<?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">OJE</journal-id><journal-title-group><journal-title>Open Journal of Ecology</journal-title></journal-title-group><issn pub-type="epub">2162-1985</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/oje.2023.136022</article-id><article-id pub-id-type="publisher-id">OJE-125687</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Taxonomic Studies of Weed Communities Growing in Date Palm and Christ’s Thorn Jujube Farms in Ad-Dawadimi, KSA
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Mesfer</surname><given-names>M. Alqahtani</given-names></name><xref ref-type="aff" rid="aff1"><sub>1</sub></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff1"><label>1</label><addr-line>Department of Biological Sciences, Faculty of Science and Humanities, Shaqra University, Ad-Dawadimi, Saudi Arabia</addr-line></aff><pub-date pub-type="epub"><day>07</day><month>06</month><year>2023</year></pub-date><volume>13</volume><issue>06</issue><fpage>345</fpage><lpage>366</lpage><history><date date-type="received"><day>1,</day>	<month>April</month>	<year>2023</year></date><date date-type="rev-recd"><day>17,</day>	<month>June</month>	<year>2023</year>	</date><date date-type="accepted"><day>20,</day>	<month>June</month>	<year>2023</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  The problem of food shortage is one of the most important problems facing many countries in the world. Various factors affect the decline in crop productivity. Where weeds are the most important reasons that cause a huge loss in crop productivity. Studying agricultural ecosystems, knowing their components and explaining the relationship between all of their components, helps a lot in achieving the highest productivity of different crops in addition to benefiting from some types of weeds, as well as, identifying appropriate methods to control the growth of weeds. In this study, 60 species were listed. The most frequent plant families were Asteraceae, Poaceae and Zygophyllaceae. Annuals were the most common life span, as well as, therophytes were the most frequent life form. The most frequent floristic categories were Saharo-Sindian-Sudano-Zambezian and Saharo-Sindian regions. The most famous indicators of biodiversity (species richness, species evenness and species diversity) have been calculated. For managing and classifying data PC-ORD program (TWINSPAN and DCA analyses) was used.
 
</p></abstract><kwd-group><kwd>Weeds</kwd><kwd> Palm</kwd><kwd> Christ’s Thorn Jujube</kwd><kwd> Ad-Dawadimi</kwd><kwd> Saudi Arabia</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>In light of the problem of food shortages facing the world, a special attention to agricultural systems to increase crop productivity was very important. One of the main reasons for the lack of crop productivity is the presence of weeds. Crop productivity losses due to the presence of weeds are greater than those from pests [<xref ref-type="bibr" rid="scirp.125687-ref1">1</xref>] . The presence of weeds in some agricultural systems can lead to a decrease in crop productivity to more than 55% [<xref ref-type="bibr" rid="scirp.125687-ref2">2</xref>] . Lots of weeds have allopathic activity [<xref ref-type="bibr" rid="scirp.125687-ref3">3</xref>] . The harmful effects of weeds on crops vary starting from preventing the growth of some crop seeds [<xref ref-type="bibr" rid="scirp.125687-ref4">4</xref>] , as well as, competition with crops for natural resources as nutrients, water in the soil and light [<xref ref-type="bibr" rid="scirp.125687-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref6">6</xref>] .</p><p>Weeds are considered a biological important component in the most ecosystems as range, arable land and forests [<xref ref-type="bibr" rid="scirp.125687-ref7">7</xref>] . One of the reasons for the emergence of weeds in ecosystems is high temperatures in addition to the regular rains. The best time to get rid of weeds is the first stages and they are removed selectively [<xref ref-type="bibr" rid="scirp.125687-ref8">8</xref>] . Soil characteristics and crop type are the most important factors determining the presence and composition of weeds communities [<xref ref-type="bibr" rid="scirp.125687-ref9">9</xref>] . Some weeds are a source of food and secondary pesticides [<xref ref-type="bibr" rid="scirp.125687-ref10">10</xref>] , as well as, several weeds have many economic and medical benefits [<xref ref-type="bibr" rid="scirp.125687-ref11">11</xref>] - [<xref ref-type="bibr" rid="scirp.125687-ref21">21</xref>] .</p><p>Weed control methods include mechanical weeding, hand weeding, burning, slashing, biological control and herbicide use. The choice of a weed control method depends on many factors such as effectiveness, availability, cost, and risks associated with use [<xref ref-type="bibr" rid="scirp.125687-ref22">22</xref>] . Hand hoeing weed is the most effective and safe method of weed control [<xref ref-type="bibr" rid="scirp.125687-ref23">23</xref>] . Modern techniques such as remote sensing programs can be used to control and monitor the growth of weeds for precision management of weeds and to make maps for the distribution of weeds to reduce the excessive use of herbicide that results in severe environmental damage [<xref ref-type="bibr" rid="scirp.125687-ref24">24</xref>] .