<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">AJPS</journal-id><journal-title-group><journal-title>American Journal of Plant Sciences</journal-title></journal-title-group><issn pub-type="epub">2158-2742</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ajps.2021.127072</article-id><article-id pub-id-type="publisher-id">AJPS-110652</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>
 
 
  Assessment of the State of &lt;i&gt;Onobrychis tavernierfolia&lt;/i&gt; Stocks ex Boiss.(Fabaceae) Cenopopulations Southwestern Kyzylkum(Uzbekistan)
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Habibullo</surname><given-names>F. Shomurodov</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>Ozodbek</surname><given-names>S. Abduraimov</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>Rizamat</surname><given-names>Sh. Khayitov</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Shakhnoza</surname><given-names>U. Saribaeva</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Institute of Botany Academy Sciences Republic of Uzbekistan, Tashkent, Uzbekistan</addr-line></aff><aff id="aff2"><addr-line>Navoi State Pedagogical Institute, Navoi, Uzbekistan</addr-line></aff><pub-date pub-type="epub"><day>29</day><month>06</month><year>2021</year></pub-date><volume>12</volume><issue>07</issue><fpage>1043</fpage><lpage>1050</lpage><history><date date-type="received"><day>3,</day>	<month>June</month>	<year>2021</year></date><date date-type="rev-recd"><day>17,</day>	<month>July</month>	<year>2021</year>	</date><date date-type="accepted"><day>20,</day>	<month>July</month>	<year>2021</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  In the period 2019-2021, two coenotic populations of 
  O. tavernierfolia
   were studied in different ecological and phytocenotic conditions of relic mountain Kuldzhuktau. Very rare species of the Kyzylkum. It is spread at the Kyzylkum: the Kuldzhuktau, near Ayak-Guzhumdy and Churuk (Bukhara region). Inhabits stony and gypseous slopes. There are three small populations can be found. Limiting factors: degradation of habitat as a result of overgrazing. Measures of protection: not protected.
   
  The article is devoted to the assessment of the current state of coenotic populations of the rarest southwestern Kyzylkum (Kuldzhuktau) Onobrychis tavernierfolia. It was found that the studied coenopopulations of O. tavernierfolia are normal and complete.
 
</p></abstract><kwd-group><kwd>Onobrychis Tavernierfolia</kwd><kwd> Cenopopulation</kwd><kwd> Kyzylkum</kwd><kwd> Assessment</kwd><kwd> Rare Plant</kwd><kwd> Population Signs</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Currently, population analysis methods are a reliable way to diagnose the conditions of populations of different plant species in natural and artificial communities. In addition, this set of methods provides the researcher with a departure from subjective visual assessments of the state of plants and plant communities by applying accurate quantitative accounting that reflects the internal plasticity and variability of plants.</p><p>Genus Onobrychis Mill it belongs to the tribe Hedysareae, the subfamily Faboidea, which is part of one of the largest families of flowering plants—Fabaceae, order Fabales. In the modern flora, the genus is represented by 170 species, which are widely distributed in the triangle of Anatolia-Iran-Caucasus.</p><p>The assessment of the state of the coenopopulation of O. tavernierfolia remains poorly understood. Onobrychis tavernierfolia Stocks ex Boiss. (Fabaceae)—a very rare and small annual plant of Kyzylkum desert (part Uzbekistan). One of the rare red book species with a disjunctive range from Central Kyzylkum to Central Iran, a remarkable ephemer—Onobrychis taevernierifolia is a new and very promising phytomeliorant. It is included in the “Red Book of the Republic of Uzbekistan” with the status 1 [<xref ref-type="bibr" rid="scirp.110652-ref1">1</xref>]. The purpose of this work is to study the state of the coenopopulations of Onobrychis taevernierifolia in southwestern Kyzylkumi (Kuldzhuktau).</p></sec><sec id="s2"><title>2. Material and Methods</title><p>In the period 2019-2021, two coenotic populations of O. tavernierfolia were studied in different ecological-phytocenotic conditions of relic mountain Kuldzhuktau (<xref ref-type="fig" rid="fig1">Figure 1</xref>).</p><p>Geobotanical descriptions were performed according to the standard method at sites of 100 m [<xref ref-type="bibr" rid="scirp.110652-ref2">2</xref>].</p><p>According to the allocation characteristics of desert species, it was studied according to the method of M. V. Markov [<xref ref-type="bibr" rid="scirp.110652-ref3">3</xref>]. The relationship between the size of the reproductive force and the life form was studied. Eight features of the allocation characteristic were analyzed: the number of seeds per individual, the total mass of one individual, the mass of roots, the mass of the aboveground vegetative part, the mass of the generative part, the mass of one seed, the height of the</p><p>aboveground part, the length of the roots, and the vector spectrum was constructed. Additionally, the density of O. tavernierifolia individuals was studied.</p></sec><sec id="s3"><title>3. Result and Discussion</title><p>The first cenopopulation was studied along the Churuk-Jangeldy highway in thean altitude of 417 m above sea level. Geographical coordinates of the cenopopulation: N 40044.816 E 063040.229. The soil of the described area is pebbly. The total projected grass cover is 22%. The botanical composition of the community is relatively rich and it consists of 25 species of vascular plants. The plant community is dominated by Salsolaarbuscula,Artemisia diffusa. The dominant species are Astragalusvillosissimus,Ammothamnus lehmanii,Ferula foetida,Tulipa sogdiana,Carex physodes, etc (<xref ref-type="table" rid="table1">Table 1</xref>).</p><p>The second cenopopulation is described 18 km north of the Kyzylkum desert station along the Shafirkan-Jangeldi road as part of the ephemeral-ephemeroid-sagebrush community. Geographical coordinates of the cenopopulation N 400 77.718 E 0630 58.843, height 373 m above sea level. The soil of the described area is gravelly. The total projected grass cover is 21%. The botanical composition of the communities consists of 34 species. The dominant community is Artemisia diffusa Krasch. ex Poljakov. Along with sagebrush, Astragalusammotrophus Bunge, Ferula foetida (Bunge) Regel, Cousiniahammadae Juz., Astragalusvillosisimus Bunge, etc. grow here (<xref ref-type="table" rid="table1">Table 1</xref>).</p><p>O. tavernierifolia Stocks ex Boiss.—annual squat plant, 3 - 7 cm tall. Almost stemless, the leaves on the upper side are covered with short pressed, and from below with long protruding white hairs, located on long (up to 5 cm) petioles ending in a large lobe-leaf obovate. Peduncles 2-3. 5 cm long. Brushes are loose, 3 - 7 flowered. Calyx 3-3. 5 cm long. The beans are wrinkly-cellular, about 1 cm long and wide. Blooms in May, bears fruit in June. Additionally, eight features of the allocation characteristic were analyzed: the number of seeds per individual, the total mass of one individual, the mass of roots, the mass of the aboveground vegetative part, the mass of the generative part, the mass of one seed, the height of the aboveground part, the length of the roots, and the vector spectrum was constructed.</p><p>The analysis of allocation polygrams showed that Onobrychis tavernierifolia has high indicators of the number of seeds (5 points) and the total mass of one individual (4 points), and less values are assigned to the height of the aboveground part of the individuals (2 points) and the length of the roots (2 points) (<xref ref-type="fig" rid="fig2">Figure 2</xref>).</p><p>Seed propagation is the most important stage in the life and development of plants, which ensures the preservation of the turnover (replacement) of generations and, thanks to passive movement, the settlement of populations. In this regard, seeds represent units of reproduction and settlement, means for experiencing unfavorable conditions, and are also a bank of genetic variants that are formed as a result of combinative variability. Seeds store information about the</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Species composition and abundance of the O. tavernierfolia community</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >№</th><th align="center" valign="middle"  rowspan="2"  >Species</th><th align="center" valign="middle"  rowspan="2"  >Life form</th><th align="center" valign="middle"  colspan="2"  >Projective coverplants, % (CP)</th></tr></thead><tr><td align="center" valign="middle" >CP 1</td><td align="center" valign="middle" >CP 2</td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Salsola arbuscula Pall.</td><td align="center" valign="middle" >Shrub</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >1</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Astragalus villosissimus Bunge</td><td align="center" valign="middle" >Shrub</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >1</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >Ammothamnus lehmanii Bunge</td><td align="center" valign="middle" >Shrub</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Artemisia diffusa Krasch.ex Poljakov</td><td align="center" valign="middle" >Semi-shrub</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >5</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Acanthophyllum stenostegium Freyn</td><td align="center" valign="middle" >Semi-shrub</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >2</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >Calligonum zakirovii (Chalkoziev)</td><td align="center" valign="middle" >Shrub</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >Astragalus ammotrophus Bunge</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >1</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >Cousinia hammadae Juz.