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<article xmlns:xlink="http://www.w3.org/1999/xlink" xml:lang="en" article-type="research-article">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">MD</journal-id>
<journal-title>Marine Drugs</journal-title>
<abbrev-journal-title>MD</abbrev-journal-title>
<issn pub-type="epub">1660-3397</issn>
<publisher>
<publisher-name>Molecular Diversity Preservation International</publisher-name></publisher></journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3390/md8092480</article-id>
<article-id pub-id-type="publisher-id">marinedrugs-08-02480</article-id>
<article-categories>
<subj-group>
<subject>Article</subject></subj-group></article-categories>
<title-group>
<article-title>Nature and Lability of Northern Adriatic Macroaggregates</article-title></title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Faganeli</surname><given-names>Jadran</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref><xref ref-type="corresp" rid="c1-marinedrugs-08-02480">*</xref></contrib>
<contrib contrib-type="author">
<name><surname>Mohar</surname><given-names>Bojana</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Kofol</surname><given-names>Romina</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Pavlica</surname><given-names>Vesna</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Marinšek</surname><given-names>Tjaša</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Rozman</surname><given-names>Ajda</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Kovač</surname><given-names>Nives</given-names></name><xref ref-type="aff" rid="af1-marinedrugs-08-02480">1</xref></contrib>
<contrib contrib-type="author">
<name><surname>Vuk</surname><given-names>Angela Šurca</given-names></name><xref ref-type="aff" rid="af2-marinedrugs-08-02480">2</xref></contrib></contrib-group>
<aff id="af1-marinedrugs-08-02480">
<label>1</label> Marine Biological Station, National Institute of Biology, 6330 Piran, Slovenia; E-Mails: <email>moharbojana@yahoo.co.uk</email> (B.M.); <email>rkofol@gmail.com</email> (R.K.); <email>vesna.pavlica@gmail.com</email> (V.P.); <email>tjasa.marinsek@gmail.com</email> (T.M.); <email>ajdaroz@yahoo.co.uk</email> (A.R.); <email>kovac@mbss.org</email> (N.K.)</aff>
<aff id="af2-marinedrugs-08-02480">
<label>2</label> National Institute of Chemistry, Hajdrihova 19, 1000 Ljubljana, Slovenia; E-Mail: <email>angela.surca.vuk@ki.si</email></aff>
<author-notes>
<corresp id="c1-marinedrugs-08-02480">*Author to whom correspondence should be addressed; E-Mail: <email>Jadran.Faganeli@mbss.org</email>; Tel.: +386-5-923-2911; Fax: +386-5-671-2902.</corresp></author-notes>
<pub-date pub-type="collection">
<year>2010</year></pub-date>
<pub-date pub-type="epub">
<day>6</day>
<month>9</month>
<year>2010</year></pub-date>
<volume>8</volume>
<issue>9</issue>
<fpage>2480</fpage>
<lpage>2492</lpage>
<history>
<date date-type="received">
<day>22</day>
<month>7</month>
<year>2010</year></date>
<date date-type="rev-recd">
<day>30</day>
<month>8</month>
<year>2010</year></date>
<date date-type="accepted">
<day>3</day>
<month>9</month>
<year>2010</year></date></history>
<permissions>
<copyright-statement>© 2010 by the authors; licensee Molecular Diversity Preservation International, Basel, Switzerland</copyright-statement>
<copyright-year>2010</copyright-year>
<license license-type="open-access" xlink:href="http://creativecommons.org/licenses/by/3.0">
<p>This article is an open-access article distributed under the terms and conditions of the Creative Commons Attribution license (http://creativecommons.org/licenses/by/3.0/).</p></license></permissions>
<abstract>
