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	<title>Environmental contaminants &#8211; