<?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">OJMS</journal-id><journal-title-group><journal-title>Open Journal of Marine Science</journal-title></journal-title-group><issn pub-type="epub">2161-7384</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/ojms.2014.44026</article-id><article-id pub-id-type="publisher-id">OJMS-50563</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>
 
 
  Biomass and Community Structure of Epilithic Biofilm on the Yellow and East Coasts of Korea
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>o</surname><given-names>Yeon Kim</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>Seo</surname><given-names>Kyoung Park</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>Jin</surname><given-names>Suk Heo</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>Han</surname><given-names>Gil Choi</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Young</surname><given-names>Sik Kim</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>Ki</surname><given-names>Wan Nam</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib></contrib-group><aff id="aff1"><addr-line>Faculty of Biological Science and Institute of Basic Natural Sciences, Wonkwang University, Iksan, Korea</addr-line></aff><aff id="aff3"><addr-line>Department of Marine Biology, Pukyong National University, Busan, Korea</addr-line></aff><aff id="aff2"><addr-line>School of Marine Life Science, Kunsan National University, Kunsan, Korea</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>hgchoi@wku.ac.kr(HGC)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>15</day><month>10</month><year>2014</year></pub-date><volume>04</volume><issue>04</issue><fpage>286</fpage><lpage>297</lpage><history><date date-type="received"><day>13</day>	<month>August</month>	<year>2014</year></date><date date-type="rev-recd"><day>14</day>	<month>September</month>	<year>2014</year>	</date><date date-type="accepted"><day>25</day>	<month>September</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>
 
 
  Spatial biomass variation and community structure of epilithic biofilms were examined using cell counts, chlorophyll 
  a extraction, and remote-sensing techniques. Samples were collected at two levels of wave exposure along the Yellow and East Coasts of Korea in December 2010. Cyanobacteria were dominant, occupying about 88% of biofilm, irrespective of wave exposure levels. The cyanobacteria species, 
  Aphanotece spp. was abundant in the Yellow Coast location and 
  Lyngbya spp. was abundant in the East coast location. The representative diatoms were 
  Navicula spp. and 
  Achnanthes spp. on the rocky shores of all study sites. Average Normalized Difference Vegetation Index (NDVI) was significantly greater in the Yellow Coast (mean 0.46) than that in the East Coast (mean 0.21); a similar pattern was observed in Vegetation Index (VI). Chlorophyll 
  a content was three times greater on the Yellow Coast (20.50 μg/cm&lt;sup&gt;2&lt;/sup&gt;) than that on the East Coast (8.21 μg/cm&lt;sup&gt;2&lt;/sup&gt;), and it was greater at the Gosapo and Bangpo shore sites than that at the Gyeokpo site, on the Yellow Coast. However, chlorophyll 
  a contents were not different between 23.33
  <sup> </sup>and 17.66 μg/cm&lt;sup&gt;2&lt;/sup&gt; at exposed- and sheltered-shores of Yellow Coast, and were 9.62 μg/cm&lt;sup&gt;2&lt;/sup&gt; and 6.80 μg/cm&lt;sup&gt;2&lt;/sup&gt; on the East Coast. Vegetation indices were positively correlated with chlorophyll 
  a contents. 
  In conclusion, biofilm of Korean upper rocky shore was mainly composed of cyanobacteria and biofilm biomass that differed between the Yellow and East Coast.
 
</p></abstract><kwd-group><kwd>Biomass</kwd><kwd> Community Structure</kwd><kwd> Epilithic Biofilm</kwd><kwd> NDVI and VI</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Epilithic biofilms are important functional components of the coastal ecosystem as a primary producer, promoter of larval settlement, and food resources for herbivorous animals [<xref ref-type="bibr" rid="scirp.50563-ref1">1</xref>] -[<xref ref-type="bibr" rid="scirp.50563-ref5">5</xref>] . They are comprised of variable assemblages of cyanobacteria, diatoms, euglenoids, bacteria, and macroalgal germlings. Studies of the intertidal epilithic biofilms have been concerned with the patterns of temporal and small scale spatial distribution [<xref ref-type="bibr" rid="scirp.50563-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref7">7</xref>] .</p><p>Environmental factors including temperature and wave action influence the community structures and biomass of the epilithic biofilms [<xref ref-type="bibr" rid="scirp.50563-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref5">5</xref>] . In coastal areas of the United Kingdom, epilithic biofilms are dominated by diatoms or cyanobacteria with maximal biomass between winter and early spring [<xref ref-type="bibr" rid="scirp.50563-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref9">9</xref>] , while, biofilms growing on tropical rocky shores are mainly composed of cyanobacteria, with the greatest biomass in the winter [<xref ref-type="bibr" rid="scirp.50563-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref11">11</xref>] . Also, biofilm biomass can differ along the tidal heights, peaking in the mid littoral zone and being the lowest in the supralittoral zone [<xref ref-type="bibr" rid="scirp.50563-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>] . Wave exposure levels affect the distribution and abundance of intertidal seaweeds and animals and it is well known [<xref ref-type="bibr" rid="scirp.50563-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref14">14</xref>] . However, in the sole study of wave exposure levels of epilithic biofilms study [<xref ref-type="bibr" rid="scirp.50563-ref15">15</xref>] , biomass was greater on exposed shores than that on sheltered shores.