</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >9</td><td align="center" valign="middle" >Ixiolirion tataricum (Pall.) Schult. &amp; Schult. fil</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" >Ferula foetida (Bunge) Regel</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >2</td></tr><tr><td align="center" valign="middle" >11</td><td align="center" valign="middle" >Tulipa sogdiana Bunge</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >12</td><td align="center" valign="middle" >Carex physodes Bieb.</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >3</td></tr><tr><td align="center" valign="middle" >13</td><td align="center" valign="middle" >Peganumharmala L.</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" ></td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >14</td><td align="center" valign="middle" >Poa bulbosa L.</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >15</td><td align="center" valign="middle" >Allium kyzylkumii Kamelin</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >16</td><td align="center" valign="middle" >Eremurus korolkowii Regel</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >17</td><td align="center" valign="middle" >Rhinopetalum karelinii Fisch.ex D. Don</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >18</td><td align="center" valign="middle" >Tulipa lehmanniana Merkl</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >19</td><td align="center" valign="middle" >Carex physodes Bieb.</td><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >3</td></tr><tr><td align="center" valign="middle" >20</td><td align="center" valign="middle" >Amberboa turanica Iljin</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >21</td><td align="center" valign="middle" >Goldbachia laevigata (Bieb.) DC.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >22</td><td align="center" valign="middle" >Hypecoum parviflorum Kar et. Kir</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >23</td><td align="center" valign="middle" >Nonea caspiсa (Willd.) G. Don</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >24</td><td align="center" valign="middle" >Roеmeria refracta (Stev.) DC</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >1</td></tr><tr><td align="center" valign="middle" >25</td><td align="center" valign="middle" >Onobrychistavernierifolia Stocks ex Boiss</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >26</td><td align="center" valign="middle" >Strigosella africana (L.) Boiss</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >27</td><td align="center" valign="middle" >Anisantha tectorum L.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >28</td><td align="center" valign="middle" >Takhtajanianthapusilla (Pall.) Nazarova</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >29</td><td align="center" valign="middle" >Koelpinia linearis Pall.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >30</td><td align="center" valign="middle" >Delphinium barbatum Bunge</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >32</td><td align="center" valign="middle" >Strigosella grandiflora (Bunge) Botsch</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >32</td><td align="center" valign="middle" >Ceratocephala testiculata (Crantz) Bess.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >33</td><td align="center" valign="middle" >Alyssum desertorum Stapf.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >34</td><td align="center" valign="middle" >Ziziphora tenior L.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >35</td><td align="center" valign="middle" >Stipa hohenackeriana Trin. &amp; Rupr</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >36</td><td align="center" valign="middle" >Bromus danthoniae Trin.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >37</td><td align="center" valign="middle" >Amberboa turanica Iljin</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >38</td><td align="center" valign="middle" >Cuminium setifolium (Boiss.) Koso-Pol.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >−</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >39</td><td align="center" valign="middle" >Ceratocephala falcata (L.) Pers.