<p>The key organic constituents of marine macroaggregates (macrogels) of prevalently phytoplankton origin, periodically occurring in the northern Adriatic Sea, are proteins, lipids and especially polysaccharides. In this article, the reactivity of various macroaggregate fractions in relation to their composition in order to decode the potentially »bioavailable« fractions is summarized and discussed. The enzymatic hydrolysis of the macroaggregate matrix, using α-amylase, β-glucosidase, protease, proteinase and lipase, revealed the simultaneous degradation of polysaccharides and proteins, while lipids seem largely preserved. In the fresh surface macroaggregate samples, a pronounced degradation of the α-glycosidic bond compared to β-linkages. Degradation of the colloidal fraction proceeded faster in the higher molecular weight (MW) fractions. <italic>N</italic>-containing polysaccharides can be important constituents of the higher MW fraction while the lower MW constituents can mostly be composed of poly- and oligosaccharides. Since the polysaccharide component in the higher MW fraction is more degradable compared to <italic>N</italic>-containing polysaccharides, the higher MW fraction represents a possible path of organic nitrogen preservation. Enzymatic hydrolysis, using α-amylase and β-glucosidase, revealed the presence of α- and β-glycosidic linkages in all fractions with similar decomposition kinetics. Our results indicate that different fractions of macroaggregates are subjected to compositional selective reactivity with important implications for macroaggregate persistence in the seawater column and deposition.</p></abstract>
<kwd-group>
<kwd>marine macroaggregates</kwd>
<kwd>lability</kwd>
<kwd>northern Adriatic</kwd></kwd-group></article-meta></front>
<body>
<sec sec-type="intro">
<title>1. Introduction</title>
<p>The northern Adriatic “mucilage phenomena”, or mucous macroaggregates, usually develop in late spring or early summer. Although their formation is not yet completely understood, these events seems to be significantly linked to preceding changes of the seawater inorganic N/P ratio [<xref ref-type="bibr" rid="b1-marinedrugs-08-02480">1</xref>,<xref ref-type="bibr" rid="b2-marinedrugs-08-02480">2</xref>] which can influence the rate of phytoplankton growth and phytoplankton metabolism inducing the production of mucilaginous material [<xref ref-type="bibr" rid="b3-marinedrugs-08-02480">3</xref>–<xref ref-type="bibr" rid="b5-marinedrugs-08-02480">5</xref>]. The phytoplankton origin is also indicated by mucilage composition, mostly composed of heteropolysaccharides produced by phytoplankton exudation [<xref ref-type="bibr" rid="b6-marinedrugs-08-02480">6</xref>] and cell lyisis [<xref ref-type="bibr" rid="b7-marinedrugs-08-02480">7</xref>]. Microscopic observations [<xref ref-type="bibr" rid="b7-marinedrugs-08-02480">7</xref>–<xref ref-type="bibr" rid="b11-marinedrugs-08-02480">11</xref>] indicate diatoms as their crucial producers although other phytoplankton species and bacteria are also present in macroaggregates. Concentrations of nutrients present during the marked retention of freshened waters and water column stratification in the northern Adriatic [<xref ref-type="bibr" rid="b12-marinedrugs-08-02480">12</xref>] seem to be less critical for mucous formation. Specific oceanographic conditions, including the formation of a gyre, higher seawater residence time, and development of a marked pycnocline during stable summer conditions with low turbulent shear [<xref ref-type="bibr" rid="b13-marinedrugs-08-02480">13</xref>], significantly contribute to the subsequent concentration and agglomeration of macromolecular organic matter, phytoplankton cells and other organics and minerals. The aggregation process can be explained by polymer gel theory [<xref ref-type="bibr" rid="b14-marinedrugs-08-02480">14</xref>] through the formation of nanogels, later microgels which continue to aggregate into macrogels and POM [<xref ref-type="bibr" rid="b15-marinedrugs-08-02480">15</xref>,<xref ref-type="bibr" rid="b16-marinedrugs-08-02480">16</xref>]. Macroaggregates represent basically the transition from colloidal organic matter (COM, macromolecules) into macrogels and particulate organic matter (POM). Their gel-like nature is manifested by a high content of water, sometimes exceeding 95%, and organic matter which represents about 35–57% of dry mass. The organic component is mostly composed of