<?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.2015.61022</article-id><article-id pub-id-type="publisher-id">AJPS-53378</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>
 
 
  Photoperiod and Nitrogen Supply Limit the Scope of Northward Migration and Seed Transfer of Black Spruce in a Future Climate Associated with Doubled Atmospheric CO2 Concentration
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>unlin</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>Qing-Lai</surname><given-names>Dang</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>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, Canada</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>qdang@lakeheadu.ca(QD)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>06</day><month>01</month><year>2015</year></pub-date><volume>06</volume><issue>01</issue><fpage>189</fpage><lpage>200</lpage><history><date date-type="received"><day>25</day>	<month>November</month>	<year>2014</year></date><date date-type="rev-recd"><day>accepted</day>	<month>18</month>	<year>January</year>	</date><date date-type="accepted"><day>20</day>	<month>January</month>	<year>2015</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 predicated changes in precipitation and temperature associated with the continued elevation of atmospheric CO2 concentration will trigger the northward shift of the Climate Envelopes for 130 North America tree species by as much as 10 degrees. However, climate envelope models do not take into account changes in other factors that may also influence the survival and growth of plants at the predicted new locations, such as photoperiod and nutrient regimes. This study investigated how photoperiod and nitrogen supply would affect the ecophysiological traits of black spruce (Picea mariana (Mill) B. S. P.) that are critical for survival and growth at new locations predicted by climate envelope models. We exposed black spruce seedlings to the photoperiod regime at the seed origin (PS) and that 10
  &#176; north of the seed origin (PNM) as predicted by climate envelope models under the current and doubled atmospheric CO2 concentration and different levels of N supply (30 vs. 300 μmol
  &#183;mol
  <sup>-1</sup> N). We found that the PNM and the 30 μmol
  &#183;mol
  <sup>-1</sup> N supply both had negative impact on the development of seedling cold hardiness in the fall, and led to earlier burst of the terminal bud and greater rate of mortality in the following growing season. While the PNM stimulated seedling growth in the first growing season, the effect was not sustained in the second growing season. Our results suggest that the photoperiod regimes and poor nutrient conditions at higher latitudes will likely constrain the scope of the northward migration or seed transfer of black spruce.
 
</p></abstract><kwd-group><kwd>Plant Migration</kwd><kwd> Tree Seed Transfer</kwd><kwd> Nutrient</kwd><kwd> Cold Hardiness</kwd><kwd> Picea mariana (Mill) B.S.P.</kwd><kwd> Boreal Forest</kwd><kwd> Climate Envelope</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>As global warming continues [<xref ref-type="bibr" rid="scirp.53378-ref1">1</xref>] , the temperature and precipitation regimes further north may become more suitable for boreal trees [<xref ref-type="bibr" rid="scirp.53378-ref2">2</xref>] - [<xref ref-type="bibr" rid="scirp.53378-ref4">4</xref>] . Northern America is one of the regions with the most pronounced increases in temperature [<xref ref-type="bibr" rid="scirp.53378-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref6">6</xref>] . Based on the projections of temperature and precipitation by the Atmosphere Ocean General Circulation Models, the climate envelopes for 130 North American tree species will shift northward by as much as 10 degrees (about 1100 kilometers) by 2071 to 2100. However, a successful migration or seed transfer of a species may also be influenced by other ecological and environmental factors, such as photoperiod and nutrient supply [<xref ref-type="bibr" rid="scirp.53378-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref8">8</xref>] . For example, a change in photoperiod regime can change the timing of phenological events [<xref ref-type="bibr" rid="scirp.53378-ref9">9</xref>] and a change in nutrient supply may affect survival and growth [<xref ref-type="bibr" rid="scirp.53378-ref10">10</xref>] . It is unknown how changes in photoperiod and nutrient supply may affect the migration or seed transfer of boreal tree species.</p><p>Changes in photoperiod regimes can induce anomalies in phenological events which in turn affect the survival and growth of plants at their new locations. For example, a delayed onset and a lower degree of cold hardening may expose plants to freeze damages in the winter and earlier bud bursts will expose plants to the risk of frost damage in the spring [<xref ref-type="bibr" rid="scirp.53378-ref11">11</xref>] . The ability to develop adequate cold hardiness is critical for the survival of plants in regions with cold winters [<xref ref-type="bibr" rid="scirp.53378-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref13">13</xref>] . Cold hardiness affects not only plant survival in the winter, but also growth in the next growing season because the formation and size of terminal buds as well as the timing of bud burst are closely related to cold hardiness [<xref ref-type="bibr" rid="scirp.53378-ref14">14</xref>] . Although longer summer photoperiods and longer growing seasons at higher latitudes can increase plant growth [<xref ref-type="bibr" rid="scirp.53378-ref15">15</xref>] , the shorter days in the winter and shorter duration of dormancy may affect the growth in the next growing season. A good understanding of the interactive effects of photoperiod, temperature and CO<sub>2</sub> elevations on plant physiology thus may be pivotal for predicting the likelihood of success in plant migration and seed transfer under the predicted future climate conditions.</p><p>The growth of forests at high latitudes is limited by the availability of nitrogen (N) [<xref ref-type="bibr" rid="scirp.53378-ref16">16</xref>] . Although ecosystems at high latitudes can store large amounts of nutrient in the soil, the available N is lower further north due to the lower rates of decomposition and mineralization of organic materials [<xref ref-type="bibr" rid="scirp.53378-ref17">17</xref>] . The predicted 2˚C - 4˚C increase in mean summer temperature does not necessarily translate into a corresponding increase in available N because of interactions among, air temperature, soil temperature, moisture, and soil microorganisms that are adapted to low temperatures [<xref ref-type="bibr" rid="scirp.53378-ref18">18</xref>] . Although low N supplies generally help cold hardening [<xref ref-type="bibr" rid="scirp.53378-ref19">19</xref>] , a certain amount of N is required for the proper development of cold hardiness and other physiological functions [<xref ref-type="bibr" rid="scirp.53378-ref20">20</xref>] . Currently, there are conflicting results in the literature on the relationship between cold hardiness and N supply [<xref ref-type="bibr" rid="scirp.53378-ref21">21</xref>] . Although the effects of CO<sub>2</sub> elevation and nutrient availability on plant physiology and morphology have been studied relatively extensively [<xref ref-type="bibr" rid="scirp.53378-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref23">23</xref>] , the potential impact of changes in N supply and photoperiod on the northward migration or seed transfer of boreal tree species is poorly understood.