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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Plant Sci.</journal-id>
<journal-title>Frontiers in Plant Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Plant Sci.</abbrev-journal-title>
<issn pub-type="epub">1664-462X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpls.2021.753151</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Plant Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Variation in Amygdalin Content in Kernels of Six Almond Species (<italic>Prunus</italic> spp. L.) Distributed in China</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Wang</surname> <given-names>Wei</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1239259/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Xiao</surname> <given-names>Xun-Ze</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Xu</surname> <given-names>Xin-Qiao</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Li</surname> <given-names>Zhen-Jian</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1294221/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Zhang</surname> <given-names>Jun-Ming</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Key Laboratory of Silviculture of the State Forestry Administration, The Institute of Forestry, The Chinese Academy of Forestry</institution>, <addr-line>Beijing</addr-line>, <country>China</country></aff>
<aff id="aff2"><sup>2</sup><institution>School of Life Sciences, Yulin University</institution>, <addr-line>Yulin</addr-line>, <country>China</country></aff>
<aff id="aff3"><sup>3</sup><institution>Department of Biology, Taiyuan Normal University</institution>, <addr-line>Taiyuan</addr-line>, <country>China</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Boris Rewald, University of Natural Resources and Life Sciences Vienna, Austria</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Akbar Karami, Shiraz University, Iran; Antonio Giovino, Council for Agricultural and Economics Research (CREA), Italy; Katherine D&#x2019;Amico-Willman, North Carolina State University, United States</p></fn>
<corresp id="c001">&#x002A;Correspondence: Wei Wang, <email>greatkinglys@163.com</email></corresp>
<fn fn-type="other" id="fn004"><p>This article was submitted to Functional Plant Ecology, a section of the journal Frontiers in Plant Science</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>28</day>
<month>01</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2021</year>
</pub-date>
<volume>12</volume>
<elocation-id>753151</elocation-id>
<history>
<date date-type="received">
<day>04</day>
<month>08</month>
<year>2021</year>
</date>
<date date-type="accepted">
<day>14</day>
<month>12</month>
<year>2021</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2022 Wang, Xiao, Xu, Li and Zhang.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Wang, Xiao, Xu, Li and Zhang</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>Amygdalin, a naturally occurring compound, is one of the main active ingredients of the Chinese raw bitter almond. The variation in amygdalin composition of seed kernels among the six almond species was determined, and relationships with geoenvironmental factors were analyzed. The amygdalin content exhibited great diversity, ranging from 0.0004 to 9.73 g/100 g. The highest level of amygdalin was detected in Tangut almond, with 5.45&#x2013;9.73 g/100 g. The other kernels showed a range from 3.14 to 6.80 g/100 g in wild almond and from 3.00 to 4.22 g/100 g in longstalk almond. Amygdalin in common almond was almost undetectable. Factor analysis showed that amygdalin content in <italic>Prunus</italic> spp. kernels increased with altitude and decreased with the degree of aspect. Many environmental factors were closely related to amygdalin content, including annual precipitation (Bio12), UV intensity, and topsoil base saturation (T_BS), which all had a significant effect on amygdalin content. The amygdalin content is closely related to rainfall indicators, especially annual precipitation (Bio12), with the highest factor analysis value (3.63). Water regulates amygdalin in diverse ways. Since amygdalin is water-soluble, water can reduce the inhibitory effect of amygdalin on germination and regulate the synthesis of amygdalin at the late stage of germination by activating the amygdalin synthesis genes <italic>CYP79D16</italic> and <italic>CYP71AN24</italic>. This study expands the understanding of amygdalin in almond resources and provides the direction for the regulation of amygdalin.</p>
</abstract>
<kwd-group>
<kwd>almond species</kwd>
<kwd>almond kernel</kwd>
<kwd>amygdalin</kwd>
<kwd>amygdalin diversity</kwd>
<kwd>amygdalin synthesis</kwd>
<kwd>environmental factor</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="1"/>
<equation-count count="3"/>
<ref-count count="26"/>
<page-count count="10"/>
<word-count count="5993"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>Amygdalin (D-mandelonitrile-&#x00DF;-D-gentiobioside), one of the main components of the kernel of Chinese almond fruit, has antioxidative, antibacterial, anti-inflammatory, and immunoregulatory activities (<xref ref-type="bibr" rid="B18">Shi et al., 2019</xref>). Cyanogenic glucoside amygdalin initially isolated from the seeds of bitter almonds (<italic>Prunus dulcis</italic> var. amara) is a major component of the kernel of <italic>Rosaceae</italic> plants. For a long time, the potential value of wild almond has been underestimated due to its toxic component, cyanogenic gluoside amygdalin, which affects its development and utilization. However, with the discovery of the nutritional value of wild almond and the potential for amygdalin to prevent and treat conditions such as migraine, hypertension, chronic inflammation, and other diseases, the content change rule of amygdalin and other nutrients or functional components, especially in response to the changing characteristics of environmental factors, has attracted increasing attention (<xref ref-type="bibr" rid="B1">Ayaz et al., 2020</xref>).</p>
<p>Almond can be divided into bitter, non-bitter, and sweet species. There are six almond species in China, and the common almond [<italic>Prunus dulcis</italic> (Mill.) D.A.Webb.] is the only species that is mainly distributed in southern Xinjiang Province. Moreover, there are five wild species including high-latitude species such as the wild almond (<italic>Prunus tenella</italic> Batsch), the desert-grown longstalk almond [<italic>Prunus pedunculata</italic> (Pall.) Maxim.], the south-to-north adapted flowering almond (<italic>Prunus triloba</italic> Lindl.), the high-elevation Tangut almond (<italic>Prunus tangutica</italic> (Batalin), and the northern mountainous-soil-grown Mongolic almond (<italic>Prunus mongolica</italic> Maxim.). These wild species of almonds are rich in amygdalin, providing a source for the precious material (<xref ref-type="bibr" rid="B23">Wang et al., 2018</xref>, <xref ref-type="bibr" rid="B24">2019</xref>, <xref ref-type="bibr" rid="B25">2020</xref>).</p>
