<?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.2014.415082</article-id><article-id pub-id-type="publisher-id">OJE-51966</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><subject> Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Distribution and Habitat Preference of Red Panda (&lt;i&gt;Ailurus fulgens fulgens&lt;/i&gt;) in Jumla District, Nepal
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>anoj</surname><given-names>Bhatta</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>Karan</surname><given-names>Bahadur Shah</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Bhupendra</surname><given-names>Devkota</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Rajiv</surname><given-names>Paudel</given-names></name><xref ref-type="aff" rid="aff4"><sup>4</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Saroj</surname><given-names>Panthi</given-names></name><xref ref-type="aff" rid="aff5"><sup>5</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff3"><addr-line>College of Applied Science, Kathmandu, Nepal</addr-line></aff><aff id="aff2"><addr-line>Natural History Museum, Tribhuvan University, Kathmandu, Nepal</addr-line></aff><aff id="aff4"><addr-line>Winrock International, Lalitpur, Nepal</addr-line></aff><aff id="aff1"><addr-line>Amrit Science Campus, Kathmandu, Nepal</addr-line></aff><aff id="aff5"><addr-line>Department of Forests, District Forest Office, Darchula, Nepal</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>mountsaroj@gmail.com(SP)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>17</day><month>11</month><year>2014</year></pub-date><volume>04</volume><issue>15</issue><fpage>989</fpage><lpage>1001</lpage><history><date date-type="received"><day>18</day>	<month>September</month>	<year>2014</year></date><date date-type="rev-recd"><day>19</day>	<month>October</month>	<year>2014</year>	</date><date date-type="accepted"><day>4</day>	<month>November</month>	<year>2014</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>
 
 
   Reliable and sufficient information regarding status, distribution and habitat preference of red panda (Ailurus fulgens fulgens) is lacking in Nepal. The research activities on red panda in the mid-western Nepal are very limited, so the status of red panda in the region is quite unknown. The study conducted during May, 2013 in three Village Development Committees (VDCs) namely Godhemahadev, Malikathata and Tamti of Jumla district was an important step for providing vital information including distribution and habitat preference of this species. The study included the reconnaissance, key informants survey, interviews and consultation for the most potential area identification, opportunistic survey comprising the direct observation and indirect sign count method for the presence and distribution, habitat assessment consisting vegetation sampling and ocular estimation. The study revealed the presence of red panda in three forests namely Bahirepatan, Imilchadamar and Tyakot of Godhemahadev, Tamti and Malikathata VDCs respectively. The species was found distributed between 2880 and 3244 m with an average dropping encounter rate of 1.04 per hour of searching effort and 12 pellets per dropping. Red panda mostly preferred the habitat in the elevation range of 2900 - 3000 m with southwest facing steep slopes (36? - 45?), associated with water sources at the distance of ≤100 m. Trees such as Acer spp., Betula utilis and Quercus semecarpifolia, shrub species of Elaeagnus parvifolia, Drepanostachyum spp. and Jasminum humile, and the herbs like Polygonatum cirrhifolium, Fragaria nubicola and Galium asperifolium were found to be the most preferred species by red panda. The red panda preferred the habitat with dense crown coverage (&gt;20% - 100%) and 31% - 50% ground cover. Fallen logs (39%) were the most preferred substrate used for defecation.  
      
 
</p></abstract><kwd-group><kwd>Distribution</kwd><kwd> Habitat Preference</kwd><kwd> Jumla</kwd><kwd> Red Panda</kwd><kwd> Sign</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>The red panda (Ailurus fulgens), the sole representative species of the monotypic family Ailuridae, one among the two sub-species Ailurus fulgens fulgens and Ailurus fulgens styani [<xref ref-type="bibr" rid="scirp.51966-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.51966-ref2">2</xref>] , is a threatened carnivore mammal species.</p><p>Globally, red pandas are found throughout the Himalayan mountains of Nepal, India, Bhutan, Myanmar and China between 2200 and 4800 m altitude [<xref ref-type="bibr" rid="scirp.51966-ref1">1</xref>] -[<xref ref-type="bibr" rid="scirp.51966-ref8">8</xref>] . The habitat of red pandas is associated with the occurrence of subtropical and temperate forests with an exceptional case in tropical forest of Meghalaya in India [<xref ref-type="bibr" rid="scirp.51966-ref6">6</xref>] .</p><p>In Nepal, red pandas are distributed within a narrow elevation range between 2500 and 4200 m in the northern part of the country and are confirmed to occur in eight Protected Areas (PAs) including Langtang National Park and Buffer Zone (LNP and BZ) [<xref ref-type="bibr" rid="scirp.51966-ref9">9</xref>] -[<xref ref-type="bibr" rid="scirp.51966-ref11">11</xref>] , Kangchenjungha Conservation Area (KCA) [<xref ref-type="bibr" rid="scirp.51966-ref12">12</xref>] , Makalu Barun National Park and Buffer Zone (MBNP and BZ) [<xref ref-type="bibr" rid="scirp.51966-ref13">13</xref>] , Sagarmatha National Park and Buffer Zone (SNP and BZ) [<xref ref-type="bibr" rid="scirp.51966-ref14">14</xref>] , Annapurna Conservation Area (ACA) [<xref ref-type="bibr" rid="scirp.51966-ref13">13</xref>] , Dhorpatan Hunting Reserve (DHR) [<xref ref-type="bibr" rid="scirp.51966-ref15">15</xref>] -[<xref ref-type="bibr" rid="scirp.51966-ref18">18</xref>] , Rara National Park and Buffer Zone (RNP and BZ) [<xref ref-type="bibr" rid="scirp.51966-ref19">19</xref>] and Gaurishankar Conservation Area (GCA) [<xref ref-type="bibr" rid="scirp.51966-ref20">20</xref>] . Beside this, some of the studies suggested the presence of red panda outside the PAs in Nepal. The evidences of its presence have been documented in the forest patches of Illam [<xref ref-type="bibr" rid="scirp.51966-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.51966-ref22">22</xref>] , Panchthar and Taplejung [<xref ref-type="bibr" rid="scirp.51966-ref22">22</xref>] , and Sankhuwasabha [<xref ref-type="bibr" rid="scirp.51966-ref23">23</xref>] districts in the eastern Nepal. Its presence has also been recorded in Manang district, north-central part of Nepal [<xref ref-type="bibr" rid="scirp.51966-ref24">24</xref>] and Kalikot [<xref ref-type="bibr" rid="scirp.51966-ref25">25</xref>] , Jajarkot [<xref ref-type="bibr" rid="scirp.51966-ref26">26</xref>] of mid-western Nepal.