</p><p>Date palm (Phoenix dactylifera) is a plant species that belongs to family Arecaceae. Palm is one of the most important economic tropical plants, which is a rich source of food and raw materials [<xref ref-type="bibr" rid="scirp.125687-ref25">25</xref>] . Palm is one of the important plant species that was used in traditional medicine for a long time, especially in the Arab countries, as well as many raw materials extracted from palms were used in the production of medicines in modern medicine [<xref ref-type="bibr" rid="scirp.125687-ref26">26</xref>] . Saudi Arabia has approximately 25 million palm trees and is the third globally in the production of dates [<xref ref-type="bibr" rid="scirp.125687-ref27">27</xref>] .</p><p>Christ’s thorn jujube (Ziziphus spina-christi) species of plant belongs to family Rhamnaceae. It has been used in traditional medicine, especially in Arab lands for a long time. It has many medical and economic benefits as ant nociceptive activity [<xref ref-type="bibr" rid="scirp.125687-ref28">28</xref>] , source for saponins, free sugar, proteins and antidiarrheal effects [<xref ref-type="bibr" rid="scirp.125687-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref30">30</xref>] , protective effect against aflatoxicosis [<xref ref-type="bibr" rid="scirp.125687-ref31">31</xref>] , treatment pain [<xref ref-type="bibr" rid="scirp.125687-ref32">32</xref>] , rich source of flavonoids [<xref ref-type="bibr" rid="scirp.125687-ref33">33</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref34">34</xref>] , source for lipids, triterpenoids, alkaloids, free radical scavenging potential and antioxidant activity [<xref ref-type="bibr" rid="scirp.125687-ref35">35</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref36">36</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref37">37</xref>] , the hypolipidemic and antioxidant activity [<xref ref-type="bibr" rid="scirp.125687-ref38">38</xref>] , antimicrobial activity [<xref ref-type="bibr" rid="scirp.125687-ref39">39</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref40">40</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref41">41</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref42">42</xref>] , anti-inflammatory [<xref ref-type="bibr" rid="scirp.125687-ref43">43</xref>] and antibacterial activity [<xref ref-type="bibr" rid="scirp.125687-ref44">44</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref45">45</xref>] , Anticancer activity [<xref ref-type="bibr" rid="scirp.125687-ref46">46</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref47">47</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref48">48</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref49">49</xref>] , Antidiabetic Potentiality [<xref ref-type="bibr" rid="scirp.125687-ref50">50</xref>] , Antiviral activity [<xref ref-type="bibr" rid="scirp.125687-ref51">51</xref>] .</p><p>Several studies have investigated weed composition in different agroecosystems in Saudi Arabia; in the Eastern part [<xref ref-type="bibr" rid="scirp.125687-ref52">52</xref>] , in the Gizan Region [<xref ref-type="bibr" rid="scirp.125687-ref53">53</xref>] , in Al-Kharj Region [<xref ref-type="bibr" rid="scirp.125687-ref54">54</xref>] , in Al-Qassim Region [<xref ref-type="bibr" rid="scirp.125687-ref55">55</xref>] and in Al-Jouf Region [<xref ref-type="bibr" rid="scirp.125687-ref56">56</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref57">57</xref>] . Nevertheless, [<xref ref-type="bibr" rid="scirp.125687-ref58">58</xref>] indicated that the study of agroecosystems and the evaluation of weeds therein have not received much attention in Saudi Arabia. During the last two decades, weeds formed a major problem in agroecosystems in many countries of the world, especially in Saudi Arabia. On the Saudi Arabia Northern region studied some species of Plantago and Genus Tephrosia [<xref ref-type="bibr" rid="scirp.125687-ref59">59</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref60">60</xref>] .</p><p>Studying agroecosystems, knowing all their components, and understanding the relationship between crops and weeds, and the effect of each on the other, is very important for achieving higher crop yields, as well as, benefiting from some types of weeds. So the aim of this study was to evaluate the weeds that are found in palm and Christ’s thorn jujube crops in the Ad-Dawadimi, Saudi Arabia.</p></sec><sec id="s2"><title>2. Materials and Methods</title><p>In Ad-Dawadimi, Saudi Arabia 20 stands (ten palm farms and ten Christ’s thorn jujube farms) were selected to do evaluate their environmental status. This study has been conducted from February to March 2022.</p><p>Five quadrates have been selected, in each stand, the area of each 100 m<sup>2</sup>. In every stand, necessary field data were recorded (name and cover of species). Also, soil samples have been collected to do various analyses later on.</p><p>Weed species were determined in the field. Then, plant species identification and nomenclature was assured later [<xref ref-type="bibr" rid="scirp.125687-ref61">61</xref>] - [<xref ref-type="bibr" rid="scirp.125687-ref69">69</xref>] . Life forms of the recorded species were identified according to [<xref ref-type="bibr" rid="scirp.125687-ref70">70</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref71">71</xref>] , while, chorology were identified according to Eig (1931) [<xref ref-type="bibr" rid="scirp.125687-ref72">72</xref>] and Davis during the period from 1965 to 1985 [<xref ref-type="bibr" rid="scirp.125687-ref73">73</xref>] .</p><p>In the 20 studied stands 15 soil factors were gauged; moisture content (%). pH, sodium (mg/L), potassium (mg/L), phosphorus (mg/L), bicarbonates (%), chlorides (mg/L), calcium (mg/L), magnesium (mg/L), nitrogen (%), electrical conductivity (EC; mS/cm) and total dissolved salts (ppm) in soil extract, on the other side, carbonates (%), organic carbon (%) and organic matter (%) were gauged, in dried soil. All soil factors were measured after Estefan et al., (2013) [<xref ref-type="bibr" rid="scirp.125687-ref74">74</xref>] . Descriptive statistics (average, minimum and maximum) of all soil factors were extracted from Sigma plot 12.5 program.