carbohydrates (12–34%), proteins (1–12%) and lipids (0.1–8%)[<xref ref-type="bibr" rid="b17-marinedrugs-08-02480">17</xref>] and the inorganic fraction is predominantly composed of quartz, calcite and clays. The latter generally results from the scavenging and inclusion of autochthonous and allochthonous particles [<xref ref-type="bibr" rid="b11-marinedrugs-08-02480">11</xref>] from the ambient seawater. The association of inorganic and organic particles [<xref ref-type="bibr" rid="b18-marinedrugs-08-02480">18</xref>] and that of colloids with cations [<xref ref-type="bibr" rid="b15-marinedrugs-08-02480">15</xref>] probably contributes to the stabilization and persistence of those macrogels in the aquatic environment.</p>
<p>Mucous macroaggregates can be observed in various forms, in the surface layer, in the water column and on the seabed. Their different color, size and shape depends on their biological and chemical composition, maturation stage, <italic>i.e.</italic>, age, basic water-column characteristics and environmental conditions, as well as local hydrodynamics [<xref ref-type="bibr" rid="b9-marinedrugs-08-02480">9</xref>,<xref ref-type="bibr" rid="b10-marinedrugs-08-02480">10</xref>,<xref ref-type="bibr" rid="b19-marinedrugs-08-02480">19</xref>–<xref ref-type="bibr" rid="b21-marinedrugs-08-02480">21</xref>]. Macroaggregates are continuously subjected to microbial and various chemical and photochemical transformations [<xref ref-type="bibr" rid="b17-marinedrugs-08-02480">17</xref>]. However, the bacteria are believed to be a principal decomposer of the macroaggregate biopolymers [<xref ref-type="bibr" rid="b21-marinedrugs-08-02480">21</xref>,<xref ref-type="bibr" rid="b22-marinedrugs-08-02480">22</xref>] leading to low molecular weight products finally released to marine dissolved matter. Complete disappearance of macroaggregates, mostly in the late summer, usually coincides with rain storm events, changes in the water column stratification and circulation pattern [<xref ref-type="bibr" rid="b23-marinedrugs-08-02480">23</xref>].</p>
<p>The principal aim of this article was to present our recent investigations on the reactivity of various macroaggregate fractions, namely matrix and interstitial water colloids, in relation to their composition as well as the linkage of macroaggregate structural units using laboratory based enzymatic and natural degradation approaches.</p></sec>
<sec sec-type="results|discussion">
<title>2. Results and Discussion</title>
<sec>
<title>2.1. Macroaggregate composition: matrix</title>
<p>The matrix can be viewed as the water-insoluble fraction of macroaggregates. Major spectrum bands (<xref ref-type="fig" rid="f1-marinedrugs-08-02480">Figure 1A</xref>) could be assigned: 3000–3600 cm<sup>−1</sup> (O-H, N-H stretching band region), 3000–2800 cm<sup>−1</sup> (aliphatic groups), 1730 cm<sup>−1</sup> (C=O stretching of COOH, ketones or aldehides), 1650–1640 cm<sup>−1</sup> (C=O stretching of amide I; C=N stretch; stretching of COO<sup>−</sup>; C=C signals of aromatic ring and/or olefins C=C, water deformational modes), 1430 cm<sup>−1</sup> (aliphatic C-H deformation of CH<sub>2</sub> and CH<sub>3</sub> groups; symmetric stretching of COO<sup>−</sup>), 1150–1000 cm<sup>−1</sup> (carbohydrates, Si-O stretch). Spectra of surface matrix display also main calcite peaks situated at 2516, 1420–1450, 876 and 713 cm<sup>−1</sup> and that of silicates (527–535 and 472 cm<sup>−1</sup>). The elemental composition of surface and water column samples revealed higher values for surface macroaggregates, averaging 16.4% of C<sub>org.</sub>, 0.7% of N<sub>tot.</sub> and 254 ppm of P<sub>tot.</sub>, with a mean C:N:P ratio (molar) of 772:26:1. Accordingly, higher contents of total carbohydrates and proteins, averaging 13.5% and 4.7%, respectively, were determined in surface samples compared to deeper seawater layer samples. This statement is supported also by FTIR analyses (<xref ref-type="fig" rid="f1-marinedrugs-08-02480">Figure 1</xref>) showing the presence of carbohydrates, evidenced by bands at ~1150–900 cm<sup>−1</sup> and proteins, evidenced by bands at 1654–1635 cm<sup>−1</sup>, in both samples. The lipid contents, clearly indicated by bands at 2950–2850 cm<sup>−1</sup> in FTIR spectra (<xref ref-type="fig" rid="f1-marinedrugs-08-02480">Figure 1A</xref>), are lower, averaging 2.2%.</p></sec>