<p>Ecogeographic factors are closely related to plant metabolism (<xref ref-type="bibr" rid="B16">Sampaio et al., 2016</xref>) and affect many metabolic pathways in almond, such as fatty acid composition (<xref ref-type="bibr" rid="B12">Nanos et al., 2002</xref>; <xref ref-type="bibr" rid="B4">Giovino et al., 2015</xref>) and tocopherol concentration (<xref ref-type="bibr" rid="B7">Kodad et al., 2011</xref>). Some correlations between ecogeographic factors (temperatures, precipitation, latitude, etc.) and cyanogenic glucoside have been illustrated in plants such as <italic>Trifolium repens</italic> (<xref ref-type="bibr" rid="B10">Majumdar et al., 2004</xref>). The amygdalin content varies widely in the <italic>Rosaceae</italic> family, which includes wild almond species. The difference is related to germplasm resources and environmental factors. However, the relationship between environmental factors and amygdalin remains unrevealed in almonds.</p>
<p>Amygdalin synthesis is closely related to the cytochrome P450 family and glycosyltransferase UGT family. The cytochrome P450 (CYP) enzymes <italic>PdCYP79D16</italic> and <italic>PdCYP71AN24</italic> catalyze the conversion of phenylalanine to mandelonitrile, <italic>PdUGT94AF3</italic> is an additional monoglucosyl transferase (UGT) catalyzing prunasin formation, and <italic>PdUGT94AF1</italic> and <italic>PdUGT94AF2</italic> are the two enzymes catalyzing amygdalin formation from prunasin (<xref ref-type="bibr" rid="B21">Thodberg et al., 2018</xref>). The transcription of <italic>PdCYP79D16</italic> and <italic>PdCYP71AN24</italic> is controlled by the basic helix-loop-helix transcription factor (<italic>bHLH2</italic>). A non-synonymous point mutation (Leu to Phe) in the dimerization domain of <italic>bHLH2</italic> prevents transcription of the two cytochrome P450 genes, resulting in the sweet kernel trait (<xref ref-type="bibr" rid="B17">S&#x00E1;nchez-P&#x00E9;rez et al., 2019</xref>).</p>
<p>In this study, the amygdalin content of ripe almond fruits from 29 regions (including both cultivated and wild varieties) in China was determined. The difference in amygdalin content in kernels was analyzed and evaluated. The main purpose of this study was to clarify the relationship among environmental parameters, genetic variation, and amygdalin content in almond germplasm resources. The results of this study will have a positive impact on the edible and medicinal value of wild almond resources and help to develop new varieties rich in amygdalin.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2.SS1">
<title>Plant Materials</title>
<p>From June to August 2018, kernels from six almond species were obtained from habitats in China according to different maturity periods (<xref ref-type="fig" rid="F1">Figure 1</xref>); including from ten regions in Shaanxi Province and Inner Mongolia Province (longstalk almond), one region in Otog Banner of Inner Mongolia Province (Mongolic almond), seven regions in Aba Prefecture, Sichuan Province (Tangut almond), six regions of Kashi region, Xinjiang Province (common almond), four regions in Altay region of Xinjiang Province (wild almond), and one region in Chengde City of Hebei Province (flowering almond) (<xref ref-type="supplementary-material" rid="TS1">Supplementary Table 1</xref>). Samples were collected from trees over 20 years old in each region. The degree of maturity was determined by the difficulty of peeling off the green skin and fruit stalk. All samples were dried in the shade and cryopreserved at -20&#x00B0;C until the experiment.</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>Geographic distribution of different sampled positions of <italic>Prunus</italic> spp. L.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g001.tif"/>
</fig>
</sec>
<sec id="S2.SS2">
<title>Extraction and Measurement of Amygdalin</title>
<p>Prior to chemical analyses, the nuts were shelled manually and screened to remove bad seeds. All kernel samples were triturated in liquid nitrogen. The extraction of amygdalin used methanol (20 ml) as the solute, as well as 0.2&#x2013;0.4 g of almond powder under an ultrasonic generator (500 W, 40 kHz) for 30 min. The supernatant was filtered through filter paper. Then, 1 ml was diluted with an equal volume of 20% methanol and filtered through a 0.22-&#x03BC;m microfiltration membrane for clarification.</p>
<p>High-performance liquid chromatography (HPLC) assays were carried out on a Waters 2650, 2487 UV detector, and a 4.6 &#x00D7; 250 mm C18 column (Waters Sunfire, MA, United States). The mobile phase used was CH<sub>3</sub>OH:H<sub>2</sub>O (20:80, v/v) under isocratic conditions at a flow rate of 1.0 ml/min. A 10-&#x03BC;l sample was injected for analysis. Detection was recorded at 210 nm. The amygdalin used as a standard was purchased from Sigma-Aldrich (MO, United States). The method produced a good separation chromatogram with excellent linearity (correlation <italic>r</italic><sup>2</sup> = 0.9999, <xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 1</xref>) between the peak area and the concentration of amygdalin.</p>
</sec>
<sec id="S2.SS3">
<title>Environmental Parameters</title>
<p>Geographical data, including longitude, latitude, and altitude, were gathered from habitats using GPS (GARMIN GPSMAP 63SC). Based on the digital elevation model (DEM) derived from SRTM 90M (Shuttle Radar Topographic Mission) data, topographic data, including slope (Slope) and aspect (Aspect), were extracted using ArcGIS 10.2 (version 10.2, ESRI, Redlands, CA, United States). Climate factor data, including 19 factors, such as the annual mean temperature (BIO1), temperature seasonality (BIO4), max temperature of warmest month (BIO5), mean temperature of wettest quarter (BIO8), mean temperature of driest quarter (BIO9), annual precipitation (BIO12), precipitation of wettest month (BIO13), and precipitation seasonality (BIO15) (Bio1-Bio19, more specific information can be found in <xref ref-type="table" rid="T1">Table 1</xref>), annual mean solar radiation (A_Srad), annual mean water vapor pressure (A_Vapr), and annual mean wind speed (A_Wind) were gathered from the world climate database<sup><xref ref-type="fn" rid="footnote1">1</xref></sup> using ArcGIS 10.2 with accurate locations to export climate data. Fifteen soil variables (T_BS, T_ESP, T_OC, T_PH_H2O, T_SAND, T_SILT, etc.) were from the Harmonized World Soil Database version 1.2<sup><xref ref-type="fn" rid="footnote2">2</xref></sup> and included 30 arc-second resolution rasters for topsoil organic carbon, pH, percent silt, and percent sand (<xref ref-type="bibr" rid="B3">Fischer et al., 2008</xref>). Global UV-B radiation data (UV-B 1-6) were from the gIUV database<sup><xref ref-type="fn" rid="footnote3">3</xref></sup> (<xref ref-type="bibr" rid="B11">Manceur et al., 2014</xref>). The above factors are shown in <xref ref-type="table" rid="T1">Table 1</xref>. In this study, forty-eight variables related to the distribution of six almond species were selected, as shown in <xref ref-type="supplementary-material" rid="TS1">Supplementary Table 1</xref>.</p>
<table-wrap position="float" id="T1">
<label>TABLE 1</label>
<caption><p>Statistical analysis of amygdalin and environmental factors.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Field</td>
<td valign="top" align="center">Description</td>
<td valign="top" align="center">Units</td>
<td valign="top" align="center">Range</td>
<td valign="top" align="center">Minimum</td>
<td valign="top" align="center">Maximum</td>
<td valign="top" align="center">Mean</td>
<td valign="top" align="center">SE</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Amygdalin</td>
<td valign="top" align="center">Amygdalin</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">9.73</td>
<td valign="top" align="center">0.0004</td>
<td valign="top" align="center">9.73</td>