</p><p>Black spruce is a key tree species in the Canadian boreal forests. It is sensitive to photoperiod [<xref ref-type="bibr" rid="scirp.53378-ref24">24</xref>] and adapted to the photoperiod regimes of its current habitats [<xref ref-type="bibr" rid="scirp.53378-ref9">9</xref>] . For example, its terminal bud formation cannot be initiated by low air temperatures unless accompanied by either a short photoperiod or a low nitrogen supply [<xref ref-type="bibr" rid="scirp.53378-ref25">25</xref>] . Therefore, black spruce is an excellent species to use for studying the interactive effects of CO<sub>2</sub>, photoperiod and nitrogen supply on the migration and seed transfer of boreal trees in the context described previously. In this study, we exposed black spruce seedlings to the photoperiod regime of the seed origin and that at 10˚ north of the seed origin (based on the prediction by Climate Envelope models [<xref ref-type="bibr" rid="scirp.53378-ref26">26</xref>] ) under two nitrogen supplies (low vs. high) and two CO<sub>2</sub> concentrations (current vs. doubled). We hypothesize that the photoperiod regime at the higher latitude and the low N supply would adversely affect the development of cold hardiness and advance the timing of bud burst in the following growing season.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Plant Materials</title><p>Black spruce (Picea mariana [Mill.] B.S.P.) seeds were collected from a 64 year-old black spruce stand near Huntsville, Ontario, Canada (45˚26'49.54''N, 79˚14'35.15''W, elevation 281.9 m). The stand was composed of 70% black spruce, 20% balsam fir (Abies balsamea (L.) Mill., and 10% larch Larix laricina (Du Roi) K. Koch) in a lowland riparian zone near Lake Fish. The soil of the stand was organic layers overlain on mineral with rich nutrient contents. The moisture regime was generally very moist to wet. Daily average air temperatures range from −10.3˚C (January) to 18.7˚C (July). Mean annual precipitation is 1105.1 mm (832.2 mm rain and 338 cm snow fall). About 5000 (about 0.1 pound) seeds were collected from 30 trees at least 50 m apart from each other. The seeds were germinated in the greenhouse. 480 germinants were chosen randomly and transplanted into pots (15 cm tall, 13 cm top diameter). The growing medium was a mixture of peat moss and vermiculite (1/1 v/v).</p></sec><sec id="s2_2"><title>2.2. Experiment Design and Treatments</title><p>The treatments consisted of two CO<sub>2</sub> concentrations (370 vs. 720 &#181;mol∙mol<sup>−1</sup>), two photoperiod regimes (photo- period at seed origin: PS; photoperiod at 10˚ north of seed origin: PNM) and two levels of nitrogen supply (30 vs. 300 &#181;mol∙mol<sup>−1</sup> N).). The photoperiods for PS were 15 and 10 h for active growing and cold hardening phase, respectively and the respective photoperiods for the PNM treatment were 17 and 8 h. The 15-hour photoperiod represents the actual median photoperiod during the growing season at the seed origin and the 17-hour is the corresponding median photoperiod 10˚ north from the seed origin (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The 10 and 8 hour photoperiods represent the median photoperiods during cold hardening phase for the above two locations. 60 &#181;mol∙mol<sup>−1</sup> P</p><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> Schematic diagram of daylength and air temperature at 45˚ (seed origin) and 55˚N latitude (10˚ north from seed origin). Points A and B indicate the critical daylength for bud burst at the two locations while points C and D represent the critical daylength for bud set. T<sub>max</sub> and T<sub>min</sub> are monthly maximum and minimum air temperatures at the location of seed origin (Data source: U.S. Naval Observatory (Astronomical Applications Department, 2009) and World Clim (Hijmans et al., 2005)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x6.png"/></fig><p>and 150 &#181;mol∙mol<sup>−1</sup> K were used in both N treatments. N, P and K were formulated using ammonium nitrate (NH<sub>4</sub>NO<sub>3</sub>), super phosphate (P<sub>2</sub>O<sub>5</sub>), and muriate of potash (K<sub>2</sub>O). The high N concentration and the concentrations of P and K are the optimal levels for the growth of black spruce seedlings (Landis 1989). The experiment was carried out in four greenhouses with identical design features and control devices. Each of the two CO<sub>2</sub> treatments was randomly assigned to two greenhouses. Since the natural day length was shorter than the required photoperiods (started in September), the natural photoperiod was extended using high pressure sodium lamps which gave about 600 &#181;mol∙m<sup>−1</sup>∙s<sup>−1</sup> flux density of photosynthetically active radiation at the canopy level.</p><p>The [CO<sub>2</sub>], photoperiod, temperature and humidity were automatically controlled and monitored using an Argus control system (Argus Control Systems Ltd, Vancouver, BC, Canada). The same temperature regime (25˚C - 26˚C/16˚C - 17˚C day/night temperature) was used for both PS and PNM treatments because according to the theory of climate envelope the temperature and moisture regimes define the climate envelope and would remain the same after the climate envelope shifts to a new location [<xref ref-type="bibr" rid="scirp.53378-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref3">3</xref>] . The photoperiods in all the greenhouses were set to the value for the PNM and the shorter photoperiod for the PS was achieved by shading the seedlings at both ends of the day. The photoperiod treatments were started with the values for the active growing phase (15 hours for 75 days for PS and 17 hours for 95 days for PNM) and followed by the corresponding values for cold hardening (10 hours for 50 days for PS and 8 hours for 30 days for PNM). The photoperiod and temperature regimes (<xref ref-type="fig" rid="fig1">Figure 1</xref>) were determined according to the Astronomical Applications Department (2009) [<xref ref-type="bibr" rid="scirp.53378-ref27">27</xref>] and Hijmans et al. (2005) [<xref ref-type="bibr" rid="scirp.53378-ref28">28</xref>] . The seedlings were fertilized once a week. The water content of the growing medium was maintained above 30% as determined using an HH2 Moisture Meter (Delta-T Devices, Cambridge, U.K.). The seedlings were watered to the dripping point when the volumetric water content of the growing medium declined to 30% [<xref ref-type="bibr" rid="scirp.53378-ref29">29</xref>] .