<sec>
<title>2.2. Macroaggregate composition: interstitial water colloids</title>
<p>FTIR spectra of interstitial water colloids (the “water-soluble” fraction) show the presence of both basic constituents, <italic>i.e.</italic>, carbohydrates and proteins (<xref ref-type="fig" rid="f1-marinedrugs-08-02480">Figure 1B</xref>). In FT-IR spectra of all colloidal fractions (not shown), the presence of a band at 2240 cm<sup>−1</sup> probably indicates the cyanogenic glycosides [<xref ref-type="bibr" rid="b24-marinedrugs-08-02480">24</xref>] represents the greatest part of organic nitrilated compounds [<xref ref-type="bibr" rid="b25-marinedrugs-08-02480">25</xref>]. Their existence was previously confirmed also by monosaccharide analyses in bulk macroaggregates [<xref ref-type="bibr" rid="b26-marinedrugs-08-02480">26</xref>]. Their source is most probably linked to amino acids [<xref ref-type="bibr" rid="b25-marinedrugs-08-02480">25</xref>]. The bands assigned to lipids, <italic>i.e.</italic>, aliphatic components, at 2800–3000 cm<sup>−1</sup> are less evident. The important contribution of carbohydrates in all colloid fractions was supported by higher UV absorption at λ = 250 nm, more typical of polysaccharides, compared to λ = 205 nm, being more typical of proteins [<xref ref-type="bibr" rid="b27-marinedrugs-08-02480">27</xref>] and humics [<xref ref-type="bibr" rid="b28-marinedrugs-08-02480">28</xref>]. The highest carbohydrate content and the lower C/N and C/P ratios (<xref ref-type="fig" rid="f2-marinedrugs-08-02480">Figure 2</xref>) were found in the higher molecular weight (MW) colloidal fraction indicating the important presence of N and P containing [<xref ref-type="bibr" rid="b29-marinedrugs-08-02480">29</xref>] carbohydrates as well as their important role in mucilage composition. The δ<sup>15</sup>N data exhibiting low values, especially in the &gt;30 kDa fraction [<xref ref-type="bibr" rid="b30-marinedrugs-08-02480">30</xref>] and previous reports on non-protein nitrogen compounds [<xref ref-type="bibr" rid="b31-marinedrugs-08-02480">31</xref>], also sustain the presence of non-protein N compounds, <italic>i.e.</italic>, amino sugars, chlorophyll and nucleic acids, in the colloidal fraction. In contrast, the lower MW fractions seem mostly composed of oligo- and polysaccharides.</p></sec></sec>
<sec>
<title>3. Macroaggregate Lability</title>
<sec>
<title>3.1. Matrix</title>
<p>According to macroaggregate enzymatic hydrolysis with α-amylase and β-glucosidase, the α (1–4) reserve polysaccharides, abundantly present in dinofllagelates in surface bulk macroaggregate samples taken in July 2004, are the most susceptible for enzymatic hydrolysis. In contrast, in the water column macroaggregates, containing prevalently diatoms, the impact of α-amylase is lower (<xref ref-type="fig" rid="f3-marinedrugs-08-02480">Figure 3</xref>).</p>
<p>The presence of α- and β-glycosidic linkages in macroaggregates was previously confirmed by <sup>1</sup>H-NMR spectroscopy [<xref ref-type="bibr" rid="b32-marinedrugs-08-02480">32</xref>] and a shift from α- to the more refractory β-glycosidic linkage was described in aged macroaggregates dominated by diatoms containing storage β-glucans [<xref ref-type="bibr" rid="b19-marinedrugs-08-02480">19</xref>,<xref ref-type="bibr" rid="b22-marinedrugs-08-02480">22</xref>]. These findings are in accordance with the observations of Herndl <italic>et al.</italic> [<xref ref-type="bibr" rid="b33-marinedrugs-08-02480">33</xref>] and Zaccone <italic>et al.</italic> [<xref ref-type="bibr" rid="b34-marinedrugs-08-02480">34</xref>] who found that the activities of α- and β-glucosidase in macroaggregates were opposite due to microbial response to the composition of substrates, <italic>i.e.