</p><p>In Korea, no study has examined the community structure and biomass of epilithic, even though they have great importance in the coastal ecosystem. The Yellow and East Coasts of Korea are temperate regions that have different environmental conditions. Seawater temperature of the Yellow Sea is usually high because of shallow, calm, and markedly variable tidal range of about 6 - 7 m, which results in less splashing during the ebb tide. In contrast, the East Coast is exposed and deep, which results in great wave action, cold seawater, and small tidal range of approximately 30 cm.</p><p>The present study addressed two hypotheses. First, epilithic biofilm biomass is greater on wave-exposed shores than that on sheltered shores, irrespective of the coastal location. Second, cyanobacteria are more abundant on sheltered shore locales, such as the relatively sheltered Yellow Coast, which are less humid than the more wave-exposed shores of the East Coast.</p></sec><sec id="s2"><title>2. Materials and Methods</title><p>Sample collections were conducted at three rocky shores on each coast from December 12-22, 2010. Six sampling sites were located near a harbor (<xref ref-type="table" rid="table1">Table 1</xref>, <xref ref-type="fig" rid="fig1">Figure 1</xref>). From each site, microbial biofilms adherent to rock chips were collected at outside area (exposed) and inside area (sheltered) of the harbor with different degrees of wave exposure. From each exposed and sheltered area, 10 chips with surface areas of 5 - 15 cm<sup>2</sup> were obtained using a chisel and hammer, and were transferred to the laboratory. The chips were sprayed with seawater occasionally and exposed to air at room temperature (ca. 20˚C) for several hours. Three chips were used to examine biofilm assemblages and the remaining seven chips from each site were used to extract chlorophyll a for estimation of biomass.</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Sampling sites, rock types, and average values (&#177;SE, n = 7) of Normalized Difference Vegetation Index (NDVI) and Vegetation Index (VI) on rock chips which are obtained at exposed and sheltered areas of the Yellow and East Coast in Korea</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Station</th><th align="center" valign="middle" >Location</th><th align="center" valign="middle" >Rock type</th><th align="center" valign="middle" >Exposure</th><th align="center" valign="middle" >NDVI</th><th align="center" valign="middle" >VI</th></tr></thead><tr><td align="center" valign="middle" >Yellow Coast</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Gosapo</td><td align="center" valign="middle" >35˚39'N, 126˚30'E</td><td align="center" valign="middle" >Sandstone</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.50 &#177; 0.03</td><td align="center" valign="middle" >3.26 &#177; 0.34</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.42 &#177; 0.04</td><td align="center" valign="middle" >3.06 &#177; 0.28</td></tr><tr><td align="center" valign="middle" >Gyeokpo</td><td align="center" valign="middle" >35˚38'N, 126˚27'E</td><td align="center" valign="middle" >Slate</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.36 &#177; 0.04</td><td align="center" valign="middle" >2.26 &#177; 0.25</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.34 &#177; 0.03</td><td align="center" valign="middle" >2.21 &#177; 0.19</td></tr><tr><td align="center" valign="middle" >Bangpo</td><td align="center" valign="middle" >36˚30'N, 126˚30'E</td><td align="center" valign="middle" >Slate</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.49 &#177; 0.04</td><td align="center" valign="middle" >3.22 &#177; 0.46</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.47 &#177; 0.03</td><td align="center" valign="middle" >2.98 &#177; 0.27</td></tr><tr><td align="center" valign="middle" >East Coast</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Yangyang</td><td align="center" valign="middle" >37˚58'N, 128˚45'E</td><td align="center" valign="middle" >Granite gneiss</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.36 &#177; 0.03</td><td align="center" valign="middle" >2.13 &#177; 0.08</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.27 &#177; 0.03</td><td align="center" valign="middle" >1.99 &#177; 0.10</td></tr><tr><td align="center" valign="middle" >Sacheon</td><td align="center" valign="middle" >37˚50'N, 128˚52'E</td><td align="center" valign="middle" >Granite gneiss</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.39 &#177; 0.04</td><td align="center" valign="middle" >2.39 &#177; 0.15</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.28 &#177; 0.02</td><td align="center" valign="middle" >1.95 &#177; 0.06</td></tr><tr><td align="center" valign="middle" >Anin</td><td align="center" valign="middle" >37˚44'N, 128˚59'E</td><td align="center" valign="middle" >Schist</td><td align="center" valign="middle" >Exposed</td><td align="center" valign="middle" >0.38 &#177; 0.06</td><td align="center" valign="middle" >2.48 &#177; 0.27</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Sheltered</td><td align="center" valign="middle" >0.25 &#177; 0.05</td><td align="center" valign="middle" >1.80 &#177; 0.22</td></tr></tbody></table></table-wrap><fig id="fig1"  position="float"><label><xref ref-type="fig" rid="fig1">Figure 1</xref></label><caption><title> A map of the study sites on the Yellow and East Coasts of Korea</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1470153x6.png"/></fig><sec id="s2_1"><title>2.1. Reflectance</title><p>To ascertain whether non-destructive remote-sensing techniques could replace destructive chlorophyll a extract method for quantifying the biomass of epilithic biofilms, the correlation between chlorophyll a contents and the normalized difference vegetation index (NDVI) and/or vegetation index (VI) was examined. Spectral reflectance from each of eight rock chips was measured with a spectroradiometer (USB2000, Ocean Optics, USA). Reflectance was determined from the light spectrum from the rock chips, normalized to the spectrum reflected from a reference white panel. A reflectance spectrum measured in the darkness was subtracted from the sample and the white reference spectra to remove machine dark current noise. In the present study, reflectance was first used to estimate the biomass of epilithic biofilms, even though the techniques have been occasionally used for biomass measurement of microphytobenthos by calculating NDVI and VI [<xref ref-type="bibr" rid="scirp.50563-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref17">17</xref>] :</p><disp-formula id="scirp.50563-formula393"><graphic  xlink:href="http://html.scirp.org/file/5-1470153x7.png"  xlink:type="simple"/></disp-formula><disp-formula id="scirp.50563-formula394"><graphic  xlink:href="http://html.scirp.org/file/5-1470153x8.png"  xlink:type="simple"/></disp-formula><p>where Infrared is the average reflectance in the range 748 - 752 nm and Red is the average reflectance of the range 673 - 677 nm.</p></sec><sec id="s2_2"><title>2.2. Chlorophyll a Concentration</title><p>After measuring the spectral reflectance, chlorophyll a of epilithic biofilm was extracted as previously described [<xref ref-type="bibr" rid="scirp.50563-ref18">18</xref>] using 100% methanol solvent. Each rock chip was placed into a wide mouth screw top jar (250 ml) and left at room temperature (ca. 20˚C) in the darkness for 8 h. Absorbance was recorded at &#197; 665 and &#197; 750 using a spectrophotometer (Libra S22, Biochrom, England). The surface area of rock chips was measured with the Image J program. Chlorophyll a concentration was calculated as follows:</p><disp-formula id="scirp.50563-formula395"><graphic  xlink:href="http://html.scirp.org/file/5-1470153x9.png"  xlink:type="simple"/></disp-formula><p>where 13.0 is a constant for methanol, &#197;<sub>net</sub> = &#197;665 − &#197;750, v = final volume of solvent, d = path length of spectrophotometer cell (usually 1 cm), and a = area of rock chip that the biofilm covered.</p></sec><sec id="s2_3"><title>2.3. Community Structure</title><p>To examine community structure, biofilm was obtained from the surface of three replicated rock chips by brushing with a toothbrush. Collected biofilm was separately placed in a Petri dish (&#216; 6 cm) containing seawater. The solutions were thoroughly mixed with a plastic pipette, identified, and microalgal cells were enumerated using a light microscope (Olympus CX41, Philippines). The biofilm was classified into the two major taxonomic groups, cyanobacteria and diatoms. Abundant species of each taxon group were further identified to the genus level by following previously described classifications [<xref ref-type="bibr" rid="scirp.50563-ref19">19</xref>] - [<xref ref-type="bibr" rid="scirp.50563-ref21">21</xref>] .</p></sec><sec id="s2_4"><title>2.4. Derivative Analysis</title><p>Epilithic biofilms with a variety of taxonomical microalgal groups present mixed spectral reflectance spectra [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>] . Many different photosynthetic pigments from different taxonomic group cells show some overlapping pigment absorption features that are subtle and difficult to differentiate using spectral reflectance. Second derivative analysis resolves some of these problematic features and allows the distinction of the different pigments in epilithic biofilms [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref22">22</xref>] . Pigment absorption features are detected in the second derivative spectra as derivative peaks where peak centers correspond to the maximum absorption wavelengths of the pigment responsible for that particular peak. Second derivative spectra were calculated as previously detailed [<xref ref-type="bibr" rid="scirp.50563-ref23">23</xref>] .</p></sec><sec id="s2_5"><title>2.5. Statistical Analyses</title><p>Statistical analyses were carried out using STATISTICA version 10.0 software. Two-way ANOVAs were used to test the effects of coast location and wave exposure levels on the cyanobacteria proportion, vegetation indices (NDVI and VI), and the chlorophyll a concentration of epilithic biofilms [<xref ref-type="bibr" rid="scirp.50563-ref24">24</xref>] . Fixed factors were coast and shore (wave exposure levels), and study sites of each coast were used as replicates. Also, two-way ANOVAs were used to test the effects of study site and shore on the NDVI, VI and chlorophyll a values of biofilms for Yellow Coast and East Coast, respectively. The significance of the differences between means was tested with the Tukey HSD test. Proportion of cyanobacteria was also analyzed with two-way ANOVA after arcsine transformation and chlorophyll a data were Log transformed before tests. Prior to analysis, homogeneity of the variance for data was tested using Cochran’s test, and data were transformed when necessary [<xref ref-type="bibr" rid="scirp.50563-ref25">25</xref>] .</p></sec></sec><sec id="s3"><title>3. Results</title><sec id="s3_1"><title>3.1. Reflectance</title><p>Average NDVI values including exposed and sheltered shores were 0.43 for the Yellow Coast and 0.33 for the East Coast; the difference was significant (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>). Also, VI values of epilithic biofilms were significantly higher on the Yellow Coast than the East Coast (2.83 vs. 2.12; <xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>). NDVI was maximal at Bangpo and minimal at Gyeokpo on the Yellow Coast, and maximal at Sacheon and minimal at Yangyang&#183;Anin on the East Coast (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>). VI was maximal at Gosapo and minimal at Gyeokpo on the Yellow Coast, and maximal at Sacheon and minimal at Yangyang on the East Coast (<xref ref-type="table" rid="table1">Table 1</xref> and <xref ref-type="table" rid="table2">Table 2</xref>).</p><p>On the rocky shore of the Yellow Coast, average NDVI values of epilithic biofilms were 0.45 and 0.41 on exposed and sheltered shores, respectively. VI values were 2.91 on exposed shores and 2.75 on sheltered shores.</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Results of two-way ANOVA for the effects of coast and shore on the biomass, NDVI, and VI of epilithic biofilms collected from Yellow and the East Coast of Korea</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Factor</th><th align="center" valign="middle"  rowspan="2"  >df</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P</th><th align="center" valign="middle" >MS</th><th align="center" valign="middle" >F</th><th align="center" valign="middle" >P</th></tr></thead><tr><td align="center" valign="middle" >NDVI</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >VI</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Biomass</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >Coast</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.04</td><td align="center" valign="middle" >12.96</td><td align="center" valign="middle" >&lt;0.01</td><td align="center" valign="middle" >1.51</td><td align="center" valign="middle" >10.31</td><td align="center" valign="middle" >&lt;0.05</td><td align="center" valign="middle" >0.41</td><td align="center" valign="middle" >20.22</td><td align="center" valign="middle" >&lt;0.01</td></tr><tr><td align="center" valign="middle" >Shore</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.02</td><td align="center" valign="middle" >6.21</td><td align="center" valign="middle" >&lt;0.05</td><td align="center" valign="middle" >0.26</td><td align="center" valign="middle" >1.75</td><td align="center" valign="middle" >0.22</td><td align="center" valign="middle" >0.06</td><td align="center" valign="middle" >3.03</td><td align="center" valign="middle" >0.12</td></tr><tr><td align="center" valign="middle" >Interaction</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >1.35</td><td align="center" valign="middle" >0.28</td><td align="center" valign="middle" >0.05</td><td align="center" valign="middle" >0.34</td><td align="center" valign="middle" >0.58</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >0.91</td></tr><tr><td align="center" valign="middle" >Residuals</td><td align="center" valign="middle" >8</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >0.15</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >0.02</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr></tbody></table></table-wrap><p>NDVI and VI values showed a similar trend, being greater on exposed shores than on sheltered shores, but significant differences were only found among study sites. NDVI and VI values revealed significantly greater at Gosapo and Bangpo than at Gyeokpo (for NDVI; F<sub>1,36</sub> = 7.23, P &lt; 0.01 and for VI; F<sub>1,36</sub> = 5.55, P &lt; 0.01). On the East Coast, NDVI values were 0.38 for exposed shores and 0.28 for sheltered shores. VI values varied from 2.13 - 2.48 on exposed shores (mean 2.33) and 1.80 - 1.99 on sheltered shores (mean 1.91). NDVI and VI values were not significantly different among study sites but they were significantly different between exposed and sheltered shores (for NDVI; F<sub>1,36</sub> = 10.35, P &lt; 0.01 and for VI; F<sub>1,36</sub> = 10.11, P &lt; 0.01).</p></sec><sec id="s3_2"><title>3.2. Chlorophyll a Concentration</title><p>Chlorophyll a concentration of epilithic biofilms ranged from 11.70 - 26.60 μg/cm<sup>2</sup> on three rocky shores of the Yellow Coast, and from 7.73 - 8.63 μg/cm<sup>2</sup> on the East Coast. Average chlorophyll a content was about three times greater on the Yellow Coast (mean 20.50 μg/cm<sup>2</sup>) than on the East coast (8.21 μg/cm<sup>2</sup>) and were significantly different (<xref ref-type="table" rid="table2">Table 2</xref>). Chlorophyll a concentration was maximal at Bangpo and minimal at Gyeokpo on the Yellow Coast, and was the greatest at Sacheon and lowest at Anin of the East Coast (<xref ref-type="fig" rid="fig2">Figure 2</xref>).</p><p>On the Yellow Coast, chlorophyll a contents were significantly higher at Gosapo (23.20 μg/cm<sup>2</sup>) and Bangpo (26.60 μg/cm<sup>2</sup>) than at Gyeokpo (11.70 μg/cm<sup>2</sup>; F<sub>1,36</sub> = 21.83, P &lt; 0.001). Also, chlorophyll a contents of the Yellow Coast ranged from 14.24 - 29.40 μg/cm<sup>2</sup> (mean 23.33 μg/cm<sup>2</sup>) on exposed shores and from 9.15 - 23.79 μg/cm<sup>2</sup> (mean 17.66 μg/cm<sup>2</sup>) on sheltered shores; the difference between the exposed and sheltered shores was significant (F<sub>1,36</sub> = 8.61, P &lt; 0.01). However, there was no interaction between the study site and shore (F<sub>1,36</sub> = 0.03, P = 0.97). On the rocky shores of the East Coast, the average chlorophyll a concentration was 9.62 μg/cm<sup>2</sup></p><fig id="fig2"  position="float"><label><xref ref-type="fig" rid="fig2">Figure 2</xref></label><caption><title> Average chlorophyll a concentration (&#181;g/cm<sup>2</sup>) of epilithic biofilms collected from exposed and sheltered shores of the Yellow Coast (a) and the East Coast (b). Vertical bars represent standard errors (n = 7 replicates)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1470153x10.png"/></fig><p>(9.28 - 9.90 μg/cm<sup>2</sup>) for exposed shores and 6.80 μg/cm<sup>2 </sup>(6.18 - 7.35 μg/cm<sup>2</sup>) for sheltered shores; the difference was significant (F<sub>1,36</sub> = 7.28, P &lt; 0.05). For chlorophyll a contents, however, no difference was found among the three study sites (F<sub>1,36</sub> = 0.24, P = 0.78) and no interaction was found between the site and shore (F<sub>1,36</sub> = 0.02, P = 0.98).</p></sec><sec id="s3_3"><title>3.3. NDVI vs VI, or Chl a Contents</title><p>NDVI epilithic biofilms was positively correlated with VI and Chl a content for the total data collected from on the Yellow and East coast of Korea. Correlations between NDVI and VI were stronger and were stronger (r<sup>2</sup> = 0.98, n = 12) than between NDVI and Chl a concentration (r<sup>2</sup> = 0.71, n = 12) (<xref ref-type="fig" rid="fig3">Figure 3</xref>).</p></sec><sec id="s3_4"><title>3.4. Community Structure</title><p>Cyanobacteria were dominant, comprising 84.70% of the communities of the six study sites, with diatoms comprising 15.30%. The average proportion of cyanobacteria was 86.81% for the three sites of the Yellow Coast and 82.58% for the three sites of the East Coast. At exposed areas of the Yellow Coast, the proportion of cyanobacteria ranged from 75.21% - 84.84% (mean 80.90%) and from 90.33% - 95.25% (mean 92.73%) at sheltered areas. Cyanobacteria proportion was maximal at Gosapo and minimal at Gyeokpo. Abundance of diatoms varied from 15.16% - 24.79% (mean 19.10%) on exposed shores and from 4.75% to 9.67% (mean 7.27%) on sheltered shores, three-times greater on the exposed areas compared to sheltered sites. Some green algae of microscopic stage Ulva spp. were observed in some rock chips collected from the Yellow Coasts; they were carefully removed as much as possible.</p><p>On the rocky shores of the East Coast, cyanobacteria proportion was 88.47% (84.00% - 91.86%) at the exposed sites and 76.69% (73.32% - 79.32%) at sheltered sites. Diatoms occupied 11.53% and 23.31% on the exposed and sheltered rocky shore sites of the East Coast.</p><fig id="fig3"  position="float"><label><xref ref-type="fig" rid="fig3">Figure 3</xref></label><caption><title> Correlations between NDVI vs VI (a), and between NDVI vs Chlorophyll a contents (b) of epilithic biofilms collected from the Yellow and East coasts of Korea. Data presented in average value of seven rock chips sampled at each sampling sites on the Yellow and East coast of Korea. Vertical and horizontal bars represent standard errors</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1470153x11.png"/></fig><p>The proportion of cyanobacteria was not significantly different between the Yellow and East Coasts (F<sub>1,8</sub> = 4.12, P = 0.08), and between wave-exposed and sheltered shore (F<sub>1,8</sub> = 0.10, P = 0.75). However, interactions were found between Coast and wave-exposed levels of cyanobacteria proportion (F<sub>1,8</sub> = 30.04, P = 0.001). Such results come from reversed pattern between wave exposed and sheltered levels on the two Coasts (<xref ref-type="fig" rid="fig3">Figure 3</xref>). The cyanobacteria proportion was significantly greater on sheltered shores than on exposed shores on the Yellow Coast, but it was also higher on exposed shores than at sheltered shores on the East Coast. The relative abundance of diatoms was 13.19% on the Yellow Coast and 17.42% on the East Coast (<xref ref-type="fig" rid="fig4">Figure 4</xref>).</p><p>Cyanobacteria Aphanotece spp. was the dominant genus in the intertidal rocky shore of the Yellow Coast, whereas Lyngbya spp. was the representative genus on the East Coast. Navicula spp. and Achnanthes spp. diatoms were mainly distributed on the coastal areas of the Yellow and East Coasts.</p></sec><sec id="s3_5"><title>3.5. Derivative Analysis and Pigments</title><p>Pigments causing absorption features between 430 and 770 nm were identified by comparison with published data (<xref ref-type="table" rid="table3">Table 3</xref>). The second derivative spectrum showed several peaks and it was apparently different between</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> Present and published wavelengths of pigments showing different absorption peaks in the second derivative spectra (430 - 700 nm)</title></caption><table><tbody><thead><tr><th align="center" valign="middle"  rowspan="2"  >Peak No.