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Study Area</title><p>Jumla district is situated in Karnali zone of the mid-western development region with total area, 2531 km&#178;. The district is surrounded by Dolpa district in the east, Kalikot district in the west, Mugu district in the north and Jajarkot district in the south (<xref ref-type="fig" rid="fig1">Figure 1</xref>). Jumla Khalanga is the district headquarters of Jumla district. The entire</p><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> Location map of the study area</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x6.png"/></fig><p>district is divided into nine forest Illakas, and 30 Village Development Committees (VDCs). The district can be accessed either through Surkhet-Jumla Karnali Public Highway (232 km) or via air service from Surkhet and Nepalgunj [<xref ref-type="bibr" rid="scirp.51966-ref27">27</xref>] .</p><p>Three VDCs namely Godhemahadev, Malikathata and Tamti were selected for the study purpose and the detail study has been carried out in the Bahirepatan, Tyakot and Imilchadamar forests of Godhemahadev, Malikathata and Tamti VDCs respectively.</p></sec><sec id="s2_2"><title>2.2. Distribution</title><p>We conducted the reconnaissance including the interaction with various representative offices as the key informants comprising the District Forest Office (DFO), ranger posts, District Development Committee (DDC), and VDCs. Similarly, interactions with villagers, herders, village level conservation committee through consultation meeting and focused group discussions regarding presence and distribution of red panda further helped for the exploration and identification of the potential habitats of red panda in the study area. Meanwhile, pamphlets and photographs of red panda, their pellets, habitats, and their preferred foods were displayed during the reconnaissance. For getting representative and reliable information, opportunistic sampling strategy was adopted for the survey. Both direct and indirect methods of wildlife survey were applied in the field. However, indirect sign count method was significant throughout the study period. We have collected geo-referenced with hand-held Geological Positioning System (GPS) unit wherever we observed the direct and indirect signs of the species and Arc Geographical Information System (GIS) and Google earth were used to prepare distribution map.</p></sec><sec id="s2_3"><title>2.3. Habitat Preference</title><p>Ivlev’s electivity index (IV) was used to analyze the habitat preference of red panda which includes various habitat parameters such as vegetation, slope, elevation, aspect, vegetation composition, cover and distance from nearest water sources. In addition, the value of index ranges from −1.0 to +1.0 where positive values implies preference, negative values refers avoidance and 0 values indicates random use. The formula developed by Ivlev [<xref ref-type="bibr" rid="scirp.51966-ref28">28</xref>] and followed by Yonzon and Hunter [<xref ref-type="bibr" rid="scirp.51966-ref29">29</xref>] , Panthi et al. [<xref ref-type="bibr" rid="scirp.51966-ref17">17</xref>] was used to calculate the habitat preference of red panda, which can be expressed as<inline-formula><inline-graphic xlink:href="http://html.scirp.org/file/5-1380305x7.png" xlink:type="simple"/></inline-formula>, where “A” indicates “availability plots” and “U” infers “use plots”.</p><p>Vegetation in any area indicates the habitat suitability and preference for the particular species that is core component for the habitat specialist like red panda. The detail vegetation analysis was carried out to determine the floral composition of the habitat. Quadrates of size 10 m &#215; 10 m for tree layer (plant above 3 m height and 5 cm DBH), 4 m &#215; 4 m for shrubs layer (woody plant below 3 m in height) and 1 m &#215; 1 m for herbs layer (plants up to 1 m in height) were used in both habitat use plot (U) and habitat availability plots (A). The quadrates sizes were determined as suggested by Cottam [<xref ref-type="bibr" rid="scirp.51966-ref30">30</xref>] . In each plot, number of trees, shrubs and herbs, their frequency and ground coverage were determined on the basis of ocular estimation. In addition, DBH, height and canopy coverage of trees were also recorded. The unidentified plant species were collected and taken to national herbarium and plant laboratories, Godawari, Lalitpur, Nepal, for identification and further authentication.</p></sec></sec><sec id="s3"><title>3. Results</title><sec id="s3_1"><title>3.1. Red Panda Distribution in the Study Area</title><p>Presence of red panda (locally known as “Nautoto”) was confirmed in three VDCs (Godhemahadev, Malikathata and Tamti) of Jumla district. Red panda signs (pellets) were observed in Bahirepatan, Tyakot and Imilchadamar forests of those three respective VDCs (<xref ref-type="fig" rid="fig2">Figure 2</xref>).</p><p>On 21<sup>st</sup> May 2013 (9:30 a.m.), one adult red panda was sighted in Tyakot forests of ward No. 9, Khopry, Malikathata VDC. The observed site (29˚08'36.7&quot;N, 82˚02'04.0&quot;E; 2894 m) was at southwest facing slope with 41˚ slope and at about 100 m from the nearest water source. The red panda observed at a distance of approximately 50 m was defecating at its latrine site, where freshest pellet group (about a minute after defecation) was seen above the old pellet layer. The red panda got disturbed due to presence of the observers and suddenly escaped from the site and disappeared in the bushes. The site was dominated by Abies spectabilis with Drepanostachyum falcatum understory.