</italic>, macroaggregate components, where β-glycosidic linkage seems more refractory. The compositional difference between “fresher” surface and aged water column macroaggregate samples is also indicated by results of enzymatic hydrolysis (<xref ref-type="fig" rid="f4-marinedrugs-08-02480">Figure 4</xref>). The addition of α-amylase and β-glucosidase produces high carbohydrate release in both samples (<xref ref-type="fig" rid="f4-marinedrugs-08-02480">Figure 4A and 4B</xref>). Protease and proteinase K, the most active ectoenzymes found in particles [<xref ref-type="bibr" rid="b35-marinedrugs-08-02480">35</xref>] and macroaggregates [<xref ref-type="bibr" rid="b22-marinedrugs-08-02480">22</xref>], produce, in addition to proteins, higher carbohydrate release in the water column sample which is clearly evident from FTIR spectra (<xref ref-type="fig" rid="f4-marinedrugs-08-02480">Figure 4B</xref>) showing a greater decrease in the carbohydrate band at ~1150–1000 cm<sup>−1</sup>.</p>
<p>FTIR spectra of the water phase from macroaggregate matrix slurries, obtained after hydrolysis with α-amylase + β-glucosidase, indicate the presence of minerals (<xref ref-type="fig" rid="f5-marinedrugs-08-02480">Figure 5</xref>) such as calcite (signals at 2516, 1430, 876 cm<sup>−1</sup>) and silicates (530 and 472 cm<sup>−1</sup>). These results confirm the importance of associations between carbohydrates and minerals (inorganic species) for mucilage events. The release of minerals was not observed in the case of the same treatment of more mature water column sample, probably due to more intense interactions between organic and inorganic components; the latter acting as a stabilizing agent.</p>
<p>In aged macroaggregates, the carbohydrates can be linked to proteins, probably in the form of glycoproteins, and thus the organic N can be preserved in these probably more crosslinked samples [<xref ref-type="bibr" rid="b36-marinedrugs-08-02480">36</xref>]. The rapid hydrolysis of organophosphorus in the macroaggregate matrix by phosphatase, a nearly 300% increase of phosphate concentrations in the first ten minutes, suggests faster cycling of P with respect to N. Phosphatase can also be involved in the hydrolysis and release of organic constituents [<xref ref-type="bibr" rid="b37-marinedrugs-08-02480">37</xref>].</p>
<p>The hydrolysis of surface (fresher) macroaggregates with lipase showed primarily the degradation of lipids and polysaccharides, suggesting an association of lipids with polysaccharides possibly in the form of glycolipids. Using lipase (<xref ref-type="fig" rid="f6-marinedrugs-08-02480">Figure 6</xref>) the macroagregate degradation is slower, ranging from days to weeks, compared to proteinase K and protease, ranging from hours to days. In the three week long degradation experiment, the relative intensities of absorptions indicating the lipidic component (2800–3000 cm<sup>−1</sup>, 1730–1740 cm<sup>−1</sup>, 1430–1450 cm<sup>−1</sup>), revealed a large decrease in lipids, only at the end of the experiment due to their lower degradability.</p>
<p>The previous studies [<xref ref-type="bibr" rid="b18-marinedrugs-08-02480">18</xref>,<xref ref-type="bibr" rid="b36-marinedrugs-08-02480">36</xref>] of temporal compositional changes of the northern Adriatic bulk macroaggregates in the summer stratified seawater column, using <sup>1</sup>H- and <sup>13</sup>C-NMR and FTIR spectroscopy, also revealed the preferential degradation of carbohydrates in comparison to the aliphatic components—lipids. Similar results were obtained in the spectroscopic <sup>1</sup>H-NMR study of the bulk macroaggregates, showing much faster degradation of carbohydrates compared to lipids during the mucilage event [<xref ref-type="bibr" rid="b31-marinedrugs-08-02480">31</xref>]. All these findings seem to contradict the reported observations of the high hydrolytic activity of lipases, one of the most active ectoenzymes in aquatic systems [<xref ref-type="bibr" rid="b38-marinedrugs-08-02480">38</xref>] and in macroaggregates [<xref ref-type="bibr" rid="b39-marinedrugs-08-02480">39</xref>].</p>