</th><th align="center" valign="middle"  rowspan="2"  >Present Wavelength (nm)</th><th align="center" valign="middle"  rowspan="2"  >Pigment</th><th align="center" valign="middle"  colspan="2"  >Previous data</th></tr></thead><tr><td align="center" valign="middle" >Wavelength (nm)</td><td align="center" valign="middle" >References</td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >432</td><td align="center" valign="middle" >Chlorophyll a</td><td align="center" valign="middle" >441</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chlorophyllide a</td><td align="center" valign="middle" >444</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >420 - 430</td><td align="center" valign="middle" >Louchard et al. [<xref ref-type="bibr" rid="scirp.50563-ref27">27</xref>]</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >469</td><td align="center" valign="middle" >Chlorophyll b</td><td align="center" valign="middle" >466</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chlorophyll c</td><td align="center" valign="middle" >468</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >470</td><td align="center" valign="middle" >Louchard et al. [<xref ref-type="bibr" rid="scirp.50563-ref27">27</xref>]</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >498</td><td align="center" valign="middle" >Zeaxanthin</td><td align="center" valign="middle" >492</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Lutein</td><td align="center" valign="middle" >495</td><td align="center" valign="middle" >Louchard et al. [<xref ref-type="bibr" rid="scirp.50563-ref27">27</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >β-carotene</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Diadinoxanthin</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >541</td><td align="center" valign="middle" >Fucoxanthin</td><td align="center" valign="middle" >538</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Peridinin</td><td align="center" valign="middle" >535 - 540</td><td align="center" valign="middle" >Louchard et al. [<xref ref-type="bibr" rid="scirp.50563-ref27">27</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >19'-Butanoyloxyfucoxanthin</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >576</td><td align="center" valign="middle" >Phycoerythrin</td><td align="center" valign="middle" >572</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >574</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr><tr><td align="center" valign="middle" >6</td><td align="center" valign="middle" >597</td><td align="center" valign="middle" >Chlorophyll c</td><td align="center" valign="middle" >591</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr><tr><td align="center" valign="middle" >7</td><td align="center" valign="middle" >618</td><td align="center" valign="middle" >Phycocyanin</td><td align="center" valign="middle" >620</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >623</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr><tr><td align="center" valign="middle" >8</td><td align="center" valign="middle" >646</td><td align="center" valign="middle" >Chlorophyll a</td><td align="center" valign="middle" >643</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chlorophyll c</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chlorophyllide a</td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td></tr><tr><td align="center" valign="middle" >9, 10</td><td align="center" valign="middle" >667, 687</td><td align="center" valign="middle" >Chlorophyll a</td><td align="center" valign="middle" >676</td><td align="center" valign="middle" >Stephens et al. [<xref ref-type="bibr" rid="scirp.50563-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >Chlorophyllide a</td><td align="center" valign="middle" >680</td><td align="center" valign="middle" >Louchard et al. [<xref ref-type="bibr" rid="scirp.50563-ref27">27</xref>]</td></tr><tr><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" ></td><td align="center" valign="middle" >682</td><td align="center" valign="middle" >Murphy et al. [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>]</td></tr></tbody></table></table-wrap><fig id="fig4"  position="float"><label><xref ref-type="fig" rid="fig4">Figure 4</xref></label><caption><title> Relative abundance of the major taxonomic groups of epilithic biofilms collected from exposed (E) and sheltered (S) shores of the Yellow Coast (a) and the East Coast (b). Data are obtained from the three rock chips of each study site. The number which is written on the graph presents individual number of each taxonomic group</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1470153x12.png"/></fig><p>Yellow Coast and East Coast (<xref ref-type="fig" rid="fig5">Figure 5</xref>). The most dominant feature in the second derivative spectra was two sharp peaks at about 430 (0.011 at exposed and sheltered shores) and 680 nm (0.011 for exposed shore and 0.013 for sheltered shore) on the Yellow Coast (peak 1 and 10 in <xref ref-type="table" rid="table3">Table 3</xref>), but one peak at about 680 nm (0.007 for exposed shore and 0.004 for sheltered shore) on the East Coast. Average heights of the derivative peak at ~680 nm were 0.011 at exposed shore and 0.013 at sheltered shores of the Yellow Coast and were 0.007 and 0.004 on the East Coast (<xref ref-type="fig" rid="fig5">Figure 5</xref>).