</p><p>Biological diversity indicators (species richness, species diversity and species evenness), Two Way Indicator Species Analysis (TWINSPAN) and DE trended Correspondence Analysis (DCA) were extracted from PC-ORD program (McCune and Mefford, 1999) [<xref ref-type="bibr" rid="scirp.125687-ref75">75</xref>] .</p></sec><sec id="s3"><title>3. Study Area</title><p>Ad-Dawadimi is famous Governorate in Northwest of Riyadh Region, Saudi Arabia. It is characterized by a wonderful location on Najd hill with a total area of 27,500 km<sup>2</sup>. It lies at longitudes of 44.3405603˚W and latitude of 24.5091759˚N, nearly 940 m above sea level. Ad-Dawadimi bounded by Unayzah, Al Mithnab, Al Bukayriyah Governorates and Buraydah Town (Al-Qassim Region) to the north, Al Quwaiiyah Governorate (Riyadh Region) to the south, Shaqra Governorate (Riyadh Region) to the east and Afif and Ar Rass Governorates (Al-Qassim Region) to the west. The study area map was extracted from Arc GIS program (<xref ref-type="fig" rid="fig1">Figure 1</xref>). The mean maximum temperature ranged from 21˚C in January to 41˚C in July and August. On the other hand, the mean minimum temperature ranged from 5˚C in January to 23˚C in August. Regarding precipitation, no rainfall was recorded in four months of the year; September, August, July and June. On the contrary, April was the rainiest month in this time (<xref ref-type="fig" rid="fig2">Figure 2</xref>) was used to illuminate climatic date during 30 years. South wind direction was the most apparent direction in this period followed by the north direction (<xref ref-type="fig" rid="fig3">Figure 3</xref>).</p></sec><sec id="s4"><title>4. Results</title><p>A collection of 60 species, belonging to 20 families, were listed in farms of both Christ’s thorn jujube and palm in Ad-Dawadimi Governorate, Saudi Arabia. The</p><p>most frequent families are Asteraceae, Poaceae and Zygophyllaceae with ten species (16.7%), nine species (15%) and seven species (11.7%), respectively. Whereas, Brassicaceae and Fabaceae include four species (6.7%) each. there are three species (5%) in the following families; Chenopodiaceae, Convolvulaceae, Euphorbiaceae and Plantaginacae. While, Borginaceae, Caryophyllaceae and Primulacae have two species (3.3%) each. At last, eight families (Asclepiadaceae, Cyperaceae, Juncaceae, Malvaceae, Polygonaceae, Portulacaceae, Solanaceae and Tamaricaceae) are denoted by a single species (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="fig" rid="fig4">Figure 4</xref>).</p><p>Concerning recorded species life span, the biggest number of species are annuals with 58.3% (35 species). On the other hand, perennials species have the percent of 41.7% (25 species) (<xref ref-type="table" rid="table1">Table 1</xref> &amp; <xref ref-type="table" rid="table2">Table 2</xref> and <xref ref-type="fig" rid="fig5">Figure 5</xref>).</p><p>With respect to life form, therophyte is the most public life form with 51.7% (31 species), hemicryptophyte was denoted by 18.3% (11 species), chamaephyte was denoted by 15% (9 species). Both of geophyte and phanerophyte were denoted by 6.7% (4 species) each. Parasite was denoted by a single species (Cuscuta campestris) (<xref ref-type="table" rid="table1">Table 1</xref> &amp; <xref ref-type="table" rid="table3">Table 3</xref> and <xref ref-type="fig" rid="fig6">Figure 6</xref>).</p><p>As for phytogeographical side, the recorded species belonged to biregional, pluriregional, palaeotropical, monoregional, cosmopolitan and pantropical. First, biregional were 21 species (35%). Second, pluriregional were 12 species (20%). Third, palaeotropical were nine species (15%). Fourth, both monoregional and cosmopolitan were seven species (11.7%) each. Finally, pantropical species were four species (6.7%) (<xref ref-type="table" rid="table1">Table 1</xref> &amp; <xref ref-type="table" rid="table4">Table 4</xref> and <xref ref-type="fig" rid="fig7">Figure 7</xref>).</p><table-wrap-group id="1"><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> List of species and their families, life spans, life forms and floristic categories in Ad-Dawadimi Governorate</title></caption><table-wrap id="1_1"><table><tbody><thead><tr><th align="center" valign="middle" >Family</th><th align="center" valign="middle" >Species</th><th align="center" valign="middle" >Life span</th><th align="center" valign="middle" >Life form</th><th align="center" valign="middle" >Floristic categories</th></tr></thead><tr><td align="center" valign="middle" >Asclepiadaceae</td><td align="center" valign="middle" >Cynanchum acutum L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Ph.</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle"  rowspan="10"  >Asteraceae</td><td align="center" valign="middle" >Cichorium endivia L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle" >Conyza bonariensis (L.) Cronquist</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME</td></tr><tr><td align="center" valign="middle" >Lactuca serriola L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle" >Launaea nudicaulis (L.) Hook. f.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >IT − TR</td></tr><tr><td align="center" valign="middle" >Launea capitata (Spreng.) Dandy</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >SA − SI</td></tr><tr><td align="center" valign="middle" >Pulicaria undulata (L.) C.A.Mey.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle" >Senecio glaucus L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Reichardia tingitana (L.) Roth</td><td align="center" valign="middle" >Ann</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle" >Pluchea dioscoridis (L.) DC.