad, T. and Agren, G.I. (1992) Theories and Methods on Plant Nutrition and Growth. Physiologia Plantarum, 84, 177-184.  
https://doi.org/10.1111/j.1399-3054.1992.tb08781.x</mixed-citation></ref><ref id="scirp.110902-ref69"><label>69</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, S.R. and Dang, Q.L. (2007) Interactive Effects of Soil Temperature and [CO&lt;SUB&gt;2&lt;/SUB&gt;] on Morphological and Biomass Traits in Seedlings of Four Boreal Tree Species. Forest Science, 53, 453-460.</mixed-citation></ref><ref id="scirp.110902-ref70"><label>70</label><mixed-citation publication-type="other" xlink:type="simple">Li, J.L., Dang, Q.L., Man, R.Z. and Marfo, J. (2013) Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Alters N-Growth Relationship in Spruce and Causes Unequal Increases in N, P and K Demands. Forest Ecology and Management, 298, 19-26.  
https://doi.org/10.1016/j.foreco.2013.02.024</mixed-citation></ref><ref id="scirp.110902-ref71"><label>71</label><mixed-citation publication-type="other" xlink:type="simple">Watanabe, M. et al. (2011) Growth and Photosynthetic Traits of Hybrid Larch F1 (Larix gmeliniivar. japonica × L. kaempferi) under Elevated CO&lt;SUB&gt;2&lt;/SUB&gt; Concentration with Low Nutrient Availability. Tree Physiology, 31, 965-975. 
https://doi.org/10.1093/treephys/tpr059</mixed-citation></ref><ref id="scirp.110902-ref72"><label>72</label><mixed-citation publication-type="other" xlink:type="simple">Onoda, Y., Hirose, T. and Hikosaka, K. (2009) Does Leaf Photosynthesis Adapt to CO&lt;SUB&gt;2&lt;/SUB&gt;-Enriched Environments? An Experiment on Plants Originating from Three Natural CO&lt;SUB&gt;2&lt;/SUB&gt; Springs. New Phytologist, 182, 698-709. 
https://doi.org/10.1111/j.1469-8137.2009.02786.x</mixed-citation></ref><ref id="scirp.110902-ref73"><label>73</label><mixed-citation publication-type="other" xlink:type="simple">Ellsworth, D.S., Reich, P.B., Naumburg, E., Koch, G.W., Kubiske, M.E. and Smith, S.D. (2004) Photosynsis, Carboxylation and Leaf Nitroeng Responses of 16 Species to Elevated pCO&lt;SUB&gt;2&lt;/SUB&gt; across Four Free—Are CO&lt;SUB&gt;2&lt;/SUB&gt; Enrichment Experiments in Forest, Grassland and Desert. Global Change Biology, 10, 1-18. 
https://doi.org/10.1111/j.1365-2486.2004.00867.x</mixed-citation></ref><ref id="scirp.110902-ref74"><label>74</label><mixed-citation publication-type="other" xlink:type="simple">Norby, R.J., Wullschleger, S.D., Gunderson, C.A., Johnson, D.W. and Ceulemans, R. (1999) Tree Responses to Rising CO&lt;SUB&gt;2&lt;/SUB&gt; in Field Experiments: Implications for the Future Forest. Plant Cell and Environment, 22, 683-714. 
https://doi.org/10.1046/j.1365-3040.1999.00391.x</mixed-citation></ref></ref-list></back></article>