</p><p>Average second-derivative spectra of Yellow and East Coast were very variable with eight peaks at wavelengths of between 430 and 650 nm (<xref ref-type="table" rid="table3">Table 3</xref>). In the range of wavelength, three prominent chlorophyll (a, b, c) and chlorophyllide a absorption features were located at 432, 469, 597 and 646 nm (peaks 1, 2, 6 and 8, respectively). An important feature was observed at 498 nm (peak 3) indicating absorption by diadinoxanthin, a pigment found in diatoms. Average height of the derivative peak 3 was greater at exposed shores (0.0008 for the Yellow Coast and 0.002 for the East Coast) than at sheltered shores (0.0006 for the Yellow and East Coasts). Also, phycoerythrin and phycocyanin absorption features were located at 576 and 618 nm (peak 5 and 7, respectively), a pigment found in cyanobacteria. A height of peak 7 was slightly greater at sheltered shores (0.0015) of on the Yellow Coast than at other shores (0.0001) of the Yellow and East Coasts (<xref ref-type="fig" rid="fig5">Figure 5</xref>).</p><fig id="fig5"  position="float"><label><xref ref-type="fig" rid="fig5">Figure 5</xref></label><caption><title> Average reflectance spectra and second derivative spectra of epilithic biofilms collected from the Yellow Coast ((a) exposed; (b) sheltered shores) and East Coast ((c), exposed; (d), sheltered shores) between December 12 and 22, 2010 (n = 7 replicates). 1, 432 nm (chlorophyll a); 2, 465 nm (chlorophyll c); 3, 498 nm (diadinoxanthin); 4, 541 nm (fucoxanthin); 5, 576 nm (phycoerythrin); 6, 597 nm (chlorophyll c); 7, 618 nm (phycocyanin); 8, 646 nm (chlorophyll a, chlorophyll c, chlorophyllide a); 9, 667 nm (chlorophyll a), and 10, 687 nm (chlorophyllide a)</title></caption><graphic mimetype="image"   position="float"  xlink:type="simple"  xlink:href="http://html.scirp.org/file/5-1470153x13.png"/></fig></sec></sec><sec id="s4"><title>4. Discussion</title><p>Cyanobacteria were the most dominant taxon showing from 78.66% - 90.04% (mean 84.70%) of the epilithic biofilms at six study sites in Korea. However, the dominant cyanobacteria differed with a unicellular rod shaped Aphanotece spp. on the Yellow Coast and filamentous Lyngbya spp. on the East Coast of Korea. Dominance of cyanobacteria in the intertidal rocky shore of Korea is understandable because they are abundant on the rocky shore in Sydney [<xref ref-type="bibr" rid="scirp.50563-ref8">8</xref>] , and in Hong Kong [<xref ref-type="bibr" rid="scirp.50563-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref28">28</xref>] . Thus, we were interested to explore whether Aphanotece spp. and Lyngbya spp. have different eco-physiological response to the desiccation and wave-exposed stresses. In the present study, Navicula spp. and Achnanthes spp. diatoms were abundant on all rocky shores investigated, and maximal proportion of diatoms was 17.23% at Gyeokpo and 21.34% at Anin on the Yellow Coast and East Coast, respectively. The two epilithic diatoms are also commonly found in the intertidal microphytobenthos biofilm around the coasts of Yellow Sea in Korea [<xref ref-type="bibr" rid="scirp.50563-ref29">29</xref>] . The resolution of the biofouling issue requires further studies of epilithic diatoms and cyanobacteria including identification and eco-physiology.</p><p>NDVI, VI, and chlorophyll a content were not different between exposed and sheltered shores on the Yellow and East Coasts. On the Yellow Coast, however, chlorophyll a and NDVI were significantly greater at Gosapo and Bangpo, than at Gyeokpo when data was pooled for exposed and sheltered shores at each study site. Kim [<xref ref-type="bibr" rid="scirp.50563-ref30">30</xref>] reported that NDVI, VI, and chlorophyll a contents were higher at the relatively exposed Gosapo shore than at Gyeokpo shore. These patterns were also observed in Australia [<xref ref-type="bibr" rid="scirp.50563-ref8">8</xref>] , with more chlorophyll a contents on exposed shores as compared to sheltered shores. Thompson et al. [<xref ref-type="bibr" rid="scirp.50563-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref15">15</xref>] also reported greater chlorophyll a contents on exposed shores than on sheltered shores. Such patterns could be a consequence of the direct effects of wave action resulting in increased nutrient supply and photosynthetic activity [<xref ref-type="bibr" rid="scirp.50563-ref15">15</xref>] . In our study, the absence of difference of chlorophyll a contents between exposed and sheltered shore might have resulted from insufficient biofilm data or different levels of wave exposure. For future study on the abundance of epilithic biofilm, seasonal data collection and clear measurement of wave exposure levels using a dynamometer should be considered. However, present results showed that NDVI values of epilithic biofilms on the Yellow Coast (0.43) and East Coast (0.33) were significantly greater than those of microphytobenthos biofilms estimated in the tidal flats of Taean (0.06), Korea [<xref ref-type="bibr" rid="scirp.50563-ref29">29</xref>] and Tagus (0.1 - 0.4), Porotugal [<xref ref-type="bibr" rid="scirp.50563-ref31">31</xref>] .