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Ph.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle" >Sonchus oleraceus L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Borginaceae</td><td align="center" valign="middle" >Heliotropium aegyptiacum Lehm.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle" >Heliotropium bacciferum Forssk.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle"  rowspan="4"  >Brassicaceae</td><td align="center" valign="middle" >Sisymbrium irio L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle" >Eruca sativa Mill.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR + SA − SI</td></tr><tr><td align="center" valign="middle" >Diplotaxis harra Forsk.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Zilla spinose L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >ME + IR − TR + EU − SI + SA − SI</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Caryophyllaceae</td><td align="center" valign="middle" >Spergularia marina (L.) Griseb.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR</td></tr><tr><td align="center" valign="middle" >Stellaria pallida (Dumort.) Murb.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + ER − SR</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Chenopodiaceae</td><td align="center" valign="middle" >Chenopodium album L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Chenopodium murale L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Suaeda aegyptiaca (Hasselq.) Zohary.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr></tbody></table></table-wrap><table-wrap id="1_2"><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="3"  >Convolvulaceae</th><th align="center" valign="middle" >Convolvulus arvensis L.</th><th align="center" valign="middle" >Per.</th><th align="center" valign="middle" >Geo.</th><th align="center" valign="middle" >PAL</th></tr></thead><tr><td align="center" valign="middle" >Cressa cretica L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Cuscuta campestris Yunck.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Par.</td><td align="center" valign="middle" >PAN</td></tr><tr><td align="center" valign="middle" >Cyperaceae</td><td align="center" valign="middle" >Cyperus rotundus L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Geo.</td><td align="center" valign="middle" >PAN</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Euphorbiaceae</td><td align="center" valign="middle" >Euphorbia peplus L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Euphorbia helioscopia L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Ricinus communis L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Ph.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle"  rowspan="4"  >Fabaceae</td><td align="center" valign="middle" >Alhagi graecorum Boiss.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Melilotus indicus (L.) All.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Prosopis farcta (Banks &amp; Sol.) Macbr.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Vicia sativa L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME</td></tr><tr><td align="center" valign="middle" >Juncaceae</td><td align="center" valign="middle" >Juncus rigidus Desf.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >ME + IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Malvaceae</td><td align="center" valign="middle" >Malva parviflora L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR</td></tr><tr><td align="center" valign="middle"  rowspan="3"  >Plantaginacae</td><td align="center" valign="middle" >Plantago amplexicaulis Cav.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Plantago lanceolata L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >ME + IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Plantago ovata Forssk.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle"  rowspan="9"  >Poaceae</td><td align="center" valign="middle" >Avena fatua L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Cynodon dactylon (L.) Pers.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Geo.</td><td align="center" valign="middle" >PAN</td></tr><tr><td align="center" valign="middle" >Imperata cylindrica (L.) Raeusch.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >ME + S − Z</td></tr><tr><td align="center" valign="middle" >Lolium perenne L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR</td></tr><tr><td align="center" valign="middle" >Phragmites australis (Cav.) Trin. ex Steud.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Geo.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Polypogon monspeliensis (L.) Desf.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >COSM</td></tr><tr><td align="center" valign="middle" >Setaria viridis (L.) P. Beauv.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR + SA − SI</td></tr><tr><td align="center" valign="middle" >Poa annua L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR</td></tr><tr><td align="center" valign="middle" >Dactyloctenium aegyptium (L.) Willd.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Polygonaceae</td><td align="center" valign="middle" >Emex spinosa (L.) Campd.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >PAN</td></tr><tr><td align="center" valign="middle" >Portulacaceae</td><td align="center" valign="middle" >Portulaca oleracea L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle"  rowspan="2"  >Primulacae</td><td align="center" valign="middle" >Anagallis arvensis L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR</td></tr><tr><td align="center" valign="middle" >Samolus valerandi L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >PAL</td></tr><tr><td align="center" valign="middle" >Solanaceae</td><td align="center" valign="middle" >Solanum nigrum L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Hem.