<?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.2022.133019</article-id><article-id pub-id-type="publisher-id">AJPS-115772</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>
 
 
  Estimate of the Current Condition of Populations of the &lt;i&gt;Lagochilus olgae&lt;/i&gt; R.KAM. (Lamiaceae Lindl.) in Uzbekistan
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Buston</surname><given-names>Islamov</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>Murtoza</surname><given-names>Hasanov</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>Gulbonu</surname><given-names>Turakulova</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>Akbar</surname><given-names>Akhmedov</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Samarkand State University, Samarkand, Uzbekistan</addr-line></aff><pub-date pub-type="epub"><day>09</day><month>03</month><year>2022</year></pub-date><volume>13</volume><issue>03</issue><fpage>307</fpage><lpage>315</lpage><history><date date-type="received"><day>1,</day>	<month>February</month>	<year>2022</year></date><date date-type="rev-recd"><day>7,</day>	<month>March</month>	<year>2022</year>	</date><date date-type="accepted"><day>10,</day>	<month>March</month>	<year>2022</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>
 
 
  Intense human pressure and global warming have caused habitat destruction in these areas and increased the number of endangered species. These species are endemic to the Nuratau ridge and are under high human pressure. We found four populations of both species in the Nuratau ridge. For each population we measured plant density and determined population maturity and ontogenetic spectrum. We also described the plant community where each population grew. At all sites population density was low, with most populations being classified as mature with centred ontogenetic structure.
 
</p></abstract><kwd-group><kwd>Biodiversity</kwd><kwd> Conservation</kwd><kwd> Population</kwd><kwd> &lt;i&gt;Lagochilus&lt;/i&gt;</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Ineffective use of plant resources for human welfare has resulted in the loss of plant biodiversity worldwide [<xref ref-type="bibr" rid="scirp.115772-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref2">2</xref>]. In terms of biodiversity, the highest-mountain ecosystems of Central Asia link to the most utility areas in the world called hotspots [<xref ref-type="bibr" rid="scirp.115772-ref3">3</xref>]. “A high level of endemism in the mountains is linked to environmental conditions such as geological structure, high mountain ranges and climatic conditions. Threats to the biodiversity of Central Asia have been recognized since the middle of the 20th century” [<xref ref-type="bibr" rid="scirp.115772-ref4">4</xref>]. Global warming is likely to drive loss of vegetation cover [<xref ref-type="bibr" rid="scirp.115772-ref5">5</xref>]. The ecosystems are exposed to intensive anthropogenic pressure which has caused habitat breakdown [<xref ref-type="bibr" rid="scirp.115772-ref6">6</xref>].</p><p>Scenarios climate change is expected to become more extreme and longer drought periods in Central Asia [<xref ref-type="bibr" rid="scirp.115772-ref7">7</xref>]. “The Millennium Ecosystem Assessment estimates a global reduction of vascular plant biodiversity of between 13% and 19%, between 1970 and 2050, and a reduction of between 7% and 9%, from 2000 to 2050 has also been predicted” [<xref ref-type="bibr" rid="scirp.115772-ref8">8</xref>].</p><p>Consequently, to the IUCN Red List update in 2008, over 900 species have gone extinct since 1500 (http://www.iucnredlist.org) including many vertebrates, invertebrates, and plants. In parallel, the number of endangered species has increased. In combination with global warming related changes in climatic conditions, these developments have also affected the flora of Uzbekistan, with the number of Red List plant species having almost doubled in the last 30 years: from 163 in 1984 to 324.</p><p>This Lamiaceae family has essential oils that are used in the medical, pharmaceutical, cosmetics, and food industries [<xref ref-type="bibr" rid="scirp.115772-ref9">9</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref10">10</xref>]. The genus Lagochilus belong to the most economically important from the Lamiaceae family. This genus comprises 46 species worldwide (www.theplantlist.org). In the flora of Uzbekistan, the genus Lagochilus is represented by 13 species [<xref ref-type="bibr" rid="scirp.115772-ref11">11</xref>]. Some plants from the genus Lagochilus are among the red listed species from the Lamiaceae family. The genus Lagochilus includes 13 species and four of which (Lagochilusvvedenskyi, L. olgae, L. proskorjakovii and L. inebrians) are in the Red Book of the Republic of Uzbekistan [<xref ref-type="bibr" rid="scirp.115772-ref12">12</xref>].