</p><p>Chlorophyll a content is typically used to estimate biofilm biomass because chlorophyll a is a reliable index of the number of microalgal cells [<xref ref-type="bibr" rid="scirp.50563-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref32">32</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref33">33</xref>] . However, chlorophyll a extraction is labor-intensive and destructive [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>] . We took advantage of a recently described remote sensing technique (spectroradiometer, vegetation index) used to quantify chlorophyll a in epilithic and benthic biofilms [<xref ref-type="bibr" rid="scirp.50563-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref22">22</xref>] . Also, derivative analysis and pigment based on reflectance data measured by spectroradiometer give us information on taxonomic group components of rocky shore biofilm. Although previous studies revealed correlations between different vegetation indices (NIR: red ratio, VI, NDVI and SAVI) and chlorophyll a contents [<xref ref-type="bibr" rid="scirp.50563-ref34">34</xref>] - [<xref ref-type="bibr" rid="scirp.50563-ref36">36</xref>] , presently NDVI was positively correlated with VI (R<sup>2</sup> = 0.98) and chlorophyll a content (R<sup>2</sup> = 0.51; <xref ref-type="fig" rid="fig4">Figure 4</xref>). Thus, vegetation indices (NDVI and VI) and reflectance data could be utilized as indices supporting chlorophyll a contents and to know taxomomical components of epilithic biofilm.</p><p>Average chlorophyll a content of epilithic biofilms was about three times greater on the Yellow Coast (20.50 μg/cm<sup>2</sup> = 205.0 mg/m<sup>2</sup>) than on the East Coast (8.21 μg/cm<sup>2</sup> = 82.1 mg/m<sup>2</sup>) in the present study. Such a difference may reflect different rock types (slate on the Yellow Coast and Granite geneiss on the East Coast), which promote different formation of biofilms. Hutchinson et al. [<xref ref-type="bibr" rid="scirp.50563-ref7">7</xref>] reported microscale spatial variations of epilithic biofilms in laboratory culture; this may be typical pattern on natural rocky shores due to variation in refuges on rough surfaces and in spatial variation in different herbivorous grazers [<xref ref-type="bibr" rid="scirp.50563-ref6">6</xref>] . Appearance of green algal species in samples from the Yellow Coast may also contribute to higher biomass of these epilithic biofilms supporting in higher second derivative at about 680 nm (<xref ref-type="fig" rid="fig5">Figure 5</xref>) as compared to those recorded from the East Coast. Finally, higher chlorophyll a contents of samples from the Yellow Coast may have resulted from the eutrophic water supply from rivers, such as the Mankyeong and Dongjin that are located near to our study site because the abundance of microalgae has been positively correlated with nutrient concentration [<xref ref-type="bibr" rid="scirp.50563-ref37">37</xref>] [<xref ref-type="bibr" rid="scirp.50563-ref38">38</xref>] . To examine the difference of biofilm biomass between the two coasts of Korea, further experiments considering the abundance of herbivorous grazers, substrate type, and detailed taxonomical classification including green algae should be done. However, it is quite interested to compare the chlorophyll a content between rocky shore and microphytobenthos around coast of Korea. In the present study, average chlorophyll a content of epilithic biofilms was 82.1 - 205.0 mg/m<sup>2</sup>, which was comparable to reported 0.24 - 32.11 mg/m<sup>2</sup> in the Saemankeum tidal flat [<xref ref-type="bibr" rid="scirp.50563-ref39">39</xref>] , 1.18 - 34.25 mg/m<sup>2</sup> at Ganghwa Island [<xref ref-type="bibr" rid="scirp.50563-ref40">40</xref>] , and 66.00 - 120.73 mg/m<sup>2</sup> at the Taean tidal flat [<xref ref-type="bibr" rid="scirp.50563-ref29">29</xref>] . The current study is the first report of the high productivity of rocky shore biofilms based on chlorophyll a content. More study is required to understand their ecological role in the food web of coastal ecosystems.</p></sec><sec id="s5"><title>5. Conclusion</title><p>Epilithic biofilm biomass estimated by chlorophyll a contents was significantly greater on the Yellow Coast (205.0 mg/m<sup>2</sup>) than that on the East Coast (82.1 mg/m<sup>2</sup>), and was higher on exposed shores than that on sheltered shores on both coasts. NDVI and VI values of epilithic biofilms showed similar trends with chlorophyll a contents, and were positively correlated. Thus, vegetation indices (NDVI and VI) and the second derivative spectrum calculated from reflectance data also could be utilized as indices supporting chlorophyll a contents and to estimate taxomomical components of epilithic biofilm. Cyanobacteria were the dominant taxon in epilithic biofilms, comprising 84.70% of the communities at the six study sites. Cyanobacteria proportion was significantly greater at sheltered shores than that at exposed shores of the Yellow Coast, but was also higher at exposed shores compared to that at sheltered shores on the East Coast. It is also important that cyanobacteria Aphanotece spp. was the dominant on the Yellow Coast, whereas Lyngbya spp. was the representative genus on the East Coast. Chlorophyll a content of epilithic biofilms was pronounced as compared to that of microphytobenthos at other sites in other studies. The present results are the first report of the high productivity of rocky shore biofilms based on chlorophyll a content.</p></sec><sec id="s6"><title>Acknowledgements</title><p>This research was financially supported by Basic Science Research Program through the National Research Foundation of Korea (NRF) funded by the Ministry of Education, Science and Technology (NRF-2011-0012519) and was also partially supported by a grant from Marine Biotechnology Program Funded by Ministry of Ocean and Fisheries of Korean Government.</p></sec><sec id="s7"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.50563-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Underwood, A.J. (1984) The Vertical-Distribution and Seasonal Abundance of Intertidal Microalgae on a Rocky Shore in New South Wales. 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