</td><td align="center" valign="middle" >ME + IR − TR + ER − SR</td></tr><tr><td align="center" valign="middle" >Tamaricaceae</td><td align="center" valign="middle" >Tamarix nilotica (Ehrenb.) Bunge</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Ph.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle"  rowspan="7"  >Zygophyllaceae</td><td align="center" valign="middle" >Fagonia arabica L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI</td></tr><tr><td align="center" valign="middle" >Fagonia indica Burm. f.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI</td></tr><tr><td align="center" valign="middle" >Fagonia mollis Delile.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI</td></tr><tr><td align="center" valign="middle" >Tribulus terrestris L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th</td><td align="center" valign="middle" >IR − TR + ER − SR + SZ</td></tr><tr><td align="center" valign="middle" >Zygophyllum album L.f.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >ME + IR − TR + SA − SI + S − Z</td></tr><tr><td align="center" valign="middle" >Zygophyllum coccineum L.</td><td align="center" valign="middle" >Per.</td><td align="center" valign="middle" >Cha.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr><tr><td align="center" valign="middle" >Zygophyllum simplex L.</td><td align="center" valign="middle" >Ann.</td><td align="center" valign="middle" >Th.</td><td align="center" valign="middle" >SA − SI + S − Z</td></tr></tbody></table></table-wrap></table-wrap-group><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Number of species and percentage belonging to its life span in Ad-Dawadimi Governorate</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Life span</th><th align="center" valign="middle" >No. of species</th><th align="center" valign="middle" >Percentage</th></tr></thead><tr><td align="center" valign="middle" >Annual</td><td align="center" valign="middle" >35</td><td align="center" valign="middle" >58.3</td></tr><tr><td align="center" valign="middle" >Perennial</td><td align="center" valign="middle" >25</td><td align="center" valign="middle" >41.7</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >100</td></tr></tbody></table></table-wrap><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Number of species and percentage according to its life forms in Ad-Dawadimi Governorate</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Life form</th><th align="center" valign="middle" >No. of species</th><th align="center" valign="middle" >Percentage</th></tr></thead><tr><td align="center" valign="middle" >Therophyte</td><td align="center" valign="middle" >31</td><td align="center" valign="middle" >51.7</td></tr><tr><td align="center" valign="middle" >Hemicryptophyte</td><td align="center" valign="middle" >11</td><td align="center" valign="middle" >18.3</td></tr><tr><td align="center" valign="middle" >Chamaephyte</td><td align="center" valign="middle" >9</td><td align="center" valign="middle" >15.0</td></tr><tr><td align="center" valign="middle" >Geophyte</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >6.7</td></tr><tr><td align="center" valign="middle" >Phanerophyte</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >6.7</td></tr><tr><td align="center" valign="middle" >Parasite</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >100</td></tr></tbody></table></table-wrap><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Number of species and percentage belonging to main floristic categories in Ad-Dawadimi Governorate</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Main floristic categories</th><th align="center" valign="middle" >No. of species</th><th align="center" valign="middle" >Percentage</th></tr></thead><tr><td align="center" valign="middle" >Biregionals</td><td align="center" valign="middle" >21</td><td align="center" valign="middle" >35.0</td></tr><tr><td align="center" valign="middle" >Pleuriregionals</td><td align="center" valign="middle" >12</td><td align="center" valign="middle" >20.0</td></tr><tr><td align="center" valign="middle" >Palaeotropical</td><td align="center" valign="middle" >9</td><td align="center" valign="middle" >15.0</td></tr><tr><td align="center" valign="middle" >Monoregional</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >11.7</td></tr><tr><td align="center" valign="middle" >Cosmopolitan</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >11.7</td></tr><tr><td align="center" valign="middle" >Pantropical</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >6.7</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >100</td></tr></tbody></table></table-wrap><p>Regarding monoregional, it includes three regions; Saharo-Sindian (4 species = 6.7%), Mediterranean (2 species = 3.3%) and Irano-Turanian (1 species = 1.7%). Biregional contains five regions; Saharo-Sindian-Sudano-Zambesian (8 species = 13.3%), Mediterranean-Irano-Turanian (6 species = 10%), Irano-Turanian-Saharo-Sindian (5 species = 8.3%). Both Mediterranean-Sudano-Zambesian and Mediterranean-Euro-Siberian (1 species = 1.7) each. Pleuriregional includes 6 regions; Mediterranean-Irano-Turanian-Euro-Siberian (5 species = 8.3%), Mediterranean-Irano-Turanian-Saharo-Sindian (3 species = 5%), Mediterranean-Irano-Turanian-Euro-Siberian-Saharo-Sindian (2 species = 3.3%). both of Irano-Turanian-Euro-Siberian-Sudano-Zambesian and Mediterranean-Irano-Turanian-Saharo-Sindian-Sudano-Zambesian (1 species = 1.7%) (<xref ref-type="table" rid="table1">Table 1</xref> &amp; <xref ref-type="table" rid="table5">Table 5</xref> and <xref ref-type="fig" rid="fig8">Figure 8</xref>).