</p></sec><sec id="s2_3"><title>2.3. Measurements</title><p>After 125-days of treatments (Growth Cycle I), height, root collar diameter, terminal bud size, biomass, chlorophyll fluorescence and cold hardiness were measured on seedlings randomly selected from each treatment combination (30 seedlings for height, root collar diameter and terminal bud size, 3 for biomass, 10 for chlorophyll fluorescence, and 15 for cold hardiness). Stem volume (V) was calculated from height (H) and RCD (D) according to van den Driessche (1992): V = (πD<sup>2</sup>/4)H/3. Biomass was determined separately for shoots and roots after oven-drying at 75˚C for 48 hours in order to calculate root mass ratio (RMR = root mass/total seedling mass).</p><p>Chlorophyll fluorescence was measured on the terminal shoot using an FMS 2 pulse modulated chlorophyll fluorometer following a 30 min dark adaptation (Hansatech Instruments Ltd, Norfolk, England). The maximum quantum efficiency of Photosystem II was derived from the initial (Fo) and maximum (Fm) fluorescence (Fv/Fm = (Fm-Fo)/Fm). The length and width of the terminal bud were determined using an AMS-MV2 high-resolution digital imaging system (Advanced Microscopy Group, Mill Creek, WA, USA, 2008) and Micron Imaging Software (USB2) 1.08 (Westover Scientific, Inc., Mill Creek, WA, USA, 2008).</p><p>The cold hardiness was assessed according to Colombo et al. [<xref ref-type="bibr" rid="scirp.53378-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref31">31</xref>] . 2 - 3 cm long shoot tips were cut and rinsed with distilled water. Three tips were used for each of the following test temperatures: control (no freezing), −5˚C, −15˚C, −30˚C and −60˚C. Each tip was placed in a separate jar filled with 100 ml distilled water and incubated at room temperature (20˚C - 25˚C) for 24 hours. The electrical conductivity of the solution was measured (referred to as ECC) using an Accumet AR 20 electrical conductivity meter (Fisher Scientific, Ottawa, Canada). Each test temperature was achieved using a programmable freezer (Foster Refrigeration Ltd, King’s Lynn Norfolk, U. K.) by reducing the temperature at a rate of 5˚C/h. One hour after the testing temperature was reached, the temperature was increased back to the room temperature at a rate of 5˚C/h and the electric conductivity of the solution was again measured (referred to as ECF). Subsequently the jars were placed in an oven at 80˚C for two hours. After cooling to the room temperature overnight, the electric conductivity of the solution was measured again (referred to as ECK). The injury index (I<sub>i</sub>), which is inversely related to the cold hardiness, was calculated according to Colombo et al. [<xref ref-type="bibr" rid="scirp.53378-ref30">30</xref>] (1984) and Colombo [<xref ref-type="bibr" rid="scirp.53378-ref31">31</xref>] (2003) as follows:</p><disp-formula id="scirp.53378-formula64"><graphic  xlink:href="http://html.scirp.org/file/22-2601868x7.png"  xlink:type="simple"/></disp-formula><p>At the completion of all the measurements, all remaining seedlings were cold-stored (−4˚C) for three months for the second growth cycle. The second growth cycle was aimed to examine the treatment effects on bud phenology and seedling survival and growth in the next growing season. The seedlings were exposed to the same growth conditions as in Growth Cycle I. The seedlings in the PS treatment were exposed to short photoperiod (10 hours) for three weeks and then to the long photoperiod (15 hours) for six weeks while the seedlings in the PNM treatment were first exposed to the corresponding short photoperiod (8 hours) for one week and then to the corresponding long photoperiod (17 hours) for eight weeks. The earlier start of the long photoperiod in the PNM treatment was dictated by the faster rate of change in photoperiod at the higher latitude (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The bud phenology was observed daily. The total number of days in the long photoperiod regime to bud burst (DBBL) were recorded. Height and RCD were measured again at the end of the second growth cycle. The relative growth rates of height (RGR<sub>h</sub>), RCD (RGR<sub>d</sub>) and volume (RGR<sub>v</sub>) were determined by dividing the growth increments in the second growth cycle by the corresponding measurements at the end of the first growth cycle.</p></sec><sec id="s2_4"><title>2.4. Statistical Analysis</title><p>The experiment was a split-plot design with CO<sub>2</sub> treatment as the main plot and factorial combinations of photoperiod and nutrient supply as the split plot. The data were examined graphically for normality (probability plots for residuals) and homogeneity of variance (scatter plots). Both assumptions for the analysis of variance (ANOVA) were satisfied. When ANOVA showed a significant interaction (P ≤ 0.05), the Least Significant Difference (LSD) multiple comparisons were conducted. Since all the seedlings in the low N treatment died in the 2<sup>nd</sup> growth cycle, the nitrogen treatment was not included in the analysis for growth cycle II. All the analyses were conducted using the GenStat statistics package, 12th Edition (VSN international Ltd, Hemel Hempstead, UK, 2009).</p></sec></sec><sec id="s3"><title>3. Results</title><sec id="s3_1"><title>3.1. Morphology and Biomass</title><p>N supply significantly affected the responses of seedling height, RCD, biomass and biomass allocation to roots to photoperiod and [CO<sub>2</sub>] (N &#215; P, N &#215; C and N &#215; P &#215; C in <xref ref-type="table" rid="table1">Table 1</xref>). While the CO<sub>2</sub> elevation and PNM both increased height and RCD growth, the increases were greater in the high than low N supply (<xref ref-type="fig" rid="fig2">Figure 2</xref>). In fact, the increases in RCD were not statistically significant in the low N treatment (<xref ref-type="fig" rid="fig2">Figure 2</xref>(c) and <xref ref-type="fig" rid="fig2">Figure 2</xref>(d)). The PNM also resulted in a greater increase in seedling biomass in the high than in the low N supply (<xref ref-type="fig" rid="fig3">Figure 3</xref>(b)).