</p><p>Occasionally red pandas were also observed by local resident and herders in Dugurnedando, Chilaunepani and</p><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Distribution of red panda in the study area</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x8.png"/></fig><p>Chada forest areas of Ghodemahadev VDC, Tyakot forest of Malikathata VDC and Imilchadamar forest of Tamti VDC. These forests are dominated by Abies spectabilis, Quercus semecarpifolia and Picea smithiana and bamboo understory.</p><p>Red panda’s droppings were found between 2880 and 3244 m altitude in the study area. Out of 28 pellet groups, 50% of them were recorded in the Tyakot forest of Malikathata VDC followed by 28.57% in Imilchadamar of Tamti and 21.43% in Bahirepatan of Godhemahadev. The red panda defecated at a particular site considered as latrine site, consisting of two or more droppings (pellets group) above the older one, however, the single dropping encountered in a plot was considered as the defecation site. In the studied plots, percentage of defecation site (85.71%) was higher than that of latrine site (14.29%). Single defecation site consisted of 7 to 18 pellets. However, average number of pellets per dropping in defecation site was 12. The number of pellets in the latrine sites could not be counted, due to higher number of broken and decayed pellets. Furthermore, an encounter rate of pellet group/hour searching effort was used as an index in order to quantify the abundance in the study area. The average droppings encounter rate in the studied forests was found to be 1.04 per hour of walk (searching effort), including highest in Tyakot forest of Malikathata VDC (1.56/hour searching effort) followed by Imilachdamar of Tamti VDC (0.89/hour searching effort) and Bahirepatan of Godhemahave VDC (0.67/hour of searching effort).</p></sec><sec id="s3_2"><title>3.2. Habitat Preference by Red Panda</title><sec id="s3_2_1"><title>3.2.1. Elevation</title><p>Evidences of red panda’s presence were observed between 2800 m and 3300 m elevation. Red panda highly preferred the altitudinal range of 2900 - 3000 m (IV = 0.20), moderately preferred the elevation of 3000 - 3100 m (IV = 0.17) followed by 3100 - 3200 m (IV = 0.14) and 2800 - 2900 m (IV = 0.09) and randomly used the altitude of 3200 - 3300 m. Red panda completely avoided the area below 2800 m and above 3300 m altitude with IV = −1.00 each (<xref ref-type="fig" rid="fig3">Figure 3</xref>).</p></sec><sec id="s3_2_2"><title>3.2.2. Slope</title><p>Slope of the red panda habitat was classified according to slope category provided by Anbalagan and Singh [<xref ref-type="bibr" rid="scirp.51966-ref31">31</xref>] . Red panda signs (pellets) were observed between the slope of 15˚ and 56˚. Red panda mostly preferred steep slope (IV = 0.14, 37.50%), moderately preferred escarpment/cliff (IV = 0.06, 30.36%), randomly used moderate</p><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Elevation preference by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x9.png"/></fig><p>slope (IV = 0.00, 21.43%) and avoided the gentle slope (IV = −0.05, 7.14%). However, red panda completely avoided very gentle slope (3.57%) (<xref ref-type="fig" rid="fig4">Figure 4</xref>).</p></sec><sec id="s3_2_3"><title>3.2.3. Aspect</title><p>Red panda mostly preferred southwest facing slopes (IV = 0.12, 44.64%), moderately preferred northwest facing slopes (IV = 0.07, 26.79%), and randomly used northeast facing slopes (IV = 0.00, 14.29%). However, red panda avoided Southeast facing slopes (IV = −0.50, 14.29%) in the area (<xref ref-type="fig" rid="fig5">Figure 5</xref>).</p></sec><sec id="s3_2_4"><title>3.2.4. Water Source</title><p>Red panda signs were found at the distance of 5 m to 350 m far from the nearest water sources in the study area. The species mostly preferred the distance &#163;100 m (IV = 0.13) from the water sources followed by distance (101 - 200) m (IV = −0.08) whereas, it avoided the distance greater than 200 m (IV = −0.45), from nearest water sources (<xref ref-type="fig" rid="fig6">Figure 6</xref>).</p></sec><sec id="s3_2_5"><title>3.2.5. Substrate</title><p>The different substrates used by red panda for defecation were fallen logs, ground (forest floor), uprooted trees and rock cliffs. Fallen logs were mostly preferred for defecation (39%) followed by forest floor (25%), uprooted trees (25%) and rock cliffs (11%) (<xref ref-type="fig" rid="fig7">Figure 7</xref>).</p></sec><sec id="s3_2_6"><title>3.2.6. Floristic Preference</title><p>1) Trees</p><p>Tree species were examined in 56 plots (28 habitat use plots and 28 habitat availability plots) each 10 m &#215; 10 m in size. Out of nine tree species recorded, red panda showed higher preference to Acer spp. (IVI = 27.14; IV = 0.35) followed by Betula utilis (IVI = 26.91; IV = 0.24) and Quercus semecarpifolia (IVI = 55.29; IV = 0.13). Abies spectabilis (IVI = 54.85; IV = 0.00) was randomly used whereas Tsuga dumosa, Juglans regia, Picea smithiana and Pinus wallichiana were avoided by red panda (<xref ref-type="table" rid="table1">Table 1</xref>).</p><p>2) Shrubs</p><p>Shrubs were examined in 56 plots (28 habitat use plots and 28 habitat availability plots) each of 4 m &#215; 4 m area. A total of 19 shrub species found in the red panda habitat, eight species were preferred, two species were randomly used and remaining were avoided by red panda. Red panda highly preferred Elaeagnus parvifolia (IV = 0.40) followed by Drepanostachyum falcatum (IV = 0.10), Drepanostachyum intermedium (IV = 0.06) and Drepanostachyum Khasianum (IV = 0.04) whereas Ribes himalense (IV = 0.00) and Viburnum cotinifolium (IV = 0.00) were randomly used. However, shrubs like Coriaria nepalensi (IV = −1.00), Prinsepia utilis (IV = −0.42), Salix denticulate (IV = −0.41) and Rosa macrophylla (IV = −0.37) were highly avoided (<xref ref-type="table" rid="table2">Table 2</xref>).