</p><p>The most important indicators of biological diversity were calculated; species richness; species diversity (Shannon’s and Simpson’s diversity index) and species evenness. The species richness average was 4.8 species. Shannon’s diversity index average was 0.7. Simpson’s diversity index average was 0.3. Species evenness average was 0.4.</p><table-wrap id="table5" ><label><xref ref-type="table" rid="table5">Table 5</xref></label><caption><title> Number of species and percentage belonging to chorology in Ad-Dawadimi Governorate</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Floristic categories</th><th align="center" valign="middle" >No. of species</th><th align="center" valign="middle" >Percentage</th></tr></thead><tr><td align="center" valign="middle"  colspan="3"  >Monoregional</td></tr><tr><td align="center" valign="middle" >IT − TR</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >ME</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >3.3</td></tr><tr><td align="center" valign="middle" >SA − SI</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >6.7</td></tr><tr><td align="center" valign="middle" >Sub total</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >11.7</td></tr><tr><td align="center" valign="middle"  colspan="3"  >Biregionals</td></tr><tr><td align="center" valign="middle" >SA − SI + S − Z</td><td align="center" valign="middle" >8</td><td align="center" valign="middle" >13.3</td></tr><tr><td align="center" valign="middle" >ME + S − Z</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >ME + ER − SR</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >ME + IR − TR</td><td align="center" valign="middle" >6</td><td align="center" valign="middle" >10.0</td></tr><tr><td align="center" valign="middle" >IR − TR + SA − SI</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >8.3</td></tr><tr><td align="center" valign="middle" >Sub total</td><td align="center" valign="middle" >21</td><td align="center" valign="middle" >35.0</td></tr><tr><td align="center" valign="middle"  colspan="3"  >Pleuriregionals</td></tr><tr><td align="center" valign="middle" >IR − TR + ER − SR + SZ</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >ME + IR − TR + ER − SR</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >8.3</td></tr><tr><td align="center" valign="middle" >ME + IR − TR + ER − SR + SA − SI</td><td align="center" valign="middle" >2</td><td align="center" valign="middle" >3.3</td></tr><tr><td align="center" valign="middle" >ME + IR − TR + SA − SI</td><td align="center" valign="middle" >3</td><td align="center" valign="middle" >5.0</td></tr><tr><td align="center" valign="middle" >ME + IR − TR + SA − SI + S − Z</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >1.7</td></tr><tr><td align="center" valign="middle" >Sub total</td><td align="center" valign="middle" >12</td><td align="center" valign="middle" >20.0</td></tr><tr><td align="center" valign="middle"  colspan="3"  >World wide</td></tr><tr><td align="center" valign="middle" >PAL</td><td align="center" valign="middle" >9</td><td align="center" valign="middle" >15.0</td></tr><tr><td align="center" valign="middle" >PAN</td><td align="center" valign="middle" >4</td><td align="center" valign="middle" >6.7</td></tr><tr><td align="center" valign="middle" >COSM</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >11.7</td></tr><tr><td align="center" valign="middle" >Sub total</td><td align="center" valign="middle" >20</td><td align="center" valign="middle" >33.3</td></tr><tr><td align="center" valign="middle" >Total</td><td align="center" valign="middle" >60</td><td align="center" valign="middle" >100</td></tr></tbody></table></table-wrap><p>Moisture content range was from 2.8% (stand 13) to 31% (stand 18) with an average of 15.3%. pH ranged from 8.1 (stands 14 and 17) to 9.1 (stands 2) with an average of 8.6. Sodium content range was from 342 mg/L (stands 9) to 5542.6 mg/L (stands 14) with an average of 1915.4 mg/L. Potassium content had an average of 139.2 mg/L and ranged from 61.4 mg/L (stands 3) to 412.9 mg/L (stands 14). Phosphorus content range was from 39.4 mg/L (stands 6) to 58.4 mg/L (stands 19) with an average of 47.4 mg/L. Carbonate content range was from 0.3% (stands 20) to 1.1% (stands 15) and with an average of 0.6%. Bicarbonate content range was from 0.3% (stands 4) to 0.9% (stands 18) and with an average of 0.5%. Chlorides content average was 7.1 mg/L and its range was from 1.1 mg/L (stands 13) to 86.7 mg/L (stands 14). Calcium content range was from 60 mg/L (stands 5) to 566.7 mg/L (stands 11) and with an average of 231.7 mg/L. Magnesium content reached the average of 116 mg/L and the range was from 12 mg/L (stands 4) to 600 mg/L (stands 14). Organic matter ranged from 1.5% (stands 14) to 8.1% (stands 13) with an average of 5.4%. Organic carbon had an average of 3.1% and a range from 0.9% (stands 14) to 4.7% (stand 13). Nitrogen content range was from 0.1% (stands 11) to 10.4% (stands 3) with an average of 3.8%. Electrical conductivity recorded an average of 1.9 mS/cm and its range was from 0.2 mS/cm (stand 13) to 9.5 mS/cm (stand 14). Total dissolved salts had an average of 1212.2 ppm and its range was from 130 ppm (stand 13) to 6050 ppm (stand 14) (<xref ref-type="table" rid="table6">Table 6</xref>).</p><table-wrap id="table6" ><label><xref ref-type="table" rid="table6">Table 6</xref></label><caption><title> Soil parameters with an average, maximum and minimum value</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Soil parameters</th><th align="center" valign="middle" >Average (Maximum-Minimum)</th></tr></thead><tr><td align="center" valign="middle" >Moisture content (%)</td><td align="center" valign="middle" >15.3 (2.8 - 31)</td></tr><tr><td align="center" valign="middle" >pH</td><td align="center" valign="middle" >8.6 (8.1 - 9.1)</td></tr><tr><td align="center" valign="middle" >Sodium (mg/L)</td><td align="center" valign="middle" >1915.4 (342 - 5542.6)</td></tr><tr><td align="center" valign="middle" >Potassium (mg/L)</td><td align="center" valign="middle" >139.2 (61.4 - 412.9)</td></tr><tr><td align="center" valign="middle" >Phosphorus (mg/L)</td><td align="center" valign="middle" >47.4 (39.4 - 58.4)</td></tr><tr><td align="center" valign="middle" >Carbonate (%)</td><td align="center" valign="middle" >0.6 (0.3 - 1.1)</td></tr><tr><td align="center" valign="middle" >Bicarbonate (%)</td><td align="center" valign="middle" >0.5 (0.3 - 0.9)</td></tr><tr><td align="center" valign="middle" >Chlorides (mg/L)</td><td align="center" valign="middle" >7.1 (1.1 - 86.7)</td></tr><tr><td align="center" valign="middle" >Calcium (mg/L)</td><td align="center" valign="middle" >231.7 (60 - 566.7)</td></tr><tr><td align="center" valign="middle" >Magnesium (mg/L)</td><td align="center" valign="middle" >116 (12 - 600)</td></tr><tr><td align="center" valign="middle" >Organic matter (%)</td><td align="center" valign="middle" >5.4 (1.5 - 8.1)</td></tr><tr><td align="center" valign="middle" >Organic carbon (%)</td><td align="center" valign="middle" >3.1 (0.9 - 4.7)</td></tr><tr><td align="center" valign="middle" >Nitrogen (%)</td><td align="center" valign="middle" >3.8 (0.1 - 10.4)</td></tr><tr><td align="center" valign="middle" >Electrical conductivity (mS/cm)</td><td align="center" valign="middle" >1.9 (0.2 - 9.5)</td></tr><tr><td align="center" valign="middle" >Total dissolved salts (ppm)</td><td align="center" valign="middle" >1212.2 (130 - 6050)</td></tr></tbody></table></table-wrap><p>TWINSPAN analysis showed that 20 stands were divided into two main groups at the first classified level. The first main group is the negative group which comprises ten stands (Sidr farms) and the most famous indicator species for this group is Ziziphus spina-christi. At the second division level, the negative group is divided into two groups; the first one comprises three stands (3, 4 and 7) with Chenopodium album as an indicator species, while the second one comprises seven stands (1, 2, 5, 6, 8, 9 and 10) with Cynanchum acutum and Spergularia marina as the indicator species. On the other side, the second main group is the positive group which comprises ten stands (Palm farms) and the most known indicator species for this group is Phoenix dactylifera. At the second classified level, the positive group is divided into two groups; the first one comprises six stands (12, 13, 16, 17, 18 and 19) with Eruca sativa and Alhagi graecorum as the indicator species, while the second one comprises only four stands (11, 14, 15 and 19) with Juncus rigidus as an indicator species (<xref ref-type="fig" rid="fig9">Figure 9</xref>).</p><p>DCA analysis illustrated that the 20 stands were classified into two main groups. The first one is Christ’s thorn jujube farms stands (1:10) with 13 indicator species (Anagallis arvensis, Suaeda aegyptiaca, Spergularia marina, Chenopodium album, Chenopodium murale, Convolvulus arvensis, Sonchus oleraceus, Polypogon monspeliensis, Stellaria pallida, Euphorbia peplus, Lolium perenne, Setaria viridis and Cynodon dactylon). The second one is Palm farms stands (11:20) with 11 indicator species (Juncus rigidus, Tamarix nilotica, Phragmites australis, Cyperus rotundus, Samolus valerandi, Imperata cylindrica, Cynanchum acutum, Eruca sativa, Alhagi graecorum, Cuscuta campestris and Sisymbrium irio) (<xref ref-type="fig" rid="fig1">Figure 1</xref>0).</p><p>DCA analysis illustrated that the 20 stands were classified into two main groups. The first one is Christ’s thorn jujube farms stands (1:10) with the most positively correlated soil factors; pH and nitrogen content. The second one is Palm farms stands (11:20) with the positively correlated soil factors; moisture</p><p>content, electrical conductivity, total dissolved salts, bicarbonates, chlorides, phosphorus, sodium, potassium, calcium, magnesium, carbonates, organic carbon and organic matter (<xref ref-type="fig" rid="fig1">Figure 1</xref>1).</p></sec><sec id="s5"><title>5. Discussion</title><p>The composition of weed communities was evaluated in two types of crops (Palm and Christ’s thorn jujube Farms). Sixty weed species were recorded in farms of Palm and Christ’s thorn jujube in Ad-Dawadimi Governorate, Saudi Arabia. The recorded species (60) belonged to 20 plant families. The number of plant species monitored in this study differs relatively from many previous studies conducted on other crops and on other regions in Saudi Arabia. 118 species were recorded in palm plantations in Al-Hasa Region [<xref ref-type="bibr" rid="scirp.125687-ref52">52</xref>] , in neglected farms, 51 species were recorded in Al-Kharj Region [<xref ref-type="bibr" rid="scirp.125687-ref54">54</xref>] , in palm farms, 55 species were recorded in central part of KSA [<xref ref-type="bibr" rid="scirp.125687-ref55">55</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref76">76</xref>] , in plantations of palms and olives, 71</p><p>species were recorded in Al-Jouf Region [<xref ref-type="bibr" rid="scirp.125687-ref56">56</xref>] , in the olive orchards, 46 species were recorded in Tabuk Region [<xref ref-type="bibr" rid="scirp.125687-ref77">77</xref>] , in citrus plantations, 33 species were recorded in Al-Jouf Region [<xref ref-type="bibr" rid="scirp.125687-ref57">57</xref>] , in plantations of olives and palms, 53 species were recorded in Al-Jouf Region [<xref ref-type="bibr" rid="scirp.125687-ref78">78</xref>] - [<xref ref-type="bibr" rid="scirp.125687-ref83">83</xref>] . Also, the results agreement with the result on Northern Border region, KSA [<xref ref-type="bibr" rid="scirp.125687-ref84">84</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref85">85</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref86">86</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref87">87</xref>] . One of the reasons for the low number and variety of weeds is the process of plowing the soil, annually [<xref ref-type="bibr" rid="scirp.125687-ref88">88</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref89">89</xref>] . Excessive use of herbicides helps the emergence of more resistant weeds [<xref ref-type="bibr" rid="scirp.125687-ref58">58</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref90">90</xref>] . The difference in the number of plant species, recorded in this study and the number of plant species recorded in previous studies on other regions in Saudi Arabia, is due to many reasons; the most important of which is the difference in natural crops in addition to many other environmental factors affecting each region.</p><p>Asteraceae, Poaceae and Zygophyllaceae were the most frequent families in farms of Christ’s thorn jujube and Palm in Ad-Dawadimi. These results are largely consistent with many studies concerned with studying agroecosystems in other regions within Saudi Arabia [<xref ref-type="bibr" rid="scirp.125687-ref57">57</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref80">80</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref81">81</xref>] . The emergence of the Poaceae family may be the result of deterioration in the agricultural environment [<xref ref-type="bibr" rid="scirp.125687-ref91">91</xref>] . In addition, the Poaceae family is known to be tolerant of environmental extremes [<xref ref-type="bibr" rid="scirp.125687-ref92">92</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref93">93</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref94">94</xref>] . The result showed that the dominant life span is annuals, as well as, the prevailing life form is therophytes in this study. These results are consistent with many previous studies done on other agricultural environments in other regions within Saudi Arabia [<xref ref-type="bibr" rid="scirp.125687-ref54">54</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref55">55</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref56">56</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref57">57</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref77">77</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref81">81</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref82">82</xref>] . This might be due to many of the factors that characterized annuals (therophytes), the most important of which was the shortening of their life cycle and the possibility of completing their life cycle in difficult environmental conditions [<xref ref-type="bibr" rid="scirp.125687-ref95">95</xref>] . In addition, therophytes can form flowers in a short time [<xref ref-type="bibr" rid="scirp.125687-ref96">96</xref>] . Moreover, therophytes can complete seed formation without the need for a visiting pollinator [<xref ref-type="bibr" rid="scirp.125687-ref97">97</xref>] .</p><p>Saharo-Sindian and Saharo-Sindian-Sudano-Zambezian regions were the most frequent floristic categories in this study. These results correspond to [<xref ref-type="bibr" rid="scirp.125687-ref83">83</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref98">98</xref>] [<xref ref-type="bibr" rid="scirp.125687-ref99">99</xref>] . This is due to the fact that these plants are important indicators of desert environments, which are characterized by harsh conditions.</p><p>A total of 15 soil parameters were analyzed in all the studied stands. TWINSPAN and DCA analyses were done to organize data and divide the studied stands into ecologically similar groups. Each group of stands has their own plant indicators, as well as, soil factors affecting them. The results showed that the studied stands were divided into two main groups: palm farms stands (10 stands) and Christ’s thorn jujube farms stands (ten stands).</p></sec><sec id="s6"><title>6. Conclusions</title><p>In this study, weed communities found in date palms and Christ’s thorn jujube farms in Ad-Dawadimi Governorate, Saudi Arabia were evaluated. 60 species belonging to the 20 plant families were recorded. The most frequent families were Asteraceae, Poaceae and Zygophyllaceae. The dominant life span is annuals whereas therophytes is the dominant life form. 15 soil factors were analyzed in the studied stands. DCA and TWINSPAN analyses were accomplish to classifying data.</p><p>Studying the agroecosystems, to know their components and the relationship between all of these components, helps a lot in achieving the highest productivity of different crops. It also helps in choosing the best methods to control the growth of weeds.</p></sec><sec id="s7"><title>Acknowledgements</title><p>The author extends their appreciation to the Department of Biological Sciences, Faculty of Science and Humanities, Shaqra University, Saudi Arabia.</p></sec><sec id="s8"><title>Conflicts of Interest</title><p>The author declares no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s9"><title>Cite this paper</title><p>Alqahtani, M.M. (2023) Taxonomic Studies of Weed Communities Growing in Date Palm and Christ’s Thorn Jujube Farms in Ad-Dawadimi, KSA. 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