<p>Regardless of bacterial enzymatic activity, the macroaggregate hydrogel structure can slow microbial degradation [<xref ref-type="bibr" rid="b40-marinedrugs-08-02480">40</xref>]. The gel microhabitat can represent an important site of organic matter degradation (microbial functioning) but, on the other hand, the gel polymers can be preserved due to their sterical hindrance [<xref ref-type="bibr" rid="b40-marinedrugs-08-02480">40</xref>] and the presence of organic-inorganic associations.</p></sec>
<sec>
<title>3.2. Interstitial water colloids</title>
<p>The enzymatic hydrolysis of all colloidal fractions using α-amylase and β-glucosidase indicates the presence of α- and β-gycosidic linkages in nearly equimolar proportions. Similar kinetics of hydrolysis appears in the &gt;30 kDa and 10–30 kDa fractions. In the 5–10 kDa fraction, the increase of carbohydrate content after seven days is probably due to the prevalently polysaccharidic nature of this fraction making it more suitable for enzymatic hydrolisis. Contents of C<sub>org.</sub>, N<sub>tot.</sub>and P<sub>tot.</sub> and the results of HPSEC analyses [<xref ref-type="bibr" rid="b41-marinedrugs-08-02480">41</xref>] from the »natural« degradation of macroaggregate colloidal fractions, indicate faster degradation in the &gt;30 kDa and 30–10 kDa fractions compared to the 10–5 kDa fraction. This could be due to the higher contents of <italic>N</italic>-containing polysaccharides in the higher MW fractions. The microbial degradation of the carbohydrate component of glycoproteins is reported to proceed up to 3-fold faster compared to the proteinaceous components [<xref ref-type="bibr" rid="b42-marinedrugs-08-02480">42</xref>,<xref ref-type="bibr" rid="b43-marinedrugs-08-02480">43</xref>] explaining the preservation of organic nitrogen and the decreasing C/N ratio in aged degraded mature macroaggregates.</p></sec></sec>
<sec>
<title>4. Experimental Section</title>
<sec>
<title>4.1. Samples</title>
<p>Macroaggregate samples were collected on 1 July, 2004, in the southern part of the Gulf of Trieste at a fixed sampling site (45° 31.46′ N, 13° 33.72′ E) at the sea surface and at a depth of 10 m above the pycnocline. The sea water temperature was 25 °C. Both macroaggregate samples were in macrogel form; hence it was possible to collect them by hand by SCUBA divers, using polyethylene bottles with a minimal amount of surrounding water. The macroaggregate interstitial water was isolated by filtration through a 50 μm mesh size plankton net and centrifuged at 4000 g. The supernatant was successively filtered through preignited 0.7 μm pore size Whatman GF/F filters. The sediment (water-insoluble fraction) experiments and filtered supernatant (water-soluble fraction) were freeze-dried and used for subsequent degradation and fractionation, and degradation experiments, respectively.</p></sec>
<sec>
<title>4.2. Degradation experiments and separations</title>
<sec>
<title>4.2.1. Matrix</title>
<p>The dry macroaggregate matrix was diluted with distilled water (aqueous phase) to obtain aqueous slurries of water-insoluble macroaggregate matrix. It was further enzymatically hydrolyzed for 0, 5, 10, 30, 60, 120, 240 and 360 min at 26 °C using 0.5 mL of α-amylase, β-glucosidase, protease or 1 mL proteinase K (all Sigma). The concentrations of all used aqueous enzyme stock solutions were 1 mg/mL. Enzymatic hydrolisis with 0.2 mL of lipase (Sigma) at 26 °C lasted for 0, 20, 60 min, and 1, 7, 14 and 21 days. The concentration of the used lipase stock solution was 6 mg/mL. The hydrolyzates were successively centrifuged at 3000 g, and the supernatant and sediment used for determination of total carbohydrates, proteins and lipids, and FTIR analyses. The blanks, consisting of samples without the addition of enzymes, represented substrates in a »natural« degradation experiment. All experiments were performed in triplicate.</p></sec>
<sec>
<title>4.2.2. Interstitial water colloids</title>
