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  <front>
    <journal-meta>
      <journal-title-group>
        <journal-title>ORCID:</journal-title>
      </journal-title-group>
    </journal-meta>
    <article-meta>
      <title-group>
        <article-title>Plant Composition and Diversity in Selected Urban Green Spaces of Athens, Greece: A Significant Management Suggestion</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Alexandra D. Solomou</string-name>
          <email>solomou@fria.gr</email>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Evangelia Avramidou</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Nikolaos D. Proutsos</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Evangelia Korakaki</string-name>
          <email>e.korakaki@gmail.com</email>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Panagiotis Koulelis</string-name>
          <email>pkoulelis@fria.gr</email>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Aimilia B. Kontogianni</string-name>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Christos Georgiadis</string-name>
          <email>cgeorgiadis@gmail.com</email>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>George Karetsos</string-name>
          <email>gekaretsos@yahoo.gr</email>
          <xref ref-type="aff" rid="aff0">0</xref>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>Alkmanos</institution>
          ,
          <addr-line>Athens, 11528</addr-line>
          ,
          <country country="GR">Greece</country>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>Hellenic Agricultural Organization “DEMETER”, Institute of Mediterranean Forest Ecosystems</institution>
          ,
          <addr-line>Terma</addr-line>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>Homeotech Co</institution>
          ,
          <addr-line>Thessaloniki</addr-line>
          ,
          <country country="GR">Greece</country>
        </aff>
      </contrib-group>
      <pub-date>
        <year>1909</year>
      </pub-date>
      <volume>000</volume>
      <fpage>0</fpage>
      <lpage>0002</lpage>
      <abstract>
        <p>Urban green spaces are of vital importance in terms of urban biodiversity conservation. The main aim of this study was to estimate urban plant composition and diversity of main green space types in Maroussi Municipality. Results showed that the highest herbaceous plant species richness was found in park-OAKA B, followed by pedestrian-Gramou and mild traffic roadM. Alexandrou, while the lowest herbaceous species richness was in street island-Vasilisis Sofias. Also, the highest woody plant species richness was found in park-OAKA B and mild traffic road-M. Alexandrou, followed by street island-Vasilisis Sofias and pedestrian-Gramou. Herbaceous and woody plant species richness were observed satisfactory in urban parks of Biodiversity, urban green spaces, native, alien, city, urbanization level, Greece1 It is a fact that urban regions can support more species than a nearby surrounding landscape, hosting large numbers of native and alien species. A significant contribution can be offered to biodiversity due to the different habitat types, which range from low to high land transformation levels [1]. That is the reason why urban green spaces contribute to the ecosystem services, becoming a progressively important refuge for native biodiversity [2].</p>
      </abstract>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>-</title>
      <p>changes.</p>
    </sec>
    <sec id="sec-2">
      <title>1. Introduction</title>
      <sec id="sec-2-1">
        <title>Maroussi</title>
      </sec>
      <sec id="sec-2-2">
        <title>Municipality. These findings could</title>
        <p>provide insights for plant biodiversity
conservation in urban green spaces. However, the underlying mechanisms of the urbanization
degree and plant diversity need further study. Finally, promoting the use of native species in
landscape design projects, especially in parks, pedestrian and mild traffic roads may contribute
to creating sustainable urban spaces in the region in the future, under the concept of climatic</p>
        <p>
          2022 Copyright for this paper by its authors.
[
          <xref ref-type="bibr" rid="ref10 ref9">9,10</xref>
          ]. Other factors, i.e. landscaping-gardening practices, usage and maintenance of exotic species
contribute to plant species diversity in cities [
          <xref ref-type="bibr" rid="ref2">2</xref>
          ]. Apart from that, urban fauna can be influenced by
vegetation structures (complexity, size, connectivity, vertical structure) [
          <xref ref-type="bibr" rid="ref11 ref2">2,11</xref>
          ]. Due to these facts,
special studies are needed so that the potential of various urban green spaces and their biodiversity
conservation should be revealed and managed accordingly. For this reason, the potential of different
green spaces in terms of biodiversity conservation along an urban-rural settlement gradient needs to be
revealed for appropriate management practices [
          <xref ref-type="bibr" rid="ref9">9</xref>
          ]. In this study we aimed to analyze the main green
space categories of Maroussi Municipality in terms of plant composition and diversity (herbaceous and
woody plant species richness), which were shaped by species selection approach, management and
ecological conditions.
        </p>
      </sec>
    </sec>
    <sec id="sec-3">
      <title>2. Study Area and Sampling</title>
      <p>The Municipality of Maroussi is located 12 km northeast of the centre of Athens and belongs
administratively to the Eastern Regional Sector of the Attica Region. The administrative boundaries of
the municipality occupy an area of 1,309.3 ha and extend north up to the lowest foothills of Penteli, up
to its hills Magoufanas (Pefki), Kifissia and today's Melissia, while to east, south and southwest the
demarcation follows basically their network small and large streams in the area: the Polydrosos stream,
which is connected to the largest stream of Podoniftis. From a geomorphological point of view,
Maroussi is located at its southeastern end basin formed between Parnitha, Penteli and Turkovounia.