</p><p>3) Herbs</p><p>Herbaceous plants were observed in 56 plots (28 habitat use plots and 28 habitat availability plots) each 1 m &#215; 1 m in area. A total of 17 herbaceous plants were observed in these plots, eight of them were preferred by red panda. Polygonatum cirrhifolium (IV = 0.32) was most preferred species followed by Fragaria nubicola (IV =</p><fig id="fig4"  position="float"><label><xref ref-type="fig" rid="fig4">Figure 4</xref></label><caption><title> Slope preference by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x10.png"/></fig><fig id="fig5"  position="float"><label><xref ref-type="fig" rid="fig5">Figure 5</xref></label><caption><title> Aspect preference by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x11.png"/></fig><fig id="fig6"  position="float"><label><xref ref-type="fig" rid="fig6">Figure 6</xref></label><caption><title> Preference of distance from water sources by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x12.png"/></fig><fig id="fig7"  position="float"><label><xref ref-type="fig" rid="fig7">Figure 7</xref></label><caption><title> Percentage of substrate used by red panda for defecation (n = 28)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x13.png"/></fig><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Tree species according to preference by red panda</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >S.N.</th><th align="center" valign="middle" >Scientific name</th><th align="center" valign="middle" >Family</th><th align="center" valign="middle" >Local name</th><th align="center" valign="middle" >IVI</th><th align="center" valign="middle" >IV</th><th align="center" valign="middle" >Status</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Acer spp.</td><td align="center" valign="middle" >Aceraceae</td><td align="center" valign="middle" >Paalau</td><td align="center" valign="middle" >27.14</td><td align="center" valign="middle" >0.35</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Betula utilis</td><td align="center" valign="middle" >Betulaceae</td><td align="center" valign="middle" >Bhuje</td><td align="center" valign="middle" >26.91</td><td align="center" valign="middle" >0.24</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >Quercus semecarpifolia</td><td align="center" valign="middle" >Fagaceae</td><td align="center" valign="middle" >Khasru</td><td align="center" valign="middle" >55.29</td><td align="center" valign="middle" >0.13</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Abies spectabilis</td><td align="center" valign="middle" >Pinaceae</td><td align="center" valign="middle" >Gobrya</td><td align="center" valign="middle" >54.85</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >Randomly Used</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Pinus wallichiana</td><td align="center" valign="middle" >Pinaceae</td><td align="center" valign="middle" >Piu Sallo</td><td align="center" valign="middle" >30.64</td><td align="center" valign="middle" >−0.17</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >Picea smithiana</td><td align="center" valign="middle" >Pinaceae</td><td align="center" valign="middle" >Jhulya</td><td align="center" valign="middle" >35.8</td><td align="center" valign="middle" >−0.21</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >Rhododendron arboreum</td><td align="center" valign="middle" >Ericaceae</td><td align="center" valign="middle" >Guraunsh</td><td align="center" valign="middle" >17.26</td><td align="center" valign="middle" >−0.27</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >Juglans regia</td><td align="center" valign="middle" >Juglandaceae</td><td align="center" valign="middle" >Oakhar</td><td align="center" valign="middle" >23.28</td><td align="center" valign="middle" >−0.4</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >9</td><td align="center" valign="middle" >Tsuga dumosa</td><td align="center" valign="middle" >Pinaceae</td><td align="center" valign="middle" >Thigo</td><td align="center" valign="middle" >28.84</td><td align="center" valign="middle" >−0.52</td><td align="center" valign="middle" >Avoided</td></tr></tbody></table></table-wrap><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Shrub species according to preference by red panda</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >S.N.</th><th align="center" valign="middle" >Scientific name</th><th align="center" valign="middle" >Family</th><th align="center" valign="middle" >Local name</th><th align="center" valign="middle" >IV</th><th align="center" valign="middle" >Status</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Elaeagnus parvifolia</td><td align="center" valign="middle" >Elaeagnaceae</td><td align="center" valign="middle" >Gunyalo</td><td align="center" valign="middle" >0.4</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Drepanostachyum falcatum</td><td align="center" valign="middle" >Poaceae</td><td align="center" valign="middle" >Malingo</td><td align="center" valign="middle" >0.1</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >Drepanostachyum intermedium</td><td align="center" valign="middle" >Poaceae</td><td align="center" valign="middle" >Jurmutho</td><td align="center" valign="middle" >0.06</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Drepanostachyum khasianum</td><td align="center" valign="middle" >Poaceae</td><td align="center" valign="middle" >Deu Ningalo</td><td align="center" valign="middle" >0.04</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Jasminum humile</td><td align="center" valign="middle" >Oleaceae</td><td align="center" valign="middle" >Kali Sanguto</td><td align="center" valign="middle" >0.04</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >Rubus biflorus</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Aainselu</td><td align="center" valign="middle" >0.03</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >Cotoneaster microphyllus</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Ghungyaru</td><td align="center" valign="middle" >0.02</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >Cotoneaster affinis</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Raisya</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >9</td><td align="center" valign="middle" >Ribes himalense</td><td align="center" valign="middle" >Grossulariaceae</td><td align="center" valign="middle" >Pangro</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >Randomly Used</td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" >Viburnum cotinifolium</td><td align="center" valign="middle" >Sambucaceae</td><td align="center" valign="middle" >Banchhudo</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >Randomly Used</td></tr><tr><td align="center" valign="middle" >11</td><td align="center" valign="middle" >Philadelphus tomentosus</td><td align="center" valign="middle" >Hydrangeaceae</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >−0.16</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >12</td><td align="center" valign="middle" >Sabia campanulata</td><td align="center" valign="middle" >Sabiaceae</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >−0.25</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >13</td><td align="center" valign="middle" >Berberis aristata</td><td align="center" valign="middle" >Berberidaceae</td><td align="center" valign="middle" >Chutto</td><td align="center" valign="middle" >−0.27</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >14</td><td align="center" valign="middle" >Unidentified</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >Pitaielo</td><td align="center" valign="middle" >−0.28</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >15</td><td align="center" valign="middle" >Unidentified</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >Chellelya</td><td align="center" valign="middle" >−0.3</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >16</td><td align="center" valign="middle" >Rosa macrophylla</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Kuiyeshi</td><td align="center" valign="middle" >−0.37</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >17</td><td align="center" valign="middle" >Salix denticulata</td><td align="center" valign="middle" >Salicaceae</td><td align="center" valign="middle" >Baish</td><td align="center" valign="middle" >−0.41</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >18</td><td align="center" valign="middle" >Prinsepia utilis</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Dhatenlo</td><td align="center" valign="middle" >−0.42</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >19</td><td align="center" valign="middle" >Coriaria nepalensis</td><td align="center" valign="middle" >Coriariaceae</td><td align="center" valign="middle" >Machaino</td><td align="center" valign="middle" >−1</td><td align="center" valign="middle" >Avoided</td></tr></tbody></table></table-wrap><p>NA = not available.</p><p>0.27) and Galium asperifolium (IV = 0.22) whereas Hemiphragma heterophyllum (IV = −1.00) and Urtica dioica (IV = −1.00) were the most avoided herbaceous plant species including Artemisia dubia (IV = −0.29) (<xref ref-type="table" rid="table3">Table 3</xref>).</p></sec><sec id="s3_2_7"><title>3.2.7. Cover</title><p>1) Crown cover</p><p>Red panda preferred the dense coverage (IV = 0.28) only. A red panda observed during the field work was also in the dense crown coverage category. All other cover classes found in the area i.e. sparse (IV = −1.00), open (IV = −0.50) and moderate (IV = −0.47) were found to be avoided by the species (<xref ref-type="fig" rid="fig8">Figure 8</xref>).</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Herb species according to preference by red panda</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >S.N.</th><th align="center" valign="middle" >Scientific name</th><th align="center" valign="middle" >Family</th><th align="center" valign="middle" >Local name</th><th align="center" valign="middle" >IV</th><th align="center" valign="middle" >Status</th></tr></thead><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Polygonatum cirrhifolium</td><td align="center" valign="middle" >Liliaceae</td><td align="center" valign="middle" >Khiraunle</td><td align="center" valign="middle" >0.32</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Fragaria nubicola</td><td align="center" valign="middle" >Rosaceae</td><td align="center" valign="middle" >Bhui Kafal</td><td align="center" valign="middle" >0.27</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >Galium asperifolium</td><td align="center" valign="middle" >Rubiaceae</td><td align="center" valign="middle" >chittu</td><td align="center" valign="middle" >0.22</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Rumex nepalensis</td><td align="center" valign="middle" >Polygonaceae</td><td align="center" valign="middle" >Halhale</td><td align="center" valign="middle" >0.16</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Unidentified</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >Thatar</td><td align="center" valign="middle" >0.16</td><td align="center" valign="middle" >preferred</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >Ajuga lupulina</td><td align="center" valign="middle" >Labiateae</td><td align="center" valign="middle" >Bhugelo</td><td align="center" valign="middle" >0.07</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >Dryopteris sp.</td><td align="center" valign="middle" >Dryopteridaceae</td><td align="center" valign="middle" >Wunniu</td><td align="center" valign="middle" >0.07</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >Asparagus filicinus</td><td align="center" valign="middle" >Liliaceae</td><td align="center" valign="middle" >Kudilo</td><td align="center" valign="middle" >0.02</td><td align="center" valign="middle" >Preferred</td></tr><tr><td align="center" valign="middle" >9</td><td align="center" valign="middle" >Thalictrum foliolosum</td><td align="center" valign="middle" >Ranunculaceae</td><td align="center" valign="middle" >Bansuli</td><td align="center" valign="middle" >−0.03</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" >Cirsium verutum</td><td align="center" valign="middle" >Compositae</td><td align="center" valign="middle" >Thakailo</td><td align="center" valign="middle" >−0.05</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >11</td><td align="center" valign="middle" >Pleurospermum dentatum</td><td align="center" valign="middle" >Umbelliferae</td><td align="center" valign="middle" >Gunaino</td><td align="center" valign="middle" >−0.09</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >12</td><td align="center" valign="middle" >Girardinia diversifolia</td><td align="center" valign="middle" >Urticaceae</td><td align="center" valign="middle" >Allo/Thulo Sisnu</td><td align="center" valign="middle" >−0.09</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >13</td><td align="center" valign="middle" >Unidentified</td><td align="center" valign="middle" >NA</td><td align="center" valign="middle" >Bina</td><td align="center" valign="middle" >−0.14</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >14</td><td align="center" valign="middle" >Lycopodium clavatum</td><td align="center" valign="middle" >Lycopodiaceae</td><td align="center" valign="middle" >Ralo</td><td align="center" valign="middle" >−0.23</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >15</td><td align="center" valign="middle" >Artemisia dubia</td><td align="center" valign="middle" >Compositae</td><td align="center" valign="middle" >Titepati</td><td align="center" valign="middle" >−0.29</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >16</td><td align="center" valign="middle" >Hemiphragma heterophyllum</td><td align="center" valign="middle" >Scrophulariaceae</td><td align="center" valign="middle" >Nas Jhar</td><td align="center" valign="middle" >−1</td><td align="center" valign="middle" >Avoided</td></tr><tr><td align="center" valign="middle" >17</td><td align="center" valign="middle" >Urtica dioica</td><td align="center" valign="middle" >Urticaceae</td><td align="center" valign="middle" >Sisnu</td><td align="center" valign="middle" >−1</td><td align="center" valign="middle" >Avoided</td></tr></tbody></table></table-wrap><p>NA = not available.</p><fig id="fig8"  position="float"><label><xref ref-type="fig" rid="fig8">Figure 8</xref></label><caption><title> Percentage of crown coverage preference by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x14.png"/></fig><p>2) Ground cover</p><p>Red panda highly preferred 31% - 50% ground cover (IV = 0.09) followed by 51% - 100% ground cover (IV = 0.05). A red panda observed during the field work was in the 31% - 50% ground coverage category. Red panda completely avoided &#163;10% ground cover (IV = −1.00) and moderately avoided 11% - 30% cover class (IV = −0.20) (<xref ref-type="fig" rid="fig9">Figure 9</xref>).</p></sec></sec></sec><sec id="s4"><title>4. Discussion</title><p>The occurrence of red panda was found only between 2800 and 3300 m elevation in the study area, whereas it was found between 3000 and 4000 m in LNP [<xref ref-type="bibr" rid="scirp.51966-ref3">3</xref>] , between 2800 and 3650 m in KCA [<xref ref-type="bibr" rid="scirp.51966-ref12">12</xref>] , between 2800 and 3400 m in SNP [<xref ref-type="bibr" rid="scirp.51966-ref14">14</xref>] , between 2600 and 3000 m in Jamuna and Mabu VDC of Illam district in Eastern Nepal [<xref ref-type="bibr" rid="scirp.51966-ref21">21</xref>] , between 3000 and 3600 m in DHR [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] , between 3117 and 3591 m in RNP [<xref ref-type="bibr" rid="scirp.51966-ref19">19</xref>] and between 2600 and</p><fig id="fig9"  position="float"><label><xref ref-type="fig" rid="fig9">Figure 9</xref></label><caption><title> Percentage of ground coverage preference by red panda</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1380305x15.png"/></fig><p>3600 m in the Singhalila National Park Darjeeling, India [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] . Roberts and Gittleman [<xref ref-type="bibr" rid="scirp.51966-ref1">1</xref>] mentioned red panda’s distribution ranging from 2200 to 4800 in the Himalayas. The Tyakot forest of Malikathata VDC possessed highest percentage (50%) of sign evidences followed by Imilchadamar and Bahirepatan of Tamti and Ghodemahadev VDC respectively. This might be due to the less human and livestock disturbances in the Tyakot forest.</p><p>One adult red panda was sighted in Tyakot forest (29˚08'36.7&quot;N, 82˚02'04.0&quot;E; 2894 m) on southwest facing slope; similar observations were also made by Sharma and Belant [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] and Sharma [<xref ref-type="bibr" rid="scirp.51966-ref19">19</xref>] . Sighting of single red panda in the Tyakot forest (21<sup>st</sup> May 2013) might be due to the post mating period as mating season starts from middle of January and ends to early March [<xref ref-type="bibr" rid="scirp.51966-ref1">1</xref>] and red pandas are solitary outside their mating period [<xref ref-type="bibr" rid="scirp.51966-ref29">29</xref>] .</p><p>Yonzon [<xref ref-type="bibr" rid="scirp.51966-ref32">32</xref>] mentioned that the single pellet group consisted several pellets. Karki [<xref ref-type="bibr" rid="scirp.51966-ref10">10</xref>] found single dropping of red panda consisted of 10 pellets on average. However, average number of pellets per pellet group was 12 in the present study. The sign encounter rate was considered as the tool for quantifying the abundance by different researchers. This study found average red panda sign encounter rate as 1.04 per hour which is comparable to that reported by Pradhan et al. [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] in term of number of sign encountered per 100 hours. They recorded sign encounter rate in Singhalila range; the highest sign encounter rate is 105.06 &#177; 53.59 (2800 - 3100 m) followed by 20.31 &#177; 10.05 (2600 - 2800 m) and 85.00 &#177; 42.00 (3100 - 3600 m) per 100 hours.</p><p>Red pandas are known to be habitat specialists, maintain a small home range, and are restricted to small pockets of microhabitat [<xref ref-type="bibr" rid="scirp.51966-ref3">3</xref>] . In this study, red panda were found to be distributed between 2800 and 3000 m elevation with the frequency of the pellet groups increasing markedly from 2800 to 3000 m and then declining gently towards the higher elevation. No evidence of red panda’s presence was observed at the elevations &lt;2800 m and &gt;3300 m. Red panda preferred the altitudinal range of 2800 - 3300 m (<xref ref-type="fig" rid="fig3">Figure 3</xref>) with higher preference to the narrow elevation range of 3000 - 3100 m (IV = 0.20). In comparison, Pradhan et al. [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] found red panda distributed in the entire study area in Singhalila National Park with the mean altitudinal range of 2600 - 3600 m; however distribution was relatively more abundant within an altitudinal range of 2800 - 3600 m. Karki [<xref ref-type="bibr" rid="scirp.51966-ref10">10</xref>] found that the red pandas were mostly distributed within the altitudinal range of 3000 - 3200 m of Cholangpati- Dokachet Area, Langtang National Park. However, contrary to this, Sharma and Belant [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] found that, the most preferable elevation of the red panda was 3500 m and no evidences of red pandas were observed at the elevation above 3730 m. Distribution of the pellet groups within the narrow elevation range found in the present study was possibly due to the availability of habitat requirements, which is supported by the findings of Sharma and Belant [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] i.e. distribution of pellet groups appeared positively associated with the abundance of bamboos Arundinaria spp. and availability of water sources.</p><p>Red panda mostly preferred the steep slopes followed by escarpments/cliffs. Most of the pellet groups were recorded in the steep slope (IV = 0.14, 37.50%) whereas least in the very gentle slope (IV = −1.00, 3.57%). This might be to avoid the competition with the livestock; the very gentle and gentle slopes were mostly used by livestock for grazing in the study area. The signs of red panda presence were recorded mostly in the southwest facing slopes (44.64%) followed by northwest facing slopes (26.79%) indicating that southwest and northwest facing slopes are preferred slope of red panda. This might be due to the presence of habitat requisites specifically food availability for red panda. Our findings are similar to those of Karki [<xref ref-type="bibr" rid="scirp.51966-ref10">10</xref>] , who recorded that red panda mostly preferred northwest facing slopes (64%) followed by northeast (29%) while the most preferred slope was 37˚. Red Panda Network (RPN)-Nepal [<xref ref-type="bibr" rid="scirp.51966-ref33">33</xref>] found frequency of red panda sign encounter in Sacred Himalayan Landscape (SHL) of Nepal as higher between 30˚ to 70˚ slopes accounting for almost 90% of sign encountered with higher preference to steep forested terrain, with high moisture which usually observed on the north and west facing slopes.</p><p>The study in Langtang National Park, Nepal<sup> </sup>by Yonzon and Hunter [<xref ref-type="bibr" rid="scirp.51966-ref29">29</xref>] indicated that proximity to water may be the important habitat requirement because 90% of the droppings were found within 100 m of the nearest water sources. Similarly, Pradhan et al. [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] mentioned the water availability as the habitat requisite for red panda, as 79% of the evidences of the red panda were at the distance 0 - 100 m from water bodies which further reflected the importance of water in its preferred habitat sites. This is supported by the observation made by Kandel [<xref ref-type="bibr" rid="scirp.51966-ref15">15</xref>] and Dorji et al. [<xref ref-type="bibr" rid="scirp.51966-ref8">8</xref>] . Red panda mostly preferred the distance less than or equal to 100 m (IV = 0.13), moderately preferred the distance of (101 - 200) m whereas mostly avoided the distance greater than 200 m from the water sources in the present study area.</p><p>As high as 39% of pellet groups were found on fallen logs followed by forest floor and uprooted tree with 25% each and 11% on the rock cliff. In contrary to this, Pradhan et al. [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] found that, during pre-monsoon (March- May), trees (70%) were the most preferred defecation substrate for the species, this is supported by the findings of Williams [<xref ref-type="bibr" rid="scirp.51966-ref21">21</xref>] and Kandel [<xref ref-type="bibr" rid="scirp.51966-ref15">15</xref>] . Most signs observed during the study were old and most of the evidences were found in the fallen logs, forest floors and uprooted trees, probably the substrates were used during post monsoon and winter seasons. Similarly, Pradhan et al. [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] suggested that the higher use of forest floor during monsoon was probably because the red panda was seeking bamboo shoots on the forest floors. Besides, pellet groups mostly found on the forest floor, paths on ridges and slopes, could be a mode of communication between the species as winter happens to be its mating season.</p><p>The habitat of red panda is associated with the occurrence of subtropical and temperate forests with exceptional case in tropical forest of Meghalaya in India [<xref ref-type="bibr" rid="scirp.51966-ref6">6</xref>] . Based on the vegetation classification given by Shrestha [<xref ref-type="bibr" rid="scirp.51966-ref34">34</xref>] , the habitat of red panda in this study area falls within the temperate and subalpine forests.</p><p>The preferred habitat of red panda in Dhorpatan Hunting Reserve was dominated by Abies spectabilis, Rhododendron campanulatum, Betula utilis, Juniperus indica and Arundinaria spp. [<xref ref-type="bibr" rid="scirp.51966-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] . In the present study area habitat of red panda was dominated by Quercus semecarpifolia, Abies spectabilis, Betula utilis and Acer spp. Furthermore, out of nine species recorded in the study area, red panda preferred Acer spp., Betula utilis and Quercus semecarpifolia where as it randomly used Abies spectabilis and avoided Tsuga dumosa, Juglans regia, Picea smithiana and Pinus wallichiana. The present study was supported by the study conducted by Panthi et al. [<xref ref-type="bibr" rid="scirp.51966-ref17">17</xref>] who reported that the red panda showed higher preference to Acer caesium, Abies spectabilis and Quercus semecarpifolia. The preferred tree species in the study area might be used by red panda for nesting, sleeping and sheltering.</p><p>Out of 19 shrubs recorded in the study area, red panda preferred only eight species. Red panda highly preferred Elaeagnus parvifolia and Drepanostachyum spp. Red panda was found eating the leaves of both species of bamboo, Arundinaria maling and A. aristata predominantly present as understory in Singhalila National Park [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] , similar observation were also made by Yonzon and Hunter [<xref ref-type="bibr" rid="scirp.51966-ref9">9</xref>] , Karki [<xref ref-type="bibr" rid="scirp.51966-ref10">10</xref>] , Thapa [<xref ref-type="bibr" rid="scirp.51966-ref11">11</xref>] in Langtang National Park, Kandel [<xref ref-type="bibr" rid="scirp.51966-ref15">15</xref>] , Sharma and Belant [<xref ref-type="bibr" rid="scirp.51966-ref16">16</xref>] , Panthi et al. [<xref ref-type="bibr" rid="scirp.51966-ref17">17</xref>] in Dhorpatan Hunting Reserve, Sharma [<xref ref-type="bibr" rid="scirp.51966-ref19">19</xref>] in Rara National Park and Mallick [<xref ref-type="bibr" rid="scirp.51966-ref35">35</xref>] in Neora Valley National Park India. Similarly, three species of bamboo, Drepanostachyum falcatum, D. intermedium and D. khasianum were found most preferred and present as understory in the habitat of red panda in Jumla. Eight herbaceous plants including Polygonatum cirrhifolium, Fragaria nubicola, Galium asperifolium were found to be preferred by red panda. The local villagers mentioned that the study area as most potential area for the medicinal herbs and their exploitation is high.</p><p>Canopy coverage is the important habitat component in the red panda habitat and it prefers forest with greater canopy cover [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.51966-ref21">21</xref>] . In the study area, red panda preferred dense crown coverage (&gt;20% - 100%). It was probably due to crown coverage might be used for hiding, resting and thermoregulation; for the protection and maintaining body temperature within narrow tolerable limit. Panthi [<xref ref-type="bibr" rid="scirp.51966-ref36">36</xref>] also found that red panda mostly preferred the crown coverage of 51% - 75% (IV = 0.21) followed by 76% - 100% (IV = 0.08).</p><p>Red panda preferred &#179;31% - 100% ground coverage, however avoided the ground coverage &#163;30%, probably it used dense ground cover for hiding and movements. Panthi [<xref ref-type="bibr" rid="scirp.51966-ref36">36</xref>] mentioned that red panda preferred the moderate ground cover of (26% - 50%) while avoided low ground cover (&#163;25%) followed by high ground cover (&#179;51% - 100%).</p><p>Although red panda is a carnivore, it is used to pure herbivore diet, primarily consisting of leaves and shoots of bamboo species. Its other dietary includes berries, fruits, mushrooms, acorns and lichens [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.51966-ref9">9</xref>] . In addition, the annual diet of red panda comprises leaves of ringal bamboo (Jhapra and Raate) (68.4%), followed by ringal shoots (14.6%), fruits of Sorbus cuspidata (9.23%), berries of Sorbus microphylla (6.15%) and mushroom (1.6%) [<xref ref-type="bibr" rid="scirp.51966-ref7">7</xref>] . The villagers and herders of the study area mentioned that red panda mainly feeds on leaves and shoot of Drepanostachyum spp. (Jurmutho, Malingo and Deu Ningalo) and partially on fruits of Rubus biflorus (Aainselu), Cotoneaster microphyllus (Ghungyaru), Berberis aristata (Chutto), Elaeagnus parvifolia (Gunyalo) and Fragaria nubicola (Bhui Kafal). Captive red panda were observed to eat birds and have shown particular interest in sweetened food and readily consumed meat [<xref ref-type="bibr" rid="scirp.51966-ref1">1</xref>] , while the herders of study area mentioned that red panda killed and devoured the newly born young of goat and sheep, but this is doubtful and need further verification.</p></sec><sec id="s5"><title>5. Conclusion</title><p>The study revealed the presence of red panda in the Bahirepatan, Tyakot and Imilchadamar forests of Godhemahadev, Malikathata and Tamti VDCs respectively. The evidences (pellet groups) of red panda found distributed from the elevation of 2880 m to 3244 m.</p><p>Red panda mostly preferred the habitat in the elevation range from 2900 to 3000 m with southwest facing steep slopes (36˚ - 45˚), associated with water availability (at distance ≤100 m). In addition, red panda mostly preferred the tree species of Acer spp., Betula utilis and Quercus semecarpifolia, shrub species of Elaeagnus parvifolia, Drepanostachyum spp. and Jasminum humile, and herbaceous of Polygonatum cirrhifolium, Fragaria nubicola and Galium asperifolium. The red panda preferred the habitat with dense crown coverage (&gt;20% - 100%) and 31% - 50% ground cover. Moreover, fallen logs (39%) were mostly preferred to use by red panda for defecation.</p></sec><sec id="s6"><title>Acknowledgements</title><p>We are highly grateful to Red Panda Network (RPN) for financial and equipment support to conduct this study. We are obliged to College of Applied Sciences-Nepal (CAS), Nepal government’s Department of National Parks and Wildlife Conservation (DNPWC), Department of Forest (DoF) and District Forest Office (DFO), Jumla for permitting to carry out this study in Jumla district. We are thankful to Mr. Badri Baral for his tireless effort and co-operation throughout the field survey, and to the field guide Mr. Bir B. Rawat, Mr. Padam Budha and Mr. Rabi Thapa and all the local people, respondents, herders and hotel owners for their support and friendly behavior during the field survey.</p></sec><sec id="s7"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.51966-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Robert, M.S. and Gittleman, J.L. (1984) Ailurus fulgens. Mammalian Species, No. 222, 1-8.http://dx.doi.org/10.2307/3503840</mixed-citation></ref><ref id="scirp.51966-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Glatston, A.R. (1994) Status Survey and Conservation Action Plan for Procyonids and Ailurids. 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