<td valign="top" align="center">4.87</td>
<td valign="top" align="center">0.19</td>
</tr>
<tr>
<td valign="top" align="left">Altitude</td>
<td valign="top" align="center">Altitude</td>
<td valign="top" align="center">m</td>
<td valign="top" align="center">1899.00</td>
<td valign="top" align="center">900.00</td>
<td valign="top" align="center">2799.00</td>
<td valign="top" align="center">1960.37</td>
<td valign="top" align="center">46.42</td>
</tr>
<tr>
<td valign="top" align="left">Aspect</td>
<td valign="top" align="center">Aspect</td>
<td valign="top" align="center">Degree</td>
<td valign="top" align="center">349.47</td>
<td valign="top" align="center">0.40</td>
<td valign="top" align="center">349.87</td>
<td valign="top" align="center">187.78</td>
<td valign="top" align="center">7.54</td>
</tr>
<tr>
<td valign="top" align="left">Slope</td>
<td valign="top" align="center">Slope</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">78.56</td>
<td valign="top" align="center">0.97</td>
<td valign="top" align="center">79.53</td>
<td valign="top" align="center">56.38</td>
<td valign="top" align="center">2.10</td>
</tr>
<tr>
<td valign="top" align="left">A_Srad</td>
<td valign="top" align="center">Annual mean solar radiation</td>
<td valign="top" align="center">kJ/m<sup>2</sup>/day</td>
<td valign="top" align="center">4325.50</td>
<td valign="top" align="center">12412.92</td>
<td valign="top" align="center">16738.42</td>
<td valign="top" align="center">14392.47</td>
<td valign="top" align="center">145.45</td>
</tr>
<tr>
<td valign="top" align="left">A_Vapr</td>
<td valign="top" align="center">Annual mean water vapor pressure</td>
<td valign="top" align="center">kPa</td>
<td valign="top" align="center">0.45</td>
<td valign="top" align="center">0.47</td>
<td valign="top" align="center">0.92</td>
<td valign="top" align="center">0.69</td>
<td valign="top" align="center">0.01</td>
</tr>
<tr>
<td valign="top" align="left">A_Wind</td>
<td valign="top" align="center">Annual mean wind speed</td>
<td valign="top" align="center">m/s</td>
<td valign="top" align="center">2.63</td>
<td valign="top" align="center">1.38</td>
<td valign="top" align="center">4.01</td>
<td valign="top" align="center">2.50</td>
<td valign="top" align="center">0.06</td>
</tr>
<tr>
<td valign="top" align="left">T_BS</td>
<td valign="top" align="center">Topsoil base saturation</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">8.00</td>
<td valign="top" align="center">92.00</td>
<td valign="top" align="center">100.00</td>
<td valign="top" align="center">99.79</td>
<td valign="top" align="center">0.08</td>
</tr>
<tr>
<td valign="top" align="left">T_BULK_DEN</td>
<td valign="top" align="center">Topsoil reference bulk density</td>
<td valign="top" align="center">kg/dm<sup>3</sup></td>
<td valign="top" align="center">0.30</td>
<td valign="top" align="center">1.20</td>
<td valign="top" align="center">1.50</td>
<td valign="top" align="center">1.38</td>
<td valign="top" align="center">0.01</td>
</tr>
<tr>
<td valign="top" align="left">T_CACO3</td>
<td valign="top" align="center">Topsoil calcium carbonate</td>
<td valign="top" align="center">% weight</td>
<td valign="top" align="center">9.00</td>
<td valign="top" align="center">0.00</td>
<td valign="top" align="center">9.00</td>
<td valign="top" align="center">6.02</td>
<td valign="top" align="center">0.19</td>
</tr>
<tr>
<td valign="top" align="left">T_CASO4</td>
<td valign="top" align="center">Topsoil gypsum</td>
<td valign="top" align="center">% weight</td>
<td valign="top" align="center">0.10</td>
<td valign="top" align="center">0.00</td>
<td valign="top" align="center">0.10</td>
<td valign="top" align="center">0.00</td>
<td valign="top" align="center">0.00</td>
</tr>
<tr>
<td valign="top" align="left">T_CEC_CLAY</td>
<td valign="top" align="center">Topsoil CEC (clay)</td>
<td valign="top" align="center">cmol/kg</td>
<td valign="top" align="center">34.00</td>
<td valign="top" align="center">46.00</td>
<td valign="top" align="center">80.00</td>
<td valign="top" align="center">58.55</td>
<td valign="top" align="center">0.91</td>
</tr>
<tr>
<td valign="top" align="left">T_CEC_SOIL</td>
<td valign="top" align="center">Topsoil CEC (soil)</td>
<td valign="top" align="center">cmol/kg</td>
<td valign="top" align="center">26.00</td>
<td valign="top" align="center">1.00</td>
<td valign="top" align="center">27.00</td>
<td valign="top" align="center">16.13</td>
<td valign="top" align="center">0.57</td>
</tr>
<tr>
<td valign="top" align="left">T_CLAY</td>
<td valign="top" align="center">Topsoil clay fraction</td>
<td valign="top" align="center">% wt.</td>
<td valign="top" align="center">22.00</td>
<td valign="top" align="center">4.00</td>
<td valign="top" align="center">26.00</td>
<td valign="top" align="center">17.74</td>
<td valign="top" align="center">0.49</td>
</tr>
<tr>
<td valign="top" align="left">T_ECE</td>
<td valign="top" align="center">Topsoil salinity (Elco)</td>
<td valign="top" align="center">dS/m</td>
<td valign="top" align="center">0.60</td>
<td valign="top" align="center">0.10</td>
<td valign="top" align="center">0.70</td>
<td valign="top" align="center">0.27</td>
<td valign="top" align="center">0.01</td>
</tr>
<tr>
<td valign="top" align="left">T_ESP</td>
<td valign="top" align="center">Topsoil sodicity (ESP)</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">6.00</td>
<td valign="top" align="center">0.00</td>
<td valign="top" align="center">6.00</td>
<td valign="top" align="center">1.85</td>
<td valign="top" align="center">0.10</td>
</tr>
<tr>
<td valign="top" align="left">T_GRAVEL</td>
<td valign="top" align="center">Topsoil Gravel Content</td>
<td valign="top" align="center">%vol.</td>
<td valign="top" align="center">13.00</td>
<td valign="top" align="center">3.00</td>
<td valign="top" align="center">16.00</td>
<td valign="top" align="center">8.16</td>
<td valign="top" align="center">0.33</td>
</tr>
<tr>
<td valign="top" align="left">T_OC</td>
<td valign="top" align="center">Topsoil organic carbon</td>
<td valign="top" align="center">% weight</td>
<td valign="top" align="center">2.01</td>
<td valign="top" align="center">0.40</td>
<td valign="top" align="center">2.41</td>
<td valign="top" align="center">0.97</td>
<td valign="top" align="center">0.05</td>
</tr>
<tr>
<td valign="top" align="left">T_PH_H2O</td>
<td valign="top" align="center">Topsoil pH (H2O)</td>
<td/>
<td valign="top" align="center">2.70</td>
<td valign="top" align="center">5.70</td>
<td valign="top" align="center">8.40</td>
<td valign="top" align="center">7.75</td>
<td valign="top" align="center">0.05</td>
</tr>
<tr>
<td valign="top" align="left">T_REF_BULK</td>
<td valign="top" align="center">Topsoil reference bulk density</td>
<td valign="top" align="center">kg/dm<sup>3</sup></td>
<td valign="top" align="center">0.39</td>
<td valign="top" align="center">1.35</td>
<td valign="top" align="center">1.74</td>
<td valign="top" align="center">1.45</td>
<td valign="top" align="center">0.01</td>
</tr>
<tr>
<td valign="top" align="left">T_SAND</td>
<td valign="top" align="center">Topsoil Sand Fraction</td>
<td valign="top" align="center">% wt.</td>
<td valign="top" align="center">66.00</td>
<td valign="top" align="center">24.00</td>
<td valign="top" align="center">90.00</td>
<td valign="top" align="center">45.90</td>
<td valign="top" align="center">1.75</td>
</tr>
<tr>
<td valign="top" align="left">T_SILT</td>
<td valign="top" align="center">Topsoil silt fraction</td>