</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >2</td></tr><tr><td align="center" valign="middle" >40</td><td align="center" valign="middle" >Astragalus remanens Nabiev</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >41</td><td align="center" valign="middle" >Eremopyrum distans (C. Koch) Nevski</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr><tr><td align="center" valign="middle" >42</td><td align="center" valign="middle" >Lallimanthia royleana (Benth.) Bent</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >+</td></tr><tr><td align="center" valign="middle" >43</td><td align="center" valign="middle" >Holosteum polyganum C. Koch</td><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >+</td><td align="center" valign="middle" >−</td></tr></tbody></table></table-wrap><p>principles of the system organization of the population and are able to recreate it under appropriate conditions). By Z. Shaniyazova [<xref ref-type="bibr" rid="scirp.110652-ref4">4</xref>], analysis of allocative signs in desert of ephemers are divided into four groups:</p><p>The first—with low values of the total biomass and seed production; the second—lowest value of the total biomass and average seed production; thirdly, medium or high values of the total biomass and high seed productivity, and a fourth having high or average values of the total biomass and low seed production (<xref ref-type="fig" rid="fig3">Figure 3</xref>; <xref ref-type="table" rid="table2">Table 2</xref>).</p><p>O. tavernierifolia belongs to the first group by the nature of allocation, characterized by low values of total biomass and low seed productivity (<xref ref-type="table" rid="table3">Table 3</xref>).</p><p>The density of ephemera populations can largely be determined by the amount of seed productivity, but it also depends on many parameters that characterize seeds as a special population group. For the permanent existence of desert annuals in the communities, the presence of a soil stock of seeds and the density of individuals is of particular importance.</p><p>At the sites, the soil stock of seeds was determined from a depth of 0 - 10 cm of soil. The maximum number of seeds of incoming seeds per year was noted in CP 2 (up to 9 pcs/1m<sup>2</sup>). On CP 1, this indicator is low (3 pcs/m<sup>2</sup>).</p><p>The density of O. tavernierifolia individuals at temporary sites in 2019 ranged from 0.9 to 2.5 individuals/m<sup>2</sup> and in 2020—0.1 - 3.3 m<sup>2</sup> (<xref ref-type="fig" rid="fig4">Figure 4</xref>). Similar variation in the density of individuals according to Z. Shaniyazova [<xref ref-type="bibr" rid="scirp.110652-ref4">4</xref>] is due to the fact that the seeds of desert ephemera do not have a period of endogenous rest or this period is very short and the possibility of germination is mainly determined by the external situation. According to the density of individuals in the transects desert ephemera are divided into 5 groups [<xref ref-type="bibr" rid="scirp.110652-ref4">4</xref>]:</p><p>1) The highest density—units of individuals/m<sup>2</sup>, presence in the active state; 2) The highest density is a unit of individuals/m<sup>2</sup>, the presence is almost constant; 3) The highest density-tens of individuals/m<sup>2</sup>, the presence of episodic; 4) The highest density-tens of individuals/m<sup>2</sup>, the presence of constant; 5) The highest density is hundreds of individuals/m<sup>2</sup>, the presence is almost constant.</p><p>According to this classification, O. tavernierifolia belongs to the second group: the highest density is a unit of individuals/m<sup>2</sup>, the presence is almost constant.</p><p>O. tavernierifolia is characterized by low seed productivity and accordingly with minimal seed entry into the soil and low density of individuals in coenopopulations. During the years of the study regardless of weather conditions, O. tavernierifolia individuals were constantly present in the transects (<xref ref-type="fig" rid="fig4">Figure 4</xref>).</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Population and organism parameters of O. tavernierifolia</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >№</th><th align="center" valign="middle"  rowspan="2"  >Signs</th><th align="center" valign="middle"  colspan="5"  >Points</th></tr></thead><tr><td align="center" valign="middle" >I</td><td align="center" valign="middle" >II</td><td align="center" valign="middle" >III</td><td align="center" valign="middle" >IV</td><td align="center" valign="middle" >V</td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >The number of seeds</td><td align="center" valign="middle" >5 - 5.4</td><td align="center" valign="middle" >5.5 - 5.8</td><td align="center" valign="middle" >5.9 - 6.2</td><td align="center" valign="middle" >6.3 - 6.6</td><td align="center" valign="middle" >6.7 - 7</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >The total mass of one individual. mg</td><td align="center" valign="middle" >0.37 - 0.45</td><td align="center" valign="middle" >0.46 - 0.54</td><td align="center" valign="middle" >0.55 - 0.63</td><td align="center" valign="middle" >0.63 - 0.72</td><td align="center" valign="middle" >0.73 - 0.85</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >The mass of the roots. mg</td><td align="center" valign="middle" >0.018 - 0.025</td><td