</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> P values for treatment effects of CO<sub>2</sub> concentration (C, 370 and 720 μmol∙mol<sup>−1</sup>), photoperiod (P, seed origin and 10˚ north), nutrient supply (N, 30 and 300 μmol∙mol<sup>−1</sup> N) and their interactions on height (H), root collar diameter (RCD), bud length (BL), bud width (BW), root mass ratio (RMR), total biomass (TM), index of injury (Ii) (at test temperatures of −5˚C, −15˚C, −30˚C, and −60˚C), and maximum quantum efficiency of PSII (F<sub>v</sub>/F<sub>m</sub>) of black spruce seedlings after for 125 days of growth (Growing season I)</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Source of variation</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" >P</td><td align="center" valign="middle" >N</td><td align="center" valign="middle" >C &#215; P</td><td align="center" valign="middle" >C &#215; N</td><td align="center" valign="middle" >P &#215; N</td><td align="center" valign="middle" >C &#215; P &#215; N</td></tr><tr><td align="center" valign="middle" >H</td><td align="center" valign="middle" >0.035</td><td align="center" valign="middle" >0.015</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.564</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >0.005</td><td align="center" valign="middle" >0.659</td></tr><tr><td align="center" valign="middle" >RCD</td><td align="center" valign="middle" >0.115</td><td align="center" valign="middle" >0.062</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.981</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.206</td></tr><tr><td align="center" valign="middle" >BL</td><td align="center" valign="middle" >0.097</td><td align="center" valign="middle" >0.049</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.134</td><td align="center" valign="middle" >0.403</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >0.652</td></tr><tr><td align="center" valign="middle" >BW</td><td align="center" valign="middle" >0.37</td><td align="center" valign="middle" >0.137</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >0.173</td><td align="center" valign="middle" >0.268</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >0.383</td></tr><tr><td align="center" valign="middle" >RMR</td><td align="center" valign="middle" >0.239</td><td align="center" valign="middle" >0.012</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.889</td><td align="center" valign="middle" >0.005</td><td align="center" valign="middle" >0.718</td><td align="center" valign="middle" >0.02</td></tr><tr><td align="center" valign="middle" >TM</td><td align="center" valign="middle" >0.527</td><td align="center" valign="middle" >0.114</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.806</td><td align="center" valign="middle" >0.107</td><td align="center" valign="middle" >0.05</td><td align="center" valign="middle" >0.115</td></tr><tr><td align="center" valign="middle" >F<sub>v</sub>/F<sub>m</sub></td><td align="center" valign="middle" >0.097</td><td align="center" valign="middle" >0.275</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.479</td><td align="center" valign="middle" >0.249</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.851</td></tr><tr><td align="center" valign="middle" >Ii (−5˚C)</td><td align="center" valign="middle" >0.904</td><td align="center" valign="middle" >0.08</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >0.379</td><td align="center" valign="middle" >0.161</td><td align="center" valign="middle" >0.802</td><td align="center" valign="middle" >0.709</td></tr><tr><td align="center" valign="middle" >Ii (−15˚C)</td><td align="center" valign="middle" >0.072</td><td align="center" valign="middle" >0.043</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.871</td><td align="center" valign="middle" >0.008</td><td align="center" valign="middle" >0.034</td><td align="center" valign="middle" >0.754</td></tr><tr><td align="center" valign="middle" >Ii (−30˚C)</td><td align="center" valign="middle" >0.057</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.038</td><td align="center" valign="middle" >0.246</td><td align="center" valign="middle" >0.022</td><td align="center" valign="middle" >0.946</td></tr><tr><td align="center" valign="middle" >Ii (−60˚C)</td><td align="center" valign="middle" >0.071</td><td align="center" valign="middle" >0.626</td><td align="center" valign="middle" >&lt;0.001</td><td align="center" valign="middle" >0.867</td><td align="center" valign="middle" >0.494</td><td align="center" valign="middle" >0.128</td><td align="center" valign="middle" >0.124</td></tr></tbody></table></table-wrap><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Mean (+SEM) height (a and b) and root collar diameter (c and d) of black spruce seedlings after 125 days of growth under two [CO<sub>2</sub>] (C) levels (370 (ambient) vs. 720 (elevated) μmol∙mol<sup>−1</sup> CO<sub>2</sub>), two photoperiods (P) (PS―seed origin and PNM-10˚ north of seed origin), and two nutrient supply (N) levels (30 (Low) vs. 300 (High) μmol∙mol<sup>−1</sup> N). “<sup>*</sup>” indicates significant effects (P ≤ 0.05). Means with different letters were significantly different from each other (P ≤ 0.05)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x8.png"/></fig><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Mean (+SEM) root mass ratio and total seedling biomass in black spruce. “AL” represents for the treatment combination of “ambient [CO<sub>2</sub>] &#215; low N supply”, “AH” for “ambient [CO<sub>2</sub>] &#215; high N supply”, “EL” for “elevated [CO<sub>2</sub>] &#215; low N supply”, and “EH” for “elevated [CO<sub>2</sub>] &#215; high N supply”. See <xref ref-type="fig" rid="fig2">Figure 2</xref> for other explanations</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x9.png"/></fig><p>The CO<sub>2</sub> elevation decreased the root mass ratio in the low N supply in both photoperiod treatments but increased RMR under the high N supply and PS (<xref ref-type="fig" rid="fig3">Figure 3</xref>(a)). While the PNM generally decreased RMR, there were significant interactions with CO<sub>2</sub> and N: the photoperiod impact was greater in the low than the high N treatment under the ambient [CO<sub>2</sub>] but the trend was the opposite under the elevated [CO<sub>2</sub>], i.e., the impact was greater in the high than the low N treatment (<xref ref-type="fig" rid="fig3">Figure 3</xref>(a)).</p><p>All the seedlings in the low N treatment died in the second growth cycle and thus N supply was not considered in the second growth cycle. While the positive effect of PNM on height growth remained significant (30.47 &#177; 1.40 vs. 26.49 &#177; 1.03 cm, <xref ref-type="table" rid="table2">Table 2</xref>) in the second growth cycle, the effects of PNM and [CO<sub>2</sub>] on RCD became insignificant (<xref ref-type="table" rid="table2">Table 2</xref>). The relative growth rates of height, stem volume and RCD, however, showed opposite trends to those of height and RCD growth, i.e., PNM reduced the RGR for height (0.44 &#177; 0.01 for PNM vs. 0.59 &#177; 0.01 cm∙cm<sup>−1</sup> for PS), stem volume (3.23 &#177; 0.15 vs. 6.39 &#177; 0.22 cm<sup>3</sup>∙cm<sup>−3</sup>) and RCD (<xref ref-type="fig" rid="fig3">Figure 3</xref>(c)). The CO<sub>2</sub> elevation also significantly reduced the RGR<sub> </sub>of RCD under the PNM but did not affect it under the PS (<xref ref-type="table" rid="table2">Table 2</xref> and <xref ref-type="fig" rid="fig3">Figure 3</xref>(c)). Photoperiod also had no significant effects on height increment (Hi) or RCD increment (RCDi) in the second growth cycle. No treatment had a significant effect on total seedling biomass in the second growth cycle (<xref ref-type="table" rid="table2">Table 2</xref>).