<td valign="top" align="center">% wt.</td>
<td valign="top" align="center">48.00</td>
<td valign="top" align="center">6.00</td>
<td valign="top" align="center">54.00</td>
<td valign="top" align="center">36.36</td>
<td valign="top" align="center">1.28</td>
</tr>
<tr>
<td valign="top" align="left">Bio1</td>
<td valign="top" align="center">Annual mean temperature</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">11.10</td>
<td valign="top" align="center">1.45</td>
<td valign="top" align="center">12.55</td>
<td valign="top" align="center">6.12</td>
<td valign="top" align="center">0.19</td>
</tr>
<tr>
<td valign="top" align="left">Bio2</td>
<td valign="top" align="center">Mean diurnal range [mean of monthly (max temp&#x2013;min temp)]</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">4.03</td>
<td valign="top" align="center">10.34</td>
<td valign="top" align="center">14.38</td>
<td valign="top" align="center">12.07</td>
<td valign="top" align="center">0.11</td>
</tr>
<tr>
<td valign="top" align="left">Bio3</td>
<td valign="top" align="center">Isothermality (BIO2/BIO7) (&#x002A; 100)</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">13.63</td>
<td valign="top" align="center">23.53</td>
<td valign="top" align="center">37.16</td>
<td valign="top" align="center">32.31</td>
<td valign="top" align="center">0.34</td>
</tr>
<tr>
<td valign="top" align="left">Bio4</td>
<td valign="top" align="center">Temperature seasonality (standard deviation &#x002A;100)</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">766.24</td>
<td valign="top" align="center">662.27</td>
<td valign="top" align="center">1428.51</td>
<td valign="top" align="center">947.83</td>
<td valign="top" align="center">22.78</td>
</tr>
<tr>
<td valign="top" align="left">Bio5</td>
<td valign="top" align="center">Max temperature of warmest month</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">13.00</td>
<td valign="top" align="center">19.80</td>
<td valign="top" align="center">32.80</td>
<td valign="top" align="center">24.19</td>
<td valign="top" align="center">0.27</td>
</tr>
<tr>
<td valign="top" align="left">Bio6</td>
<td valign="top" align="center">Min temperature of coldest month</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">18.30</td>
<td valign="top" align="center">-24.80</td>
<td valign="top" align="center">-6.50</td>
<td valign="top" align="center">-14.12</td>
<td valign="top" align="center">0.48</td>
</tr>
<tr>
<td valign="top" align="left">Bio7</td>
<td valign="top" align="center">Temperature annual range (BIO5-BIO6)</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">20.70</td>
<td valign="top" align="center">29.90</td>
<td valign="top" align="center">50.60</td>
<td valign="top" align="center">38.31</td>
<td valign="top" align="center">0.68</td>
</tr>
<tr>
<td valign="top" align="left">Bio8</td>
<td valign="top" align="center">Mean temperature of wettest quarter</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">12.78</td>
<td valign="top" align="center">12.07</td>
<td valign="top" align="center">24.85</td>
<td valign="top" align="center">15.93</td>
<td valign="top" align="center">0.21</td>
</tr>
<tr>
<td valign="top" align="left">Bio9</td>
<td valign="top" align="center">Mean temperature of driest quarter</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">22.10</td>
<td valign="top" align="center">-17.12</td>
<td valign="top" align="center">4.98</td>
<td valign="top" align="center">-5.86</td>
<td valign="top" align="center">0.40</td>
</tr>
<tr>
<td valign="top" align="left">Bio10</td>
<td valign="top" align="center">Mean temperature of warmest quarter</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">11.30</td>
<td valign="top" align="center">13.55</td>
<td valign="top" align="center">24.85</td>
<td valign="top" align="center">17.24</td>
<td valign="top" align="center">0.22</td>
</tr>
<tr>
<td valign="top" align="left">Bio11</td>
<td valign="top" align="center">Mean temperature of coldest quarter</td>
<td valign="top" align="center">&#x00B0;C</td>
<td valign="top" align="center">17.33</td>
<td valign="top" align="center">-17.12</td>
<td valign="top" align="center">0.22</td>
<td valign="top" align="center">-6.22</td>
<td valign="top" align="center">0.43</td>
</tr>
<tr>
<td valign="top" align="left">Bio12</td>
<td valign="top" align="center">Annual precipitation</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">689.00</td>
<td valign="top" align="center">38.00</td>
<td valign="top" align="center">727.00</td>
<td valign="top" align="center">513.33</td>
<td valign="top" align="center">15.71</td>
</tr>
<tr>
<td valign="top" align="left">Bio13</td>
<td valign="top" align="center">Precipitation of wettest month</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">121.00</td>
<td valign="top" align="center">8.00</td>
<td valign="top" align="center">129.00</td>
<td valign="top" align="center">102.83</td>
<td valign="top" align="center">1.62</td>
</tr>
<tr>
<td valign="top" align="left">Bio14</td>
<td valign="top" align="center">Precipitation of driest month</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">10.00</td>
<td valign="top" align="center">0.00</td>
<td valign="top" align="center">10.00</td>
<td valign="top" align="center">2.71</td>
<td valign="top" align="center">0.12</td>
</tr>
<tr>
<td valign="top" align="left">Bio15</td>
<td valign="top" align="center">Precipitation seasonality (coefficient of variation)</td>
<td valign="top" align="center">%</td>
<td valign="top" align="center">71.93</td>
<td valign="top" align="center">40.26</td>
<td valign="top" align="center">112.19</td>
<td valign="top" align="center">91.03</td>
<td valign="top" align="center">1.38</td>
</tr>
<tr>
<td valign="top" align="left">Bio16</td>
<td valign="top" align="center">Precipitation of wettest quarter</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">324.00</td>
<td valign="top" align="center">17.00</td>
<td valign="top" align="center">341.00</td>
<td valign="top" align="center">270.45</td>
<td valign="top" align="center">5.63</td>
</tr>
<tr>
<td valign="top" align="left">Bio17</td>
<td valign="top" align="center">Precipitation of driest quarter</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">31.00</td>
<td valign="top" align="center">2.00</td>
<td valign="top" align="center">33.00</td>
<td valign="top" align="center">12.48</td>
<td valign="top" align="center">0.37</td>
</tr>
<tr>
<td valign="top" align="left">Bio18</td>
<td valign="top" align="center">Precipitation of warmest quarter</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">324.00</td>
<td valign="top" align="center">17.00</td>
<td valign="top" align="center">341.00</td>
<td valign="top" align="center">263.97</td>
<td valign="top" align="center">5.55</td>
</tr>
<tr>
<td valign="top" align="left">Bio19</td>
<td valign="top" align="center">Precipitation of coldest quarter</td>
<td valign="top" align="center">mm</td>
<td valign="top" align="center">40.00</td>
<td valign="top" align="center">3.00</td>
<td valign="top" align="center">43.00</td>
<td valign="top" align="center">12.61</td>
<td valign="top" align="center">0.42</td>
</tr>
<tr>
<td valign="top" align="left">UVB1</td>
<td valign="top" align="center">Annual mean UV-B</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">2685.33</td>
<td valign="top" align="center">2204.83</td>
<td valign="top" align="center">4890.16</td>
<td valign="top" align="center">3530.66</td>
<td valign="top" align="center">75.34</td>
</tr>
<tr>