align="center" valign="middle" >0.026 - 0.033</td><td align="center" valign="middle" >0.034 - 0.041</td><td align="center" valign="middle" >0.042 - 0.049</td><td align="center" valign="middle" >0.050 - 0.057</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Mass vegetative part. mg</td><td align="center" valign="middle" >0.22 - 0.27</td><td align="center" valign="middle" >0.28 - 0.33</td><td align="center" valign="middle" >0.34 - 0.39</td><td align="center" valign="middle" >0.40 - 0.45</td><td align="center" valign="middle" >0.46 - 0.51</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Mass generative part. g</td><td align="center" valign="middle" >0.05 - 0.116</td><td align="center" valign="middle" >0.007 - 0.183</td><td align="center" valign="middle" >0.184 - 0.25</td><td align="center" valign="middle" >0.26 - 0.326</td><td align="center" valign="middle" >0.327 - 0.384</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >The mass of one seed</td><td align="center" valign="middle" >0.017 - 0.023</td><td align="center" valign="middle" >0.024 - 0.031</td><td align="center" valign="middle" >0.032 - 0.039</td><td align="center" valign="middle" >0.040 - 0.045</td><td align="center" valign="middle" >0.046 - 0.055</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >The height of the aboveground part</td><td align="center" valign="middle" >2.80 - 2.93</td><td align="center" valign="middle" >2.94 - 3.01</td><td align="center" valign="middle" >3.02 - 3.09</td><td align="center" valign="middle" >3.10 - 3.17</td><td align="center" valign="middle" >3.18 - 3.25</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >The length of the roots. cm</td><td align="center" valign="middle" >8.3 - 8.8</td><td align="center" valign="middle" >8.9 - 9.5</td><td align="center" valign="middle" >9.6 - 10.2</td><td align="center" valign="middle" >10.3 - 10.8</td><td align="center" valign="middle" >10.9 - 11.3</td></tr></tbody></table></table-wrap><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Seed productivity of O. tavernierifolia in transects</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Years</th><th align="center" valign="middle"  colspan="4"  >Number of seeds per 1 individual</th></tr></thead><tr><td align="center" valign="middle" >min</td><td align="center" valign="middle" >max</td><td align="center" valign="middle" >Average</td><td align="center" valign="middle" >The error is average.</td></tr><tr><td align="center" valign="middle" >2019</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >4.7</td><td align="center" valign="middle" >0.37</td></tr><tr><td align="center" valign="middle" >2020</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >5.9</td><td align="center" valign="middle" >0.33</td></tr></tbody></table></table-wrap></sec><sec id="s4"><title>4. Conclusions</title><p>In practice, with the modern study of the species population, the main strategy for the protection of rare species is to protect their habitats, i.e., the creation of protected areas is one of the most important areas of human nature protection. However, the last 10 years in the world have seen a doubling in the number and increase in the area of specially protected natural areas of more than 30 million km<sup>2</sup>. The results obtained from the evaluation of populations are used in carrying out monitoring studies for long years on rare plants. At the same time he used it as a material for local “Red books” [<xref ref-type="bibr" rid="scirp.110652-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.110652-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.110652-ref7">7</xref>].</p><p>The analysis of some indicators of O. tavernierifolia showed the following: having low values of total biomass and low seed productivity; the highest density is a unit of individuals/m<sup>2</sup> but the presence is almost constant. According to these characteristics O. tavernierifolia corresponds to the R-strategies and belongs to the group of tolerant species. The results obtained are used in plant protection.</p></sec><sec id="s5"><title>Acknowledgements</title><p>The current research is done under the project PZ—20170919165 Inventory of rare and endangered species of vascular plants of Navoi and Bukhara regions.</p></sec><sec id="s6"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s7"><title>Cite this paper</title><p>Shomurodov, H.F., Abduraimov, O.S., Khayitov, R.Sh. and Saribaeva, S.U. (2021) Assessment of the State of Onobrychistavernierfolia Stocks ex Boiss.(Fabaceae) Cenopopulations Southwestern Kyzylkum(Uzbekistan). American Journal of Plant Sciences, 12, 1043-1050. https://doi.org/10.4236/ajps.2021.127072</p></sec></body><back><ref-list><title>References</title><ref id="scirp.110652-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Red Book of Uzbekistan (2019) Plants and Fungi. 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