</p></sec><sec id="s3_2"><title>3.2. Bud Size, Chlorophyll Fluorescence and Cold Hardiness</title><p>Buds were much longer and wider under the PS than PNM photoperiod regime in the high N treatment, but photoperiod had no significant effect on bud size in the low N treatment (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="fig" rid="fig4">Figure 4</xref>). The elevated [CO<sub>2</sub>] also did not significantly affect bud size (<xref ref-type="table" rid="table1">Table 1</xref>).</p><p>In the first growth cycle, the maximum quantum efficiency of PSII (F<sub>v</sub>/F<sub>m</sub>) was greater in the high than low N treatment in both photoperiod treatments, and the PNM significantly increased F<sub>v</sub>/F<sub>m</sub> only at the high N (P &#215; N interaction in <xref ref-type="table" rid="table1">Table 1</xref>, <xref ref-type="fig" rid="fig5">Figure 5</xref>(a)). In the following growth cycle, the PNM significantly increased F<sub>v</sub>/F<sub>m</sub> under the elevated [CO<sub>2</sub>], and the CO<sub>2</sub> elevation increased F<sub>v</sub>/F<sub>m</sub> in both photoperiod treatments (C &#215; P interaction in <xref ref-type="table" rid="table2">Table 2</xref>, <xref ref-type="fig" rid="fig5">Figure 5</xref>(b)).</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> P values for treatments effects of CO<sub>2</sub> concentration (C, 370 and 720 μmol∙mol<sup>−1</sup>), photoperiod (P, seed origin and 10˚ north), and their interactions on height (H), root collar diameter (RCD), height increment (H<sub>i</sub>), RCD increment (RCD<sub>i</sub>), relative growth rates of height (RGR<sub>h</sub>), root collar diameter (RGR<sub>d</sub>) and volume (RGR<sub>v</sub>), root mass ratio (RMR), total biomass (TM), number of long days to bud burst (DBBL), mortality, and maximum quantum efficiency of PSII photochemistry (F<sub>v</sub>/F<sub>m</sub>) of black spruce seedlings after 63 days of growth in the Growing season II. The level of nutrient supply was dropped due to seedlings mortality after cold storage</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Source of variation</th><th align="center" valign="middle"  colspan="3"  >Treatment effects</th></tr></thead><tr><td align="center" valign="middle" >C</td><td align="center" valign="middle" >P</td><td align="center" valign="middle" >C &#215; P</td></tr><tr><td align="center" valign="middle" >H</td><td align="center" valign="middle" >0.056</td><td align="center" valign="middle" >0.029</td><td align="center" valign="middle" >0.221</td></tr><tr><td align="center" valign="middle" >RCD</td><td align="center" valign="middle" >0.112</td><td align="center" valign="middle" >0.483</td><td align="center" valign="middle" >0.896</td></tr><tr><td align="center" valign="middle" >Hi</td><td align="center" valign="middle" >0.076</td><td align="center" valign="middle" >0.382</td><td align="center" valign="middle" >0.896</td></tr><tr><td align="center" valign="middle" >RCDi</td><td align="center" valign="middle" >0.277</td><td align="center" valign="middle" >0.368</td><td align="center" valign="middle" >0.407</td></tr><tr><td align="center" valign="middle" >RGRh</td><td align="center" valign="middle" >0.157</td><td align="center" valign="middle" >0.018</td><td align="center" valign="middle" >0.486</td></tr><tr><td align="center" valign="middle" >RGRd</td><td align="center" valign="middle" >0.14</td><td align="center" valign="middle" >0.003</td><td align="center" valign="middle" >0.042</td></tr><tr><td align="center" valign="middle" >RGRv</td><td align="center" valign="middle" >0.278</td><td align="center" valign="middle" >0.005</td><td align="center" valign="middle" >0.081</td></tr><tr><td align="center" valign="middle" >RMR</td><td align="center" valign="middle" >0.532</td><td align="center" valign="middle" >0.057</td><td align="center" valign="middle" >0.173</td></tr><tr><td align="center" valign="middle" >TM</td><td align="center" valign="middle" >0.393</td><td align="center" valign="middle" >0.124</td><td align="center" valign="middle" >0.777</td></tr><tr><td align="center" valign="middle" >DBBL</td><td align="center" valign="middle" >0.332</td><td align="center" valign="middle" >0.947</td><td align="center" valign="middle" >0.567</td></tr><tr><td align="center" valign="middle" >F<sub>v</sub>/F<sub>m</sub></td><td align="center" valign="middle" >0.011</td><td align="center" valign="middle" >0.032</td><td align="center" valign="middle" >0.053</td></tr><tr><td align="center" valign="middle" >Mortality</td><td align="center" valign="middle" >0.795</td><td align="center" valign="middle" >0.012</td><td align="center" valign="middle" >0.423</td></tr></tbody></table></table-wrap><fig id="fig4"  position="float"><label><xref ref-type="fig" rid="fig4">Figure 4</xref></label><caption><title> Mean (+SEM) bud length and bud width in black spruce seedlings. See <xref ref-type="fig" rid="fig2">Figure 2</xref> for other explanations</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x10.png"/></fig><fig id="fig5"  position="float"><label><xref ref-type="fig" rid="fig5">Figure 5</xref></label><caption><title> Mean (+SEM) maximum quantum efficiency of PSII (F<sub>v</sub>/F<sub>m</sub>) of black spruce seedlings measured in the first (a) and second growth cycle (b). See <xref ref-type="fig" rid="fig2">Figure 2</xref> for other explanations</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x11.png"/></fig><p>The freezing injury was generally much greater in the low than high N treatment at all the freezing temperatures (−5˚C to −60˚C, <xref ref-type="table" rid="table1">Table 1</xref>). For example, the injury index at −5˚C was 4.20 &#177; 0.34 (mean &#177; SEM) and 2.87 &#177; 0.20 for the low and high N respectively, and 30.91 &#177; 0.81 and 15.15 &#177; 0.89 for the low and high N respectively at −60˚C. N supply also significantly influenced the effects of [CO<sub>2</sub>] and photoperiod on freezing injuries at the two modest freezing temperatures, −15˚C and −30˚C (<xref ref-type="table" rid="table1">Table 1</xref>). While the injury index was generally greater in the PNM than in the PS, the difference was greater in the high N treatment at −15˚C but trend was the reverse at −30˚C (<xref ref-type="fig" rid="fig6">Figure 6</xref>(a) &amp; <xref ref-type="fig" rid="fig6">Figure 6</xref>(c)). The CO<sub>2</sub> elevation reduced the freezing injury in the low but not in the high N treatment (<xref ref-type="fig" rid="fig6">Figure 6</xref>(b)). The CO<sub>2</sub> elevation increased freezing injury in both photoperiod treatments but the PNM increased freezing injury only under the ambient [CO<sub>2</sub>] (<xref ref-type="fig" rid="fig6">Figure 6</xref>(d)).</p></sec><sec id="s3_3"><title>3.3. Mortality and DBBL</title><p>Seedling mortality was greater in the PNM than the PS (<xref ref-type="table" rid="table2">Table 2</xref>; 41.46% &#177; 4.81% vs. 4.17% &#177; 0.41%). None of the treatments had a significant effect on the timing of bud burst (DBBL in <xref ref-type="table" rid="table2">Table 2</xref>).</p></sec></sec><sec id="s4"><title>4. Discussion</title><p>Our data suggest that CO<sub>2</sub> elevations, photoperiod regimes further north from the seed origin and high nitrogen supply will likely increase the growth of black spruce. The results are consistent with the findings of others that elevated CO<sub>2</sub> alone [<xref ref-type="bibr" rid="scirp.53378-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref32">32</xref>] - [<xref ref-type="bibr" rid="scirp.53378-ref35">35</xref>] or in combination with high nutrient supply [<xref ref-type="bibr" rid="scirp.53378-ref36">36</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref37">37</xref>] enhances photosynthesis and promotes growth. The increased growth under the PNM was probably due to the longer photoperiod (17 h vs. 15 h) during the longer growing season (95 days vs. 75 days, <xref ref-type="fig" rid="fig1">Figure 1</xref>). The growth stimulation by PNM was further enhanced by the high N supply. Lower biomass allocations to roots under certain conditions, such as less nutrient stress [<xref ref-type="bibr" rid="scirp.53378-ref38">38</xref>] or drought stress [<xref ref-type="bibr" rid="scirp.53378-ref39">39</xref>] , also lead to greater aboveground growth, as evidenced by the enhanced seedling height and RCD in this study. The growth enhancement by the CO<sub>2</sub> elevation or PNM, however, largely disappeared in the second growth cycle, resulting in lower relative growth rates. The reversal of growth enhancement in the second growth cycle may have been related to the poor quality of buds and inadequate development of cold hardiness. The shorter time period for cold hardening under the PNM may have been a contributing factor.</p><fig id="fig6"  position="float"><label><xref ref-type="fig" rid="fig6">Figure 6</xref></label><caption><title> Mean (+SEM) injury index of black spruce seedlings measured at different freezing temperatures. See <xref ref-type="fig" rid="fig2">Figure 2</xref> for other explanations</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/22-2601868x12.png"/></fig><p>Our results suggest that the change in photoperiod regime associated with a northward migration will likely retard the development of adequate cold hardiness and thus limit the scope of such migrations or seed transfers. Black spruce is sensitive to changes in photoperiod [<xref ref-type="bibr" rid="scirp.53378-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref40">40</xref>] and continues vegetative growth without setting buds under long days [<xref ref-type="bibr" rid="scirp.53378-ref41">41</xref>] . The longer growing season photoperiods north of the seed origin reduce the time period for the development of cold hardiness in the fall, leading to deteriorated cold hardiness and increased vulnerability to freezing injuries as indicated by the smaller bud size [<xref ref-type="bibr" rid="scirp.53378-ref42">42</xref>] , higher F<sub>v</sub>/F<sub>m</sub> and F<sub>o</sub> [<xref ref-type="bibr" rid="scirp.53378-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref43">43</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref44">44</xref>] and greater freezing injury index. Therefore, although the climate envelope for the species may shift to higher latitudes under the predicted scenario of climate change, a successful migration or seed transfer will depend on the ability of the specific genetic material to develop adequate cold hardiness in shortened periods of time for cold hardening with greater rates of temperature declining than their current habitats. This ecophysiological trait may be critical for the success of future tree breeding programs in forestry.</p><p>The results also demonstrate that an adequate nutrient supply is critical for the development of proper cold hardiness in black spruce. This finding is consistent with the results of other studies [<xref ref-type="bibr" rid="scirp.53378-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref25">25</xref>] [<xref ref-type="bibr" rid="scirp.53378-ref45">45</xref>] . It is well known that too much nutrient supply, particularly nitrogen, has negative impact on the development of plant cold hardiness [<xref ref-type="bibr" rid="scirp.53378-ref19">19</xref>] . However, it is less well known that too little nutrient supply can also jeopardize the hardening in the fall [<xref ref-type="bibr" rid="scirp.53378-ref20">20</xref>] . The results of this study show that insufficient supply of nitrogen can jeopardize the proper hardening of black spruce and lead to severe freezing injuries and mortality in the following growing season. This suggests that low nutrient availability may also restrict the natural spread or introduction of black spruce to poor sites.</p></sec><sec id="s5"><title>Acknowledgements</title><p>We thank Dr. C. Shahi for advice on statistics and J. Lee for greenhouse assistance. This study was supported by NSERC DG to Q.L. Dang.</p></sec><sec id="s6"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.53378-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">IPCC (2007) Climate Change 2007: The Physical Science Basis. Cambridge University Press, Cambridge.</mixed-citation></ref><ref id="scirp.53378-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">McKenney, Daniel W., Pedlar, J.H., Lawrence, K., Campbell, K. and Hutchinson, M.F. (2007) Potential Impacts of Climate Change on the Distribution of North American Trees. BioScience, 57, 939-948.  
http://dx.doi.org/10.1641/B571106</mixed-citation></ref><ref id="scirp.53378-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">McKenney, D.W., Pedlar, J.H., Rood, R.B. and Price, D. (2011) Revisiting Projected Shifts in the Climate Envelopes of North American Trees Using Updated General Circulation Models. Global Change Biology, 17, 2720-2730.  
http://dx.doi.org/10.1111/j.1365-2486.2011.02413.x</mixed-citation></ref><ref id="scirp.53378-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Walther, G.R., Post, E., Convey, P., Menzel, A., Parmesan, C., Beebee, T.J.C., Fromentin, J.M., Hoegh-Guldberg, O. and Bairlein, F. (2002) Ecological Responses to Recent Climate Change. Nature, 416, 389-395.  
http://dx.doi.org/10.1038/416389a</mixed-citation></ref><ref id="scirp.53378-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Bronson, D.R., Gower, S.T., Tanner, M. and Van Herk, I. (2009) Effect of Ecosystem Warming on Boreal Black Spruce Bud Burst and Shoot Growth. Global Change Biology, 15, 1534-1543.  