<p>In the natural degradation study, the filtrate was incubated for four weeks at 26 °C in the dark and subsamples were taken at the start (t = 0), after one (t = 1), two (t = 2), three (t = 3) and four weeks (t = 4). The subsamples were subsequently filtered through 0.22 μm pore size Nucleopore filters and separated by ultrafiltration. Ultrafiltration in a “cascade fashion” through membranes with nominal molecular weight cutoff (MWCO) values of 30, 10 and 5 kDa was performed using a Vivascience VivaFlow 200 unit (Sartorius) with a MasterFlex L/S membrane pump (Cole-Palmer) at a flow rate of 300 mL min<sup>−1</sup> at 2.5 bar. The permeates (F) and retentates (O) were freeze-dried and analyzed for C<sub>org.</sub>, N<sub>tot.</sub>, P<sub>tot.</sub> and carbohydrate contents, and used for FTIR analyses.</p>
<p>For enzymatic study, the macroaggregate interstitial water used as a substrate was firstly filtered through 0.7 μm pore size Whatman GF/F filters and then filtered through a 0.22 μm pore size Nucleopore filter and, finally, separated by ultrafiltration as described above. The obtained retentates were subsequently hydrolyzed using α-amylase and β-glucosidase at 26 °C, the mean summer surface temperature in the Gulf of Trieste, for 14 days, and the products freeze-dried and analyzed for C<sub>org.</sub>, N<sub>tot.</sub> and total carbohydrate content, and characterized using FTIR analyses. Concentration of both enzyme stock solutions was 1 mg/mL. All experiments were performed in triplicate.</p></sec></sec>
<sec>
<title>4.3. Analyses</title>
<p>C<sub>org.</sub> and N<sub>tot.</sub> in freeze-dried samples were analyzed using a Carlo Erba mod. EA 1108 C, H, N, S analyzer and P<sub>tot.</sub> colorimetrically [<xref ref-type="bibr" rid="b44-marinedrugs-08-02480">44</xref>] after sample digestion with K<sub>2</sub>S<sub>2</sub>O<sub>8</sub>. Total proteins, carbohydrates and lipids were assayed colorimetrically using the Coomassie Brilliant Blue method of Setchell <italic>et al.</italic> [<xref ref-type="bibr" rid="b45-marinedrugs-08-02480">45</xref>], the phenol-sulphuric acid method of Dubois <italic>et al.</italic> [<xref ref-type="bibr" rid="b46-marinedrugs-08-02480">46</xref>] and the Folch [<xref ref-type="bibr" rid="b47-marinedrugs-08-02480">47</xref>] method, respectively. Standards comprised solutions of <sc>d</sc>-glucose (Sigma) for carbohydrates and BSA (Sigma) for proteins in Milli-Q water. All colorimetric analyses were performed in triplicate. FTIR spectra were obtained from homogenized samples using a Perkin-Elmer Spectrum One spectrometer with a diffuse reflectance sampling accessory. The micro-cup of the accessory was filled with the sample diluted by anhydrous KBr to give up to a 5% mixture. Spectra were collected at room temperature with a resolution of 4 cm<sup>−1</sup> and 4–10 scans were accumulated for each spectrum in a frequency range of 4000–450 cm<sup>−1</sup>.</p></sec></sec>
<sec sec-type="conclusions">
<title>5. Conclusions</title>
<p>Results obtained from the enzymatically hydrolyzed macroaggregate matrix, prevalently of phytoplankton origin, by amylase, glucosidase, protease, proteinase and lipase, reveal fast, almost simultaneous, decomposition of polysaccharides and proteins, but slower decomposition of lipids probably in the form of glycolipids. Hence, the majority of carbohydrate and protein pools are potentially degradable, while the great majority of lipids can be preserved in the water column and transported away and finally deposited on the seabed. A pronounced degradation of the α-glycosidic bond compared to β-linkages was observed, probably due to the presence of α-reserve algal polysaccharides. The rapid hydrolysis of the organophosphorus component suggests fast cycling of macroaggregate phosphorus.</p>
<p>Hydrolysis of the macroaggregate matrix with α-amylase + β-glucosidase resulted in a release of inorganic particles, indicating an important interaction between carbohydrates and minerals. Minerals act as an important aggregation nucleus in mucilage formation and stabilization.</p>
<p><italic>N</italic>-containing polysaccharides seem to be important constituents of the higher MW colloidal fractions, whereas poly- and oligosaccharides prevailed in the lower MW fractions. Degradation of the polysaccharide component proceeded faster in the higher MW fractions contributing to the preservation of organic nitrogen in the form of less degradable <italic>N</italic>-containing polysaccharides.</p>
<p>Our present knowledge indicates that various macroaggregate fractions and components are subjected to compositionally selective lability with important implications for macroaggregate persistence.</p>
<p>The compositional and degradation studies of marine mucous macroaggregates can contribute to the general knowledge of gels, gelation and aggregation (sol-gel transition) processes, binding capacity and other adsorbing properties, ion-exchange processes and inter- and intra-associations of such substrates, and the outcomes can potentially be used for technological purposes. To our knowledge, there are no reports on technological and pharmaceutical use of marine macroaggregates.</p></sec></body>
<back>
<fn-group><fn>
<p><italic>Samples Availability:</italic> Available from the authors.</p></fn></fn-group>
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<sec sec-type="display-objects">
<title>Figures</title>
<fig id="f1-marinedrugs-08-02480" position="float">
<label>Figure 1</label>
<caption>
<p>FT-IR spectra of (<bold>A</bold>) macroaggregate matrix, surface sample (black bold line) and water column sample (black dotted line); and (<bold>B</bold>) macroaggregate interstitial water colloids, surface sample (blue bold line) and water column sample (blue dotted line).</p></caption><graphic xlink:href="marinedrugs-08-02480f1.gif"/></fig>
<fig id="f2-marinedrugs-08-02480" position="float">
<label>Figure 2</label>
<caption>
<p>C<sub>org.</sub>/N<sub>tot.</sub> (<bold>A</bold>) and C<sub>org.</sub>/P<sub>tot.</sub> (<bold>B</bold>) molar ratios ultrafiltrate retentates (UF/0) and permeates (UF/F) using a nominal molecular weight cutoff of 30–10 (UF1), 10–5 (UF2) and &lt;5 kDa (UF3) at the start, after 1 week and after 4 weeks of the degradation experiment.</p></caption><graphic xlink:href="marinedrugs-08-02480f2.gif"/></fig>
<fig id="f3-marinedrugs-08-02480" position="float">
<label>Figure 3</label>
<caption>
<p>Concentration changes of carbohydrates and proteins during various enzyme hydrolyses (6 hours at 26 °C).</p></caption><graphic xlink:href="marinedrugs-08-02480f3.gif"/></fig>
<fig id="f4-marinedrugs-08-02480" position="float">
<label>Figures 4</label>
<caption>
<p>FT-IR spectra of the (<bold>A</bold>) surface and (<bold>B</bold>) water column macroaggregate matrices, and after (i) α-amylase + β-glucosidase, (ii) protease + proteinase K hydrolysis: carbohydrate bands (region ~1150–900 cm<sup>−1</sup>), protein bands (region 1654–1635 cm<sup>−1</sup>), lipid bands (region 2950–2850 cm<sup>−1</sup>) and inorganic (mineral) components (region &lt;1000 cm<sup>−1</sup>).</p></caption><graphic xlink:href="marinedrugs-08-02480f4.gif"/></fig>
<fig id="f5-marinedrugs-08-02480" position="float">
<label>Figures 5</label>
<caption>
<p>FT-IR spectra of the surface macroaggregate matrix and aqueous phase of experimental slurries after α-amylase + β-glucosidase and protease + proteinase K hydrolysis.</p></caption><graphic xlink:href="marinedrugs-08-02480f5.gif"/></fig>
<fig id="f6-marinedrugs-08-02480" position="float">
<label>Figure 6</label>
<caption>
<p>FT-IR spectra of the surface macroaggregate matrix (sampled at the beginning of the degradation experiment; t<sub>1</sub>—black line), and after lipase (after 3 weeks at 26 °C, t<sub>1</sub>—blue line) hydrolysis: carbohydrate bands (region ~1150–900 cm<sup>−1</sup>), protein bands (region 1654–1635 cm<sup>−1</sup>), lipid bands (region 2950–2850 cm<sup>−1</sup>) and inorganic (mineral) components (region &lt;1000 cm<sup>−1</sup>).</p></caption><graphic xlink:href="marinedrugs-08-02480f6.gif"/></fig></sec></back></article>