The water systems of the area are formed mainly by three streams named Kokkinaras, Sappho and
Polydrosos.</p>
      <p>
        Based on available longterm data of the most recent climatic period (1960-1997), obtained from the
nearest meteorological station of Tatoi (38.10oN, 23.78oE, alt. 236 m a.s.l.), the climate of the region
is semi-arid [
        <xref ref-type="bibr" rid="ref12 ref13">12,13</xref>
        ] according to UNEP’s [
        <xref ref-type="bibr" rid="ref14">14</xref>
        ] aridity classification system which is based on
Thornthwaite’s [
        <xref ref-type="bibr" rid="ref15">15</xref>
        ] water balance approach. The annual precipitation of the broader area is low
(460mm) with however increased potential evapotranspiration rate (891 mm/y) resulting in a rather
decreased aridity index of 0.48. During the dry period of the year, the water deficit for the development
of vegetation is about 460m, whereas in the wet period the water surplus is zero.
      </p>
      <p>
        Fοur public green spaces (street island-Vasilisis Sofias, park-OAKA B, pedestrian-Gramou and mild
traffic road-M. Alexandrou) were selected for the current study. More specifically, the sampling of
herbaceous plant communities was done in each type of urban green space in spring 2019. The
samplings of herbaceous plants were carried out in plots 0.25 m2 (0.5 m × 0.5 m), in order to record
herbaceous plant composition and diversity (species richness). Also, representative sampling surfaces
measuring 100 m2 (10x10m) [
        <xref ref-type="bibr" rid="ref16 ref17">16,17</xref>
        ] were used for woody plant species composition and diversity [
        <xref ref-type="bibr" rid="ref18">18</xref>
        ].
Species identification was mainly based on Mountain Flora of Greece I, II [
        <xref ref-type="bibr" rid="ref19 ref20">19,20</xref>
        ], Flora Hellenica I &amp;
II [
        <xref ref-type="bibr" rid="ref2 ref21">21,2</xref>
        ] and Flora Europaea [
        <xref ref-type="bibr" rid="ref23 ref24 ref25 ref26 ref27">23,24,25,26,27</xref>
        ]. Plant nomenclature and distribution follow Dimopoulos
et al. [
        <xref ref-type="bibr" rid="ref28 ref29">28,29</xref>
        ].
      </p>
    </sec>
    <sec id="sec-4">
      <title>3. Results and Discussion</title>
      <p>
        A total of 29 herbaceous plant and 14 woody plant species were determined in the selected urban
green spaces. Among these, 28 herbaceous plant and 9 woody plant species are native species while
one herbaceous plant (Figure 1) and five woody plant species are alien species (Figure 2-6). The highest
herbaceous plant species richness was found in park-OAKA B, followed by pedestrian-Gramou and
mild traffic road-M. Alexandrou while the lowest herbaceous species richness was in street
islandVasilisis Sofias (Figure 7, Table 1). Also, the highest woody plants species richness was found in
parkOAKA B and mild traffic road-M. Alexandrou, followed by street island-Vasilisis Sofias and
pedestrian-Gramou (Figure 8, Table 2). Herbaceous and woody plant species richness were observed
satisfactory in urban parks. It is a well-known fact that by understanding the various roles of vegetation
as far as our environment is concerned, we become fully aware of its importance. We have to safeguard
vegetation because it is a natural protection-a kind of barrier-as it directly influences the energy balance
on the earth's surface saving us not only from extreme weather conditions but also from pollution or
erosion. Moreover, it helps to maintain and even enrich ecology, resulting in better living conditions.
However, selecting and applying vegetation species in particular areas is a demanding task which
requires in-depth knowledge of the physical characteristics and relative needs of the specific/selected
vegetation [
        <xref ref-type="bibr" rid="ref30">30</xref>
        ].
      </p>
      <p>
        Another very interesting and crucial issue is that of invasive plants-when alien species spread into
landscapes through trade, traffic and horticulture (the most common dispersal pathways) [
        <xref ref-type="bibr" rid="ref31 ref32">31,32</xref>
        ].
Invasive plants can affect bioregions causing serious ecological/environmental damage and measures
should be taken targeting the human-facilitated introductions. Studies have shown that the composition
of the invasive plants is higher in parks containing highway greenings and public gardens. The alien
species of the present study cover large areas because of their extensive quality. According to Kowarik
[
        <xref ref-type="bibr" rid="ref1">1</xref>
        ], although the presence of alien plant harbours risks, these risks are mostly related to particular
species and do not apply to the whole group of alien ones. This very fact explains the need for programs
targeting species management and their implementation by many municipalities advising against
planting alien species.