http://dx.doi.org/10.1111/j.1365-2486.2009.01845.x</mixed-citation></ref><ref id="scirp.53378-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Hansen, J., Ruedy, R. and Sato, M. (1996) Global Surface Air Temperature in 1995: Return to Pre-Pinatubo Level. Geophysical Research Leiters, 23, 1665-1668. http://dx.doi.org/10.1029/96GL01040</mixed-citation></ref><ref id="scirp.53378-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Chen, C., Hill, J.K., Ohlemuller, R., Roy, D.B. and Thomas, C.D. (2011) Rapid Range Shifts of Species Associated with High Levels of Climate Warming. Science, 333, 1024-1026. http://dx.doi.org/10.1126/science.1206432</mixed-citation></ref><ref id="scirp.53378-ref8"><label>8</label><mixed-citation publication-type="journal" xlink:type="simple"><name name-style="western"><surname>Pitelka</surname><given-names> L.F. </given-names></name>,<etal>et al</etal>. (<year>1997</year>)<article-title>Plant Migration and Climate Change</article-title><source> American Scientist</source><volume> 85</volume>,<fpage> 464</fpage>-<lpage>473</lpage>.<pub-id pub-id-type="doi"></pub-id></mixed-citation></ref><ref id="scirp.53378-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Thomas, B. and Vince-Prue, D. (1997) Photoperiodism in Plants. Second Edition, Academic Press, London.</mixed-citation></ref><ref id="scirp.53378-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Marschner, H. (1995) Mineral Nutrition of Higher Plants. Academic Press, San Diego.</mixed-citation></ref><ref id="scirp.53378-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Man, R.Z., Kayahara, G.J., Dang, Q.L. and Rice, J.A. (2009) A Case of Severe Frost Damage Prior to Budbreak in Young Conifers in Northeastern Ontario: Consequence of Climate Change? The Forestry Chronicle, 85, 453-462.  
http://dx.doi.org/10.5558/tfc85453-3</mixed-citation></ref><ref id="scirp.53378-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Weiser, C.J. (1970) Cold Resistance and Injury in Woody Plants: Knowledge of Hardy Plant Adaptations to Freezing Stress May Help Us to Reduce Winter Damage. Science, 169, 1269-1278.  
http://dx.doi.org/10.1126/science.169.3952.1269</mixed-citation></ref><ref id="scirp.53378-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Li, P.H. and Sakai, A. (1978) Plant Cold Hardiness and Freezing Stress. Academic Press, New York.</mixed-citation></ref><ref id="scirp.53378-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Colombo, S.J., Zhao, S.Y. and Blumwald, E. (1995) Frost Hardiness Gradients in Shoots and Roots of Picea mariana Seedlings. Scandinavian Journal of Forest Research, 10, 32-36.</mixed-citation></ref><ref id="scirp.53378-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Hay, R.K.M. (1990) The Influence of Photoperiod on the Dry Matter Production of Grasses and Cereals. New Phytologist, 116, 233-254. http://dx.doi.org/10.1111/j.1469-8137.1990.tb04711.x</mixed-citation></ref><ref id="scirp.53378-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Houlton, B.Z., Wang, Y.P., Vitousek, P.M. and Field, C.B. (2008) A Unifying Framework for Dinitrogen Fixation in the Terrestrial Biosphere. Nature, 454, 327-330. http://dx.doi.org/10.1038/nature07028</mixed-citation></ref><ref id="scirp.53378-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Couteaux, M.M., Bottner, P. and Berg, B. (1995) Litter Decomposition, Climate and Liter Quality. Trends in Ecology &amp; Evolution, 10, 63-66. http://dx.doi.org/10.1016/S0169-5347(00)88978-8</mixed-citation></ref><ref id="scirp.53378-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Robinson, C.H. (2002) Controls on Decomposition and Soil Nitrogen Availability at High Latitudes. Plant and Soil, 242, 65-81. http://dx.doi.org/10.1023/A:1019681606112</mixed-citation></ref><ref id="scirp.53378-ref19"><label>19</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, Vol. 4, Department of Agriculture, Forest Service, Washington DC, 1-67.</mixed-citation></ref><ref id="scirp.53378-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">Miller, B.D. and Timmer, V.R. (1997) Nutrient Dynamics and Carbon Partitioning in Nutrient Loaded Picea mariana [Mill.] B.S.P. Seedlings during Hardening. Scandinavian Journal of Forest Research, 12, 122-129.  
http://dx.doi.org/10.1080/02827589709355393</mixed-citation></ref><ref id="scirp.53378-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">Puertolas, J., Gil, L. and Pardos, J.A. (2005) Effects of Nitrogen Fertilization and Temperature on Frost Hardiness of Aleppo Pine (Pinus halepensis Mill.) Seedlings Assessed by Chlorophyll Fluorescence. Forestry, 78, 501-511.  
http://dx.doi.org/10.1093/forestry/cpi055</mixed-citation></ref><ref id="scirp.53378-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">Bigras, F.J. and Bertrand, A. (2006) Responses of Picea mariana to Elevated CO2 Concentration during Growth, Cold Hardening and Dehardening: Phenology, Cold Tolerance, Photosynthesis and Growth. Tree Physiology, 26, 875-888.  
http://dx.doi.org/10.1093/treephys/26.7.875</mixed-citation></ref><ref id="scirp.53378-ref23"><label>23</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) CO2 Enhancement of Forest Productivity Constrained by Limited Nitrogen Availability. Proceedings of the National Academy of Sciences of the United States of America, 107, 19368-19373.</mixed-citation></ref><ref id="scirp.53378-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">D’Aoust, A.L. and Hubac, C. (1986) Phytochrome Action and Frost Hardening in Black Spruce Seedlings. Physiologia Plantarum, 67, 141-144. http://dx.doi.org/10.1111/j.1399-3054.1986.tb02435.x</mixed-citation></ref><ref id="scirp.53378-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Bigras, F.J., Gonzalez, A., D’Aoust, A.L. and Hebert, C. (1996) Frost Hardiness, Bud Phenology and Growth of Containerized Picea mariana Seedlings Grown at Three Nitrogen Levels and Three Temperature Regimes. New Forests, 12, 243-259.</mixed-citation></ref><ref id="scirp.53378-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Pearson, R.G. and Dawson, T.P. (2003) Predicting the Impacts of Climate Change on the Distribution of Species: Are Bioclimate Envelope Models Useful? Global Ecology and Biogeography, 12, 361-371.  
http://dx.doi.org/10.1046/j.1466-822X.2003.00042.x</mixed-citation></ref><ref id="scirp.53378-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">Astronomical Applications Department, U. S. Naval Observatory (2011) Table of Sunrise/Sunset for an Entire Year.  
http://aa.usno.navy.mil/data/docs/RS_OneYear.php</mixed-citation></ref><ref id="scirp.53378-ref28"><label>28</label><mixed-citation publication-type="other" xlink:type="simple">Hijmans, R.J., Cameron, S.E., Parra, J.L., Jones, P.G. and Jarvis, A. (2005) Very High Resolution Interpolated Climate Surfaces for Global Land Areas. International Journal of Climatology, 25, 1965-1978.  