<td valign="top" align="left">UVB2</td>
<td valign="top" align="center">UV-B seasonality</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">118944.00</td>
<td valign="top" align="center">114355.00</td>
<td valign="top" align="center">233299.00</td>
<td valign="top" align="center">182413.92</td>
<td valign="top" align="center">2841.44</td>
</tr>
<tr>
<td valign="top" align="left">UVB3</td>
<td valign="top" align="center">Mean UV-B of highest_month</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">3433.31</td>
<td valign="top" align="center">4363.33</td>
<td valign="top" align="center">7796.64</td>
<td valign="top" align="center">5875.74</td>
<td valign="top" align="center">101.23</td>
</tr>
<tr>
<td valign="top" align="left">UVB4</td>
<td valign="top" align="center">Mean UV-B of lowest month</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">1426.32</td>
<td valign="top" align="center">296.98</td>
<td valign="top" align="center">1723.30</td>
<td valign="top" align="center">1126.55</td>
<td valign="top" align="center">40.99</td>
</tr>
<tr>
<td valign="top" align="left">UVB5</td>
<td valign="top" align="center">UV-B radiation of highest quarter</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">10102.50</td>
<td valign="top" align="center">12047.50</td>
<td valign="top" align="center">22150.00</td>
<td valign="top" align="center">16519.49</td>
<td valign="top" align="center">301.38</td>
</tr>
<tr>
<td valign="top" align="left">UVB6</td>
<td valign="top" align="center">Sum of UV-B radiation of lowest quarter</td>
<td valign="top" align="center">J/m<sup>2</sup>/day</td>
<td valign="top" align="center">5867.20</td>
<td valign="top" align="center">2015.48</td>
<td valign="top" align="center">7882.68</td>
<td valign="top" align="center">5351.33</td>
<td valign="top" align="center">153.20</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="S2.SS4">
<title>Water Treatment</title>
<p>The seeds of longstalk almonds were soaked in twice their volume of pure water for 7 days, and the water was changed every day. Then, the soaked seeds were treated with sterilized river sand for 9 days at 25&#x00B0;C. Some shelled kernels (2.0 g) were randomly selected to test the moisture content after each sampling. The rest of the kernels were ground in a mortar under liquid nitrogen. Then, the crushed samples were wrapped with aluminum foil paper and stored at -80&#x00B0;C.</p>
</sec>
<sec id="S2.SS5">
<title>Moisture Detection of Shelled Kernel</title>
<p>The seed kernel samples were weighed in a glass dish and then, dried in an oven at 105&#x00B0;C for 1 h. After taking the samples out, the dry weight was measured. Each sample was measured three times, and the average value was obtained.</p>
</sec>
<sec id="S2.SS6">
<title>RNA Isolation and Gene Expression Analysis</title>
<p>The primers used in this study refer to six amygdalin synthesis gene primers reported by <xref ref-type="bibr" rid="B21">Thodberg et al. (2018)</xref>. The primers were synthesized by Shenggong Bioengineering (Shanghai) Co., Ltd. <italic>UBQ10</italic> was the internal reference gene. All primers were purified by HPLC (<xref ref-type="supplementary-material" rid="TS2">Supplementary Table 2</xref>).</p>
<p>For RNA extraction, 0.2 g of crushed samples were collected from the corresponding plants, and RNAprep pure plant kits were used in strict accordance with the requirements of the manufacturer. The determination of RNA content and quality was mainly performed using a NanoDrop 2000 (Thermo Fisher Scientific, Waltham, MA, United States). cDNA was synthesized by using a reverse transcription kit according to the instructions (PrimeScript&#x2122;RT Master Mix, TaKaRa Biotechnology Co., Ltd. Dalian, China). RT-PCR experiments were conducted using previously reported methods (real-time quantitative PCR was performed using the KAPA SYBR FAST qPCR Master Mix kit). PCRs were carried out using high-fidelity Phusion DNA polymerase. The primer sequences of the test genes were consistent with previous studies (<xref ref-type="bibr" rid="B21">Thodberg et al., 2018</xref>). The cycle threshold (CT) 2<sup>&#x2013;&#x0394;&#x0394;CT</sup> method was used to measure the relative expression of the tested gene. All the samples were analyzed in triplicate.</p>
<p>Parameter settings for real-time fluorescence quantitative PCR are as follows:</p>
<list list-type="simple">
<list-item><label>1.</label><p>Predenaturation: temperature 95&#x00B0;C, retention time 30 s (temperature rising and falling speed: 4.4&#x00B0;C/s), 1 cycle;</p></list-item>
<list-item><label>2.</label><p>Amplification: temperature 95&#x00B0;C, retention time 5 s (temperature rise and fall rate: 4.4&#x00B0;C/s), temperature 60&#x00B0;C, retention time 30 s (temperature rise and fall speed: 2.2&#x00B0;C/s), 40 cycles;</p></list-item>
<list-item><label>3.</label><p>Melting: temperature 95&#x00B0;C, retention time 5 s (temperature rise and fall speed: 4.4&#x00B0;C/s), temperature 60&#x00B0;C, retention time 1 min (temperature rise and fall speed: 2.2&#x00B0;C/s), temperature 95&#x00B0;C (temperature rise and fall speed: 4.4&#x00B0;C/s), 1 cycle;</p></list-item>
<list-item><label>4.</label><p>Cooling: temperature 50&#x00B0;C (temperature rise and fall speed: 2.2&#x00B0;C/s), 1 cycle.</p></list-item>
</list>
<p>Data processing:</p>
<p>The CT value data were analyzed by relative quantitative analysis (<italic>UBQ10</italic> as the internal reference gene) and sorted into 2<sup>&#x2013;&#x0394;&#x0394;<italic>CT</italic></sup> mean values, which were positively correlated with the expression level, as shown in Formula (1).</p>
<disp-formula id="S2.Ex1"><label>(1)</label><mml:math id="M1" display="block"><mml:mrow><mml:mpadded width="+3.3pt"><mml:mi>Relative</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>expression</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>of</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>the</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>target</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>gene</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>in</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>each</mml:mi></mml:mpadded><mml:mo>&#x2062;</mml:mo><mml:mi>sample</mml:mi></mml:mrow><mml:mrow><mml:mi mathvariant="normal"> </mml:mi><mml:mo rspace="5.8pt">=</mml:mo><mml:mn>2</mml:mn><mml:mmultiscripts><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mi>mean</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mprescripts/><mml:none/><mml:mo>-</mml:mo><mml:none/><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:none/><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:none/><mml:mrow><mml:mi>C</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mi>T</mml:mi></mml:mrow></mml:mmultiscripts></mml:mrow></mml:math></disp-formula>
<disp-formula id="S2.Ex2"><mml:math id="M2" display="block"><mml:mrow><mml:mrow><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mpadded width="+3.3pt"><mml:mi>CT</mml:mi></mml:mpadded></mml:mrow><mml:mo rspace="5.8pt">=</mml:mo><mml:mrow><mml:mrow><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mi>CT</mml:mi></mml:mrow><mml:mo>-</mml:mo><mml:mrow><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mi>CT</mml:mi><mml:mo>&#x2062;</mml:mo><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mi>mean</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mrow></mml:mrow></mml:mrow></mml:math></disp-formula>