      </p>
      <sec id="sec-4-1">
        <title>Status</title>
      </sec>
      <sec id="sec-4-2">
        <title>Native</title>
      </sec>
      <sec id="sec-4-3">
        <title>Native</title>
      </sec>
      <sec id="sec-4-4">
        <title>Native</title>
      </sec>
      <sec id="sec-4-5">
        <title>Native</title>
      </sec>
      <sec id="sec-4-6">
        <title>Native</title>
      </sec>
      <sec id="sec-4-7">
        <title>Native</title>
      </sec>
      <sec id="sec-4-8">
        <title>Native</title>
      </sec>
      <sec id="sec-4-9">
        <title>Native</title>
      </sec>
      <sec id="sec-4-10">
        <title>Native</title>
      </sec>
      <sec id="sec-4-11">
        <title>Native</title>
      </sec>
      <sec id="sec-4-12">
        <title>Native</title>
      </sec>
      <sec id="sec-4-13">
        <title>Native</title>
      </sec>
      <sec id="sec-4-14">
        <title>Native</title>
      </sec>
      <sec id="sec-4-15">
        <title>Native</title>
      </sec>
      <sec id="sec-4-16">
        <title>Native</title>
      </sec>
      <sec id="sec-4-17">
        <title>Native</title>
      </sec>
      <sec id="sec-4-18">
        <title>Native</title>
      </sec>
      <sec id="sec-4-19">
        <title>Native</title>
      </sec>
      <sec id="sec-4-20">
        <title>Native</title>
      </sec>
      <sec id="sec-4-21">
        <title>Native</title>
      </sec>
      <sec id="sec-4-22">
        <title>Native</title>
      </sec>
      <sec id="sec-4-23">
        <title>Native</title>
      </sec>
      <sec id="sec-4-24">
        <title>Native</title>
      </sec>
      <sec id="sec-4-25">
        <title>Native</title>
      </sec>
      <sec id="sec-4-26">
        <title>Native</title>
      </sec>
      <sec id="sec-4-27">
        <title>Native</title>
      </sec>
      <sec id="sec-4-28">
        <title>Native</title>
      </sec>
      <sec id="sec-4-29">
        <title>Native</title>
      </sec>
      <sec id="sec-4-30">
        <title>Native</title>
      </sec>
      <sec id="sec-4-31">
        <title>Native</title>
      </sec>
      <sec id="sec-4-32">
        <title>Native</title>
      </sec>
      <sec id="sec-4-33">
        <title>Native</title>
      </sec>
      <sec id="sec-4-34">
        <title>Native</title>
      </sec>
      <sec id="sec-4-35">
        <title>Native</title>
      </sec>
      <sec id="sec-4-36">
        <title>Native</title>
      </sec>
      <sec id="sec-4-37">
        <title>Native</title>
      </sec>
      <sec id="sec-4-38">
        <title>Native</title>
      </sec>
      <sec id="sec-4-39">
        <title>Alien</title>
      </sec>
      <sec id="sec-4-40">
        <title>Native</title>
      </sec>
      <sec id="sec-4-41">
        <title>Native</title>
      </sec>
      <sec id="sec-4-42">
        <title>Native</title>
        <p>
          This study demonstrates that parks in Maroussi are among the most species rich types of urban
greenspaces for herbaceous and woody plants. It is also remarkable to note that the species richness
found in urban green spaces is to a great extent determined by certain factors, such as: a) the
environmental heterogeneity in urban areas [
          <xref ref-type="bibr" rid="ref1">1</xref>
          ], b) the species selection made by the person in charge
[
          <xref ref-type="bibr" rid="ref33">33</xref>
          ], c)the status of the neighborhood both cultural and socioeconomic [
          <xref ref-type="bibr" rid="ref1 ref34 ref35">34,35,1</xref>
          ], d) the selective force
of random natural disasters [
          <xref ref-type="bibr" rid="ref36">36</xref>
          ] and e) the plant availability of local garden produce.
        </p>
      </sec>
    </sec>
    <sec id="sec-5">
      <title>4. Conclusions</title>
      <p>In this study, the tree register of urban forests gives a certain baseline for the settings of the urban
tree canopy and its management. These registers are very useful for the establishment of safe species
without any risk of invasion and those with high invasion risk which -naturally- must be avoided and
excluded. Our main conclusion is that a recent checklist of Greece invasive alien flora (i.e.
https//www.alienplants.gr/taxa-checklist) can form a basis concerning the national management
strategies towards nature conservation, not to mention that by promoting the use of native species in
landscape design projects, mainly in parks and pedestrian/traffic roads we contribute to the future
creation of sustainable urban green spaces in a region, under the concept of climate change.</p>
    </sec>
    <sec id="sec-6">
      <title>5. Acknowledgements</title>
      <p>This work was financially supported by the LIFE17 GIC/GR/000029 GrIn project "Promoting Urban
Integration of Green INfrastructure to improve climate governance in cities", which is co-funded by the
European Commission under the "Climate Change Action-Climate Change Governance and
Information" component of the LIFE Programme and the Greek Green Fund.</p>
    </sec>
    <sec id="sec-7">
      <title>6. References</title>
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