</p><p>Species of this genus have great economic importance and are extensively used as medicinal raw material [<xref ref-type="bibr" rid="scirp.115772-ref13">13</xref>]. The leaves contain alcohols, lagochilin (0.6% - 2%), essential oils (0.03%) and vitamin K and most of the genus’ members contain narcotic, hemostatic, and other substances [<xref ref-type="bibr" rid="scirp.115772-ref14">14</xref>]. Locally, most species of this genus are used for treating skin illness, controlling bloodletting and nervous disorders [<xref ref-type="bibr" rid="scirp.115772-ref15">15</xref>].</p><p>Populations of Lagochilus species are affected in their native range by harsh environmental conditions, such as highly eroded soils, rock slides, large rocky slopes, intense winds and few pollinators. In addition, populations of Lagochilus species are under pressure from anthropogenic factors, such as overgrazing, harvesting for fodder, fuel, medicinal raw material and trampling which have resulted in a decrease of the natural habitats of these plants, as observed by Beshko [<xref ref-type="bibr" rid="scirp.115772-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref17">17</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref20">20</xref>]. The purpose of this paper is to assess the status of L. olgae (Lo) in the wild nature.</p></sec><sec id="s2"><title>2. Material and Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p>The study was conducted in the Nuratau ridge. The Nuratau ridge includes some mountains (Nuratau, Koytash, Gubdintau, Karachatau, Aktau and Karatau) and is located at the north-western edge of the Pamir-Alai mountain range (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The climate is Mediterranean, the average minimum temperature is 13.4˚C and average maximum temperature 43˚C. Annual rainfall exceeds 206 mm (<xref ref-type="fig" rid="fig2">Figure 2</xref> and <xref ref-type="fig" rid="fig3">Figure 3</xref>). Soils are grey-brown, sandy and brown and contain between 4% to 7% humus The highest point of Nuratau reaches 2169 m above sea level (<xref ref-type="fig" rid="fig4">Figure 4</xref>) [<xref ref-type="bibr" rid="scirp.115772-ref18">18</xref>].</p><p>This mountain system forms part of the tectonic range in Central Asia. This system comprises middle-dry lowlands and mountains, and hosts high biodiversity.</p><p>This ridge is one of the key botanical regions of Central Asia. The flora of the Nuratau mountains includes about 1285 species of vascular plants, out of them 29 are endemic species [<xref ref-type="bibr" rid="scirp.115772-ref16">16</xref>].</p></sec><sec id="s2_2"><title>2.2. Study Species</title><p>The study focuses on red-list species is L. olgae.</p><p>L. olgae was described by Beshko in 1997 [<xref ref-type="bibr" rid="scirp.115772-ref16">16</xref>]. The species is endemic for Nuratau. The species belonged to caudex, polycarpicdwarf shrubs, whose perennial axes form a short multiaxial caudex. Renewal buds are at a height of 1 - 2 cm above the substrate. Flowering occurs in June - July. Reproduction is mainly by seeds but the species also vegetative reproduce by particulation. Mostly Lagochilus species are C3 plants [<xref ref-type="bibr" rid="scirp.115772-ref19">19</xref>] (<xref ref-type="table" rid="table1">Table 1</xref>).</p></sec><sec id="s2_3"><title>2.3. Study Design</title><p>Due to the united distribution of L. olgae only four populations of L. olgae have been described in the wild. All these populations are included in this study, were studied in the Nuratau mountains.</p><p>In this study, we focus on the four populations L. olgae.</p><p>At each of the sites we described the plant community and, we inventoried all plant species occurring in one randomly selected 25 &#215; 25 mplot. Unidentified plant species were collected for identification. Total vegetation cover was estimated in each plot using the method developed by Braun Blanquet [<xref ref-type="bibr" rid="scirp.115772-ref20">20</xref>], where each species cover was assessed based on cover classes (0 - 5%, 5% - 25%, 25% - 50%, 50% - 75%, and 95% - 100%). The life form of plants was described according to the 9th volume “Plant Identifier of Central Asia” [<xref ref-type="bibr" rid="scirp.115772-ref21">21</xref>], into trees, shrubs, semi-shrubs, dwarf-shrubs, herbs (perennial, biennial and annual). Plant taxonomy was in accordance to Cherepanov [<xref ref-type="bibr" rid="scirp.115772-ref22">22</xref>] and www.plantlist/.</p><p>Each transect was 1 m wide and 10 m long and was subdivided into 10<sup>−</sup><sup>1</sup> m<sup>2</sup> squares. In each of the squares we counted the number of individuals in each ontogenetic stage-seedlings, j—juvenile, im—immature, v—virginile, g1—young generative, g2—mature generative, g3—old generative, ss—subsenile, s – senile [<xref ref-type="bibr" rid="scirp.115772-ref23">23</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref24">24</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref25">25</xref>].</p><p>The ontogenetic spectrum of the population was then determined according to a standard method by Uranov [<xref ref-type="bibr" rid="scirp.115772-ref24">24</xref>] and Uranov, Smirnova [<xref ref-type="bibr" rid="scirp.115772-ref26">26</xref>]. Four types of ontogenetic spectrum can be distinguished [<xref ref-type="bibr" rid="scirp.115772-ref27">27</xref>], dependent on the proportion of individuals in the pre-generative state (seedlings, juvenile, immature, virginile), generative state (young generative, mature generative, old generative) and</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Characteristics of the focal species L. olgae</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Characteristics</th><th align="center" valign="middle" >L. olgae</th></tr></thead><tr><td align="center" valign="middle" >Life form</td><td align="center" valign="middle" >Dwarf-shrub</td></tr><tr><td align="center" valign="middle" >Height (cm)</td><td align="center" valign="middle" >30 - 40</td></tr><tr><td align="center" valign="middle" >Colour of flower</td><td align="center" valign="middle" >White</td></tr><tr><td align="center" valign="middle" >Form of leaves</td><td align="center" valign="middle" >Divided</td></tr><tr><td align="center" valign="middle" >Flowering</td><td align="center" valign="middle" >May - June</td></tr><tr><td align="center" valign="middle" >Uses</td><td align="center" valign="middle" >Fodder</td></tr><tr><td align="center" valign="middle" >Red List category</td><td align="center" valign="middle" >II-rare</td></tr><tr><td align="center" valign="middle" >C<sub>3</sub> plants (doesn’t have photosynthetic adaptations to reduce photorespiration)</td><td align="center" valign="middle" >+</td></tr></tbody></table></table-wrap><p>post-generative state (subsenile, senile).</p><p>Average density of individuals per 1 m<sup>2</sup> was measured as the average number of individuals in each of the 30 1 m<sup>2</sup> quadrates within a population. Ecological density was measured according to Odum [<xref ref-type="bibr" rid="scirp.115772-ref28">28</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.115772-ref31">31</xref>].</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><p>The first population of L. olgae was in the northern part of Nuratau ridge, it was far 4 - 6 km from Ukhum village (<xref ref-type="table" rid="table2">Table 2</xref>). The soil was described as fine gravelly. Total vegetative cover was 30%, total cover of L. olgae in the community was less than 4%. We found 30 species of plants in the community. Out of them four were shrubs, semi-shrubs three, dwarf-shrub one, perennials 17 and annuals five.</p><p>The second population L. olgae (Buloksoy) located of 10 - 12 km north of the Ukhum village. The soil of the described area is fine-grained - gravelly. Total vegetation cover was 40%, and total cover of L. olgae was about 5% (<xref ref-type="table" rid="table2">Table 2</xref>). I found 22 species in the population of which three were shrubs, dwarf-shrubs two, perennials 16, annual one (<xref ref-type="table" rid="table2">Table 2</xref>).</p><p>The third population of L. olgae (Toshtashlarsoy) was 8 - 10 km of the north of Mekhayamvillage. The soil of the described area was gravelly with large stones. Total vegetative cover was ca. 25%, in it the share of focal species was about 3% (<xref ref-type="table" rid="table2">Table 2</xref>). We found 26 species of vascular species in the population, of which four were shrubs, semi-shrubs three, dwarf-shrub one, perennials seven and annuals two.</p><p>The last fourth population of L. olgae recorded on the south-eastern slope of Nuratau ridge. This population was near the settlement of Mekhayam (2 km east of the village). The soil of the surveyed area was stony gravelly. Total vegetative cover of this population was 35% and total cover of L. olgae was less than 3% (<xref ref-type="table" rid="table2">Table 2</xref>). We found 14 species of vascular species in the population, of which two were semi-shrubs, dwarf-shrub one, perennials nine and annuals two.</p><p>Our study has revealed that the studied populations do not span the entire</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Description of current population of L. olgae</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Population №</th><th align="center" valign="middle" >N</th><th align="center" valign="middle" >E</th><th align="center" valign="middle" >Elevation</th><th align="center" valign="middle" >Community/dominant species</th><th align="center" valign="middle" >Total vegetation cover %</th><th align="center" valign="middle" >Total cover of focal species %</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >40˚29.258'</td><td align="center" valign="middle" >66˚46.702'</td><td align="center" valign="middle" >1784</td><td align="center" valign="middle" >Amygdalus bucharica, Artemisia tunuisecta, Galiumpamiroalaicum, Poabulbosa</td><td align="center" valign="middle" >30</td><td align="center" valign="middle" >4</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >40˚50'085&quot;</td><td align="center" valign="middle" >66˚44.414'</td><td align="center" valign="middle" >1672</td><td align="center" valign="middle" >Phlomisnubilans, Thalictrumsultanabadense, Loniceranummulariifolia, Cotoneaster nummularius, Tulipaturkestanica, Iris maracandica</td><td align="center" valign="middle" >40</td><td align="center" valign="middle" >5</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >40˚43.904'</td><td align="center" valign="middle" >66˚94.819'</td><td align="center" valign="middle" >1412</td><td align="center" valign="middle" >Amygdalus bucharica, Loniceranummulariifolia, Artemisia tunuisecta, Perovskiascrophulariifolia, Taeniatherumcrinitum, Ferula ovina, Bromusscoparius</td><td align="center" valign="middle" >25</td><td align="center" valign="middle" >3</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >39˚67.153'</td><td align="center" valign="middle" >66˚92.155'</td><td align="center" valign="middle" >1127</td><td align="center" valign="middle" >Artemisia tunuisecta, Carexpachystylus, Hepyricumperforatum</td><td align="center" valign="middle" >35</td><td align="center" valign="middle" >3</td></tr></tbody></table></table-wrap><p>ontogenetic spectrum as there were no seedlings, juvenile, immature, and senile individuals. The characteristic spectrum of the populations of L. olgae was the centred type, with a peak on the mature generative individuals. The ontogenetic structure of the populations of L. olgae has not previously been studied. We found that the peak in the spectrum of the studied populations corresponds to a group of middle generative plants. The first population has the percentage ratio of these age groups is 60%, in the second population has 85%, in third is 93.75%, and last one has 78.2% middle generative plants (<xref ref-type="fig" rid="fig5">Figure 5</xref>). Proceeding from the ontogeny described, we can assume that the characteristic ontogenetic spectrum of L. olgae, should be centred.</p><p>Centred spectra, according to Zaugolnova (1994), are formed in caudex herbaceous plants with a long-life span of individuals in the middle age ontogenetic state, their least elimination and difficult germination of seeds. Accumulation of middle generative plants in populations is associated with long-term development and minimal elimination of individuals of this ontogenetic group.</p></sec><sec id="s4"><title>4. Conclusions</title><p>During the field research, we studied four populations of L. olgae and determined 102 vascular species in Nuratau Mountain. L. olgae was very rare in this study area. Populations of these focal species were unsatisfactory. The study revealed that ontogenetic structure was predominantly centred, with most plants in the generative (g2) state. Because mature plants (g2) were more tolerant than others under the natural and human pressure in this study area.</p><p>The investigation indicated that the populations were all in all mature with most plants in the generative state. Mature generative plants were dominated in the populations because g2 was tolerant to abiotic and anthropogenic influences that’s why basically populations were mature.</p></sec><sec id="s5"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s6"><title>Cite this paper</title><p>Islamov, B., Hasanov, M., Turakulova, G. and Akhmedov, A. (2022) Estimate of the Current Condition of Populations of the Lagochilus olgae R.KAM. (Lamiaceae Lindl.) in Uzbekistan. American Journal of Plant Sciences, 13, 307-315. https://doi.org/10.4236/ajps.2022.133019</p></sec></body><back><ref-list><title>References</title><ref id="scirp.115772-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">World Conservation Monitoring Centre (1992) Global Biodiversity: Status of the Earth’s Living Resources. 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