<disp-formula id="S2.Ex3"><mml:math id="M3" display="block"><mml:mrow><mml:mi mathvariant="normal">&#x0394;</mml:mi><mml:mpadded width="+3.3pt"><mml:mi>CT</mml:mi></mml:mpadded><mml:mo rspace="5.8pt">=</mml:mo><mml:mi>CT</mml:mi><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mi>target</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow><mml:mo>-</mml:mo><mml:mi>CT</mml:mi><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mi>ref</mml:mi><mml:mo>.</mml:mo><mml:mi>mean</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:mrow></mml:math></disp-formula>
<p>Symbols of formulas:</p>
<p>CT (target)&#x2014;Cycle number of the target gene in the sample;</p>
<p>CT (ref.mean)&#x2014;The average number of internal reference gene cycles in three replicates;</p>
<p>&#x0394;CT (mean)&#x2014;Average &#x0394;CT values of three repeats of the target gene in the sample.</p>
</sec>
<sec id="S2.SS7">
<title>Statistical Analyses</title>
<p>Interspecific and intraspecific data on amygdalin content and environmental factors were integrated. The Pearson correlation analysis between amygdalin and other environmental data and the CABFAC factor analysis of environmental factors on amygdalin content were carried out using Paleontological Statistics (PAST) software program Version 3.14 (<xref ref-type="bibr" rid="B6">Hammer et al., 2001</xref>). Figures were drawn using Sigmaplot 14 (version 14, Systat Software Inc., Chicago, IL, United States) and MATLAB R2014a (version R2014a, MathWorks, Natick, MA, United States), and tables were created in Excel 2010.</p>
</sec>
</sec>
<sec id="S3" sec-type="results|discussion">
<title>Results and Discussion</title>
<sec id="S3.SS1">
<title>Sample Collection</title>
<p>Wild almond species are widely distributed in the world showing a large span in both latitude and longitude. In this study, 145 wild almond germplasm resources were collected in the natural distribution area of wild almond, and 6 almond cultivars were collected in the main cultivation area of almond (<xref ref-type="supplementary-material" rid="TS1">Supplementary Table 1</xref>). The span of the sample collection area covers the natural distribution areas of six almond species in mainland China, spanning the longitude range of 38&#x00B0;46&#x2032;12&#x2033; and the latitude range of 16&#x00B0;2&#x2032;33&#x2033; (<xref ref-type="fig" rid="F1">Figure 1</xref>), with an altitude span of 1,960.37 m (<xref ref-type="fig" rid="F1">Figure 1</xref> and <xref ref-type="table" rid="T1">Table 1</xref>).</p>
</sec>
<sec id="S3.SS2">
<title>Variation of Amygdalin Content in Almond Germplasm</title>
<p>The variation range of amygdalin contents in six species seeds is given in <xref ref-type="fig" rid="F2">Figure 2</xref>. Among the species analyzed, amygdalin was most abundant in Tangut almond, with the highest amygdalin content (9.73 g/100 g) and the highest average (7.78 g/100 g). The amygdalin content in wild almond was highly related to the germplasm, with an average of 3.14&#x2013;6.80 g/100 g. Longstalk almond was the most sampled, and its amygdalin content varied from 3.00 to 4.22 g/100 g. The contents of flowering almond and Mongolic almond seeds were slightly lower at 1.41&#x2013;2.65 and 1.55&#x2013;3.22 g/100 g, respectively. Nearly no amygdalin was found in common almond. <xref ref-type="fig" rid="F2">Figure 2</xref> shows that the amygdalin content of Tangut almond and wild almond fluctuates greatly. In addition, the median amount of amygdalin in Tangut almond (8.47 g/100 g) was much higher than the average, while the median amount of amygdalin in other almond resources was close to the average. These results may stem from genotype adaptation to the environment.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Range of amygdalin contents in six almond species in China. Medium dashed lines show each mean value, and solid lines show each median.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g002.tif"/>
</fig>
<p>Among the other species studied, Tangut almond and wild almond represent the highest levels of amygdalin, which are extremely high compared with other species in <italic>Rosaceae</italic> as well. Amygdalin contents similar to Tangut almond have been reported in the bitter apricot (<italic>Prunus armeniaca</italic> L.) cultivars &#x201C;Palstein,&#x201D; &#x201C;Canino,&#x201D; and &#x201C;Tirynthos&#x201D; (<xref ref-type="bibr" rid="B5">G&#x00F3;mez et al., 1998</xref>), and it was also reported that some Turkish bitter apricot species (&#x201C;Paviot,&#x201D; &#x201C;Karacabey,&#x201D; and &#x201C;Alyanak&#x201D;) (<xref ref-type="bibr" rid="B26">Yildirim and Askin, 2010</xref>) have approximately the same content as wild almond. Longstalk almond represents the middle level of amygdalin among the six species, with a range from 3.00 to 4.22 g/100 g (<xref ref-type="bibr" rid="B8">Lee et al., 2013</xref>). Mongolic almond and flowering almond are considered to have low levels, which is similar to the slightly bitter almond with a reported concentration of 2.25 g/100 g (<xref ref-type="bibr" rid="B26">Yildirim and Askin, 2010</xref>). According to the Chinese pharmacopeia, the amygdalin content of almond kernels should be more than 3.0 g/100 g. Therefore, longstalk almond, Tangut almond, and wild almond are suitable as raw materials for traditional Chinese medicine (<xref ref-type="bibr" rid="B2">Chinese-pharmacopoeia-commission, 2015</xref>).</p>
<p>Amygdalin content has a significant variation among almond species. Cyanide such as amygdalin concentration in plants is highly related to environmental factors (<xref ref-type="bibr" rid="B14">Pederson et al., 1996</xref>; <xref ref-type="bibr" rid="B13">Nied&#x017A;wied&#x017A;-Siegie&#x0144; and Gierasimiuk, 2001</xref>). Considering the disparate amygdalin contents and habitat range among different almond species, it is plausible to consider that location and climate factors have an effect on amygdalin content.</p>
</sec>
<sec id="S3.SS3">
<title>Contribution of Ecogeographic Variables to Amygdalin Contents</title>
<p>Although the exact reasons for the high amygdalin content in the kernels of wild almond have not been elucidated, it has been speculated that the unique geographical environments (longitude and latitude, altitude, aspect, slope, and corresponding climate change) and genomic differences could greatly influence the biosynthesis and accumulation of amygdalin. Therefore, this study first explores the correlation between amygdalin content and ecogeographic variables (<xref ref-type="fig" rid="F3">Figure 3</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Factor analysis scores of amygdalin content in five topographic datasets (longitude, latitude, altitude, slope, and aspect) of six almond species <bold>(A)</bold>; amygdalin content in different longitudes, latitudes <bold>(B)</bold>, and altitudes <bold>(C)</bold>; scatter plot of amygdalin content in different aspects <bold>(D)</bold> and slopes <bold>(E)</bold>.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g003.tif"/>
</fig>