http://dx.doi.org/10.1002/joc.1276</mixed-citation></ref><ref id="scirp.53378-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Bergeron, O., Lamhamedi, M.S., Margolis, H.A., Bernier, P.Y. and Stowe, D.C. (2004) Irrigation Control and Physiological Responses of Nursery-Grown Black Spruce Seedlings (1 + 0) Cultivated in Air-Slit Containers. HortScience, 39, 599-605.</mixed-citation></ref><ref id="scirp.53378-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">Colombo, S.J., Webb, D.P. and Glerum, C. (1984) Frost Hardiness Testing: An Operational Manual for Use with Extended Greenhouse Culture. Ontario Ministry of Natural Resources, Forest Research Report No. 110, 1-14.</mixed-citation></ref><ref id="scirp.53378-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Colombo, S.J., Glerum, C. and Webb, D.P. (2003) Daylength, Temperature and Fertilization Effects on Desiccation Resistance, Cold Hardiness and Root Growth Potential of Picea mariana Seedlings. Annals of Forest Science, 60, 307-317. http://dx.doi.org/10.1051/forest:2003022</mixed-citation></ref><ref id="scirp.53378-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">DeLucia, E.H. and Thomas, R.B. (2000) Photosynthetic Responses to CO2 Enrichment of Four Hardwood Species in a Forest Understory. Oecologia, 122, 11-19. http://dx.doi.org/10.1007/PL00008827</mixed-citation></ref><ref id="scirp.53378-ref33"><label>33</label><mixed-citation publication-type="other" xlink:type="simple">El Kohen, A. and Mousseau, M. (1994) Interactive Effects of Elevated CO2 and Mineral Nutrition on Growth and CO2 Exchange of Sweet Chestnut Seedlings (Castanea sativa). Tree Physiology, 14, 679-690.  
http://dx.doi.org/10.1093/treephys/14.7-8-9.679</mixed-citation></ref><ref id="scirp.53378-ref34"><label>34</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 CO2-Enriched Sweetgum Forest. Ecology, 87, 5-14. http://dx.doi.org/10.1890/04-1950</mixed-citation></ref><ref id="scirp.53378-ref35"><label>35</label><mixed-citation publication-type="other" xlink:type="simple">Yazaki, K., Ishida, S., Kawagishi, T., Fukatsu, E., Maruyama, Y., Kitao, M., Tobita, H., Koike, T. and Funada, T.R. (2004) Effects of Elevated CO2 Concentration on Growth, Annual Ring Structure and Photosynthesis in Larix kaempferi Seedlings. Tree Physiology, 24, 941-949. http://dx.doi.org/10.1093/treephys/24.9.941</mixed-citation></ref><ref id="scirp.53378-ref36"><label>36</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, S.R., Dang, Q.L. and Yu, X.G. (2006) Nutrient and [CO2] Elevation Had Synergistic Effects on Biomass Production but Not on Biomass Allocation of White Birch Seedlings. Forest Ecology and Management, 234, 238-244.  
http://dx.doi.org/10.1016/j.foreco.2006.07.017</mixed-citation></ref><ref id="scirp.53378-ref37"><label>37</label><mixed-citation publication-type="other" xlink:type="simple">Wang, Z.M., Lechowicz, M.J. and Potvin, C. (1995) Responses of Black Spruce Seedlings to Simulated Present versus Future Seedbed Environments. Canadian Journal of Forest Research, 25, 545-554.</mixed-citation></ref><ref id="scirp.53378-ref38"><label>38</label><mixed-citation publication-type="other" xlink:type="simple">Chapin III, F.S. (1980) The Mineral Nutrition of Wild Plants. Annual Review of Ecology and Systematics, 11, 233-260.  
http://dx.doi.org/10.1146/annurev.es.11.110180.001313</mixed-citation></ref><ref id="scirp.53378-ref39"><label>39</label><mixed-citation publication-type="other" xlink:type="simple">Guo, J.Y., Yang, Y., Wang, G.X., Yang, L.D. and Sun, X.Y. (2010) Ecophysiological Responses of Abies fabri Seedlings to Drought Stress and Nitrogen Supply. Physiologia Plantarum, 139, 335-347.</mixed-citation></ref><ref id="scirp.53378-ref40"><label>40</label><mixed-citation publication-type="other" xlink:type="simple">Colombo, S.J., Glerum, C. and Webb, D.P. (1989) Winter Hardening in First-Year Black Spruce (Picea mariana) Seedlings. Physiologia Plantarum, 76, 1-9. http://dx.doi.org/10.1111/j.1399-3054.1989.tb05444.x</mixed-citation></ref><ref id="scirp.53378-ref41"><label>41</label><mixed-citation publication-type="other" xlink:type="simple">Odlum, K.D. and Colombo, S.J. (1989) The Influence of Night Temperature under Declining Photoperiod on Bud Initiation in Black Spruce Seedlings. Canadian Journal of Forest Research, 19, 274-275.  
http://dx.doi.org/10.1139/x89-039</mixed-citation></ref><ref id="scirp.53378-ref42"><label>42</label><mixed-citation publication-type="other" xlink:type="simple">Colombo, S.J. and Templeton, C.W.G. (2006) Bud and Crown Architecture of White Spruce and Black Spruce. Trees, 20, 633-641. http://dx.doi.org/10.1007/s00468-006-0078-y</mixed-citation></ref><ref id="scirp.53378-ref43"><label>43</label><mixed-citation publication-type="other" xlink:type="simple">Krause, G. and Weis, E. (1984) Chlorophyll Fluorescence as a Tool in Plant Physiology. Photosynthesis Research, 5, 139-157. http://dx.doi.org/10.1007/BF00028527</mixed-citation></ref><ref id="scirp.53378-ref44"><label>44</label><mixed-citation publication-type="other" xlink:type="simple">Krause, G.H., Somersalo, S., Osmond, C.B., Briantais, J.M. and Schreiber, U. (1989) Fluorescence as a Tool in Photosynthesis Research: Application in Studies of Photoinhibition, Cold Acclimation and Freezing Stress [and Discussion]. Philosophical Transactions of the Royal Society B: Biological Sciences, 323, 281-293.  
http://dx.doi.org/10.1098/rstb.1989.0010</mixed-citation></ref><ref id="scirp.53378-ref45"><label>45</label><mixed-citation publication-type="other" xlink:type="simple">Rikala, R. and Repo, T. (1997) The Effect of Late Summer Fertilization on the Frost Hardening of Second-Year Scots Pine Seedlings. New Forests, 14, 33-44. http://dx.doi.org/10.1023/A:1006505919556</mixed-citation></ref></ref-list></back></article>