<p>Factor analysis showed that amygdalin content in <italic>Prunus</italic> spp. kernels increased with altitude (<xref ref-type="fig" rid="F3">Figures 3A,C</xref> and <xref ref-type="supplementary-material" rid="TS3">Supplementary Table 3</xref>), decreased with the degree of aspect (<xref ref-type="fig" rid="F3">Figures 3A,D</xref> and <xref ref-type="supplementary-material" rid="TS3">Supplementary Table 3</xref>), and had less relationship with longitude, latitude (<xref ref-type="fig" rid="F3">Figures 3A,B</xref> and <xref ref-type="supplementary-material" rid="TS3">Supplementary Table 3</xref>), and slope (<xref ref-type="fig" rid="F3">Figures 3A,E</xref> and <xref ref-type="supplementary-material" rid="TS3">Supplementary Table 3</xref>). The elevation of altitude is often accompanied by an increase in UV intensity, a decrease in temperature, and an increase in illumination hours. These changes in the external environment may be the main reason for the increase in secondary metabolites including amygdalin (<xref ref-type="bibr" rid="B9">Liu et al., 2020</xref>). With increasing altitude, the amygdalin content increases, so this may be one of the characteristics of almonds adapting to the harsh features of high-altitude climates, including high UV radiation. As shown in <xref ref-type="fig" rid="F3">Figure 3D</xref>, the distribution of almond resources is mostly concentrated on sunny and partial sunny slopes with an aspect of 90&#x2013;270&#x00B0;, indicating that almond resources are photophilous plants. The correlation between geographical factors (such as altitude, slope, and aspect) and amygdalin may be affected by the difference in light and UV light.</p>
</sec>
<sec id="S3.SS4">
<title>Contribution of Climate Variables to Amygdalin Contents</title>
<p>Different regions of almond habitats bring diverse environmental factors, mainly changing precipitation and temperature. In this study, common almond [<italic>Prunus dulcis</italic> (Mill.) D.A.Webb.] is the only species mainly distributed in southern Xinjiang Province; wild almond (<italic>Prunus tenella</italic> Batsch) is distributed in the high latitudes of northern Xinjiang Province; and longstalk almond [<italic>Prunus pedunculata</italic> (Pall.) Maxim.] is distributed in deserts and rocky mountainous areas such as Shaanxi and Inner Mongolia. In addition, there are south-to-north-adapted flowering almond (<italic>Prunus triloba</italic> Lindl.), high-elevation Tangut almond (<italic>Prunus tangutica</italic> (Batalin), and northern mountainous-soil-grown Mongolic almond (<italic>Prunus mongolica</italic> Maxim.) (<xref ref-type="fig" rid="F1">Figure 1</xref>). Among the sample collection regions, total annual precipitation ranges from 38 to 727 mm and the annual average temperature ranges from 1.45 to 12.55&#x00B0;C. The highest precipitation was found in Tangut almond habitat, which receives 610&#x2013;727 mm. The second was the flowering almond habitat with about 476 mm. Precipitation of longstalk almond, Mongolic almond, and wild almond habitats was between 100 and 400 mm. The lowest was observed in the common almond habitat, with 38&#x2013;85 mm. Conversely, the annual average temperature in the common almond habitat was the highest: about 12.55&#x00B0;C. The habitats of other species show the same temperature span of 1.45&#x2013;10.02&#x00B0;C (<xref ref-type="table" rid="T1">Table 1</xref>).</p>
<p>The factor analysis function of PAST3 software was used to analyze the contribution of 19 temperature and rainfall-related data to amygdalin content. The results showed that among the temperature-related factors (Bio1&#x2013;Bio11), only the factor analysis score of temperature seasonality (Bio4) exceeded 0.5 (<xref ref-type="fig" rid="F4">Figures 4A,B</xref> and <xref ref-type="supplementary-material" rid="TS4">Supplementary Table 4</xref>). Other temperature indexes had less effect on amygdalin content. However, amygdalin content was closely related to rainfall indicators, especially annual precipitation (Bio12). The factor analysis value was the highest for annual precipitation (3.63), followed by 1.57 and 1.54 for the precipitation of the wettest quarter (Bio16) and the precipitation of the warmest quarter (Bio18). Both Bio16 and Bio18 contributed more than 1.5 to the amygdalin content (<xref ref-type="fig" rid="F4">Figure 4A</xref>). The chemical composition of plant seeds is closely related to rainfall, irrigation, and drought. <xref ref-type="bibr" rid="B20">Tangolar et al. (2019)</xref> showed that the phytochemical contents of grape seeds changed according to irrigation levels. There was a significant negative correlation between soybean seed oil and rainfall (<xref ref-type="bibr" rid="B19">Solanki et al., 2007</xref>). Rainfall may further affect the chemical composition of plant seeds by changing the water content in the soil and atmosphere. However, how the amygdalin content changes in almond kernels corresponding to rainfall needs further study.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Factor analysis scores of amygdalin content in 19 climate factor datasets (Bio1&#x2013;Bio19) of six almond varieties <bold>(A)</bold>. Correlation analysis between amygdalin content and precipitation from January to December <bold>(B)</bold>. The correlation coefficients ranged from 1 (blue, positive) to -1 (red, negative).</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g004.tif"/>
</fig>
</sec>
<sec id="S3.SS5">
<title>Correlation Between Amygdalin Contents and Other Environmental Indicators</title>
<p>The correlation between amygdalin and other environmental data was also analyzed using PAST3 software. The results showed that amygdalin was positively correlated with the annual mean wind speed (A_Wind), was negatively correlated with the annual mean solar radiation (A_Srad), and had a low correlation coefficient with the annual mean water vapor pressure (A_Vapr) (<xref ref-type="fig" rid="F5">Figure 5A</xref> and <xref ref-type="supplementary-material" rid="TS5">Supplementary Table 5</xref>). Almond species are light-preferring plants, but an increase in light radiation beyond a certain range is not conducive to the synthesis of amygdalin, while an increase in wind speed can promote amygdalin synthesis. As shown in <xref ref-type="fig" rid="F5">Figure 5B</xref> and <xref ref-type="supplementary-material" rid="TS6">Supplementary Table 6</xref>, the amygdalin content was positively correlated with the six UV intensity indices, which indicated that the amygdalin content was closely related to the intensity of UV radiation. UV radiation is a small fraction of the solar spectrum which acts as a key environmental modulator of plant function, affecting metabolic regulation and growth (<xref ref-type="bibr" rid="B22">Wang et al., 2010</xref>; <xref ref-type="bibr" rid="B15">Reyes et al., 2020</xref>). Therefore, the increase of amygdalin content with elevation may be due to the change of UV intensity. The highest positive correlation coefficient was of amygdalin and the topsoil sodicity (T_ESP) with 0.75, while the lowest negative coefficient was the topsoil base saturation (T_BS) with -0.65 (<xref ref-type="supplementary-material" rid="TS7">Supplementary Table 7</xref>). The correlation coefficients of other soil indexes were generally low (<xref ref-type="fig" rid="F5">Figure 5C</xref> and <xref ref-type="supplementary-material" rid="TS7">Supplementary Table 7</xref>). There was a positive correlation between the topsoil sodicity and amygdalin, indicating that increased soil salinity was beneficial to amygdalin synthesis.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Correlation coefficient between amygdalin content and 3 annual climate factor datasets (A_Srad, annual mean solar radiation; A_Vapr, annual mean water vapor pressure; A_Wind, annual mean wind speed). <bold>(A)</bold> Correlation coefficient between amygdalin content and six UV-B radiation datasets. <bold>(B)</bold> Correlation coefficient between 15 soil variables and amygdalin content. <bold>(C)</bold> The correlation coefficients ranged from 1 (blue, positive) to -1 (red, negative).</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g005.tif"/>
</fig>
</sec>
<sec id="S3.SS6">
<title>Effect of Water on Amygdalin Content of the Wild Almond Kernel</title>
<p>The indices related to water and the factors affecting water, such as the annual precipitation (Bio12) and the annual mean solar radiation (A_Srad), have positive effects on amygdalin content. Therefore, we studied the effect of water treatment on amygdalin content in kernels. During the seed germination promoted by water immersion, the kernel water content continued to increase. There was a small peak on the 7th day and the largest peak on the 13th day (<xref ref-type="fig" rid="F6">Figure 6A</xref>). The amygdalin content decreased in the early stage, but increased after the 6th day and reached a peak on the 13th day (<xref ref-type="fig" rid="F6">Figure 6B</xref>). The P450 gene families <italic>CYP79D16</italic> and <italic>CYP71AN24</italic> showed similar expression patterns. The expression level was not high before the 10th day, with only a small peak appearing on the 7th day. A larger peak appeared on the 11th day while the highest peak occurred on the 13th day, and then expression decreased to the previous level by the 16th day (<xref ref-type="fig" rid="F6">Figure 6C</xref>). In contrast, the expression peaks of four glycosyltransferase genes (i.e., <italic>UGT85A19</italic>, <italic>UGT94AF1</italic>, <italic>UGT94AF2</italic>, and <italic>UGT94AF3</italic>) appeared in the fruit development stage (<xref ref-type="bibr" rid="B21">Thodberg et al., 2018</xref>). The expression levels of these four genes did not fluctuate significantly during seed germination.</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption><p>Changes in the water content <bold>(A)</bold>, amygdalin content <bold>(B)</bold>, and expression of key regulatory genes <bold>(C)</bold> in kernels of longstalk almond during the process of seed germination promoted by water treatment.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fpls-12-753151-g006.tif"/>
</fig>
<p>Amygdalin has the effect of inhibiting seed germination, providing a nitrogen source for plant growth and insect resistance, which can be coordinated by water. In the early stage of water treatment, water can dissolve amygdalin to reduce the amount of amygdalin in the seed kernel and relieve its inhibition on seed germination to a certain extent. After seed germination, amygdalin synthesis is initiated by two key enzymes, namely, <italic>CYP79D16</italic> and <italic>CYP71AN24</italic>, which regulate amygdalin synthesis (<xref ref-type="bibr" rid="B21">Thodberg et al., 2018</xref>) to avoid insect pests in the early stage of seed germination. The response of amygdalin content to water is favorable to avoid seed germination in periods of drought. Almond germplasm may reduce its demand for precipitation in arid areas by regulating the amygdalin content.</p>
</sec>
</sec>
<sec id="S4" sec-type="conclusion">
<title>Conclusion</title>
<p>In this study, a large-scale study and evaluation of amygdalin content in wild and cultivated almond kernels were carried out for the first time. Almond resources contain abundant amygdalin, which indicates that kernels are an excellent source of amygdalin. The results also showed that different almond germplasm resources have great variation in kernel amygdalin content. Longstalk almond, Tangut almond, and wild almond are suitable as raw materials for traditional Chinese medicine.</p>
<p>This study also points out that some environmental factors were closely related to amygdalin content, among which altitude, aspect, annual precipitation (Bio12), UV intensity, topsoil sodicity (T_ESP), and topsoil base saturation (T_BS) significantly affected the amygdalin content. This provides a direction for future research on amygdalin regulation. It also provides a method for reference for the relationship between other plant metabolites and environmental factors.</p>
<p>During the germination of almond seeds, water had a synergistic effect on seed germination ability by regulating the amygdalin content. At the early stages of germination, water decreased the inhibitory effect of amygdalin on germination. At the later stage, amygdalin was synthesized by regulating key genes to improve the insect resistance of the plants. Almonds may utilize the water-soluble nature of amygdalin and activate amygdalin synthesis genes for the purpose of regulating amygdalin to play an important physiological role in almond seed germination. The correlation between amygdalin concentration and water stress needs further research.</p>
</sec>
<sec id="S5" sec-type="data-availability">
<title>Data Availability Statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="FS1">Supplementary Material</xref>, further inquiries can be directed to the corresponding author/s.</p>
</sec>
<sec id="S6">
<title>Author Contributions</title>
<p>WW conceived and X-QX designed the study. WW and X-ZX processed the data, performed the analyses and analyzed the results, and wrote the manuscript. J-MZ and Z-JL edited the manuscript. All authors read and approved the final version of the manuscript.</p>
</sec>
<sec id="conf1" sec-type="COI-statement">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="pudiscl1" sec-type="disclaimer">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
</body>
<back>
<sec id="S7" sec-type="funding-information">
<title>Funding</title>
<p>The authors gratefully acknowledge the financial support from the Fundamental Research Funds for the Central Non-profit Research Institution of CAF (CAFYBB2017ZA004-7), the National Natural Science Foundation of China (32170392, 41501059), and the National Science and Technology Program for Public Wellbeing (2012GS610203).</p>
</sec>
<sec id="S8" sec-type="supplementary-material">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fpls.2021.753151/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fpls.2021.753151/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Image_1.TIF" id="FS1" mimetype="image/tiff" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>Supplementary Figure 1</label>
<caption><p>Standard curve of HPLC assay in amygdalin detection.</p></caption>
</supplementary-material>
<supplementary-material xlink:href="Table_1.DOCX" id="TS1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_2.DOCX" id="TS2" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_3.DOCX" id="TS3" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_4.DOCX" id="TS4" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_5.DOCX" id="TS5" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_6.DOCX" id="TS6" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
<supplementary-material xlink:href="Table_7.DOCX" id="TS7" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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<fn id="footnote2"><label>2</label><p><ext-link ext-link-type="uri" xlink:href="http://www.fao.org/soils-portal/soil-survey/soil-maps-and-databases/harmonized-world-soil-database-v12/en/">http://www.fao.org/soils-portal/soil-survey/soil-maps-and-databases/harmonized-world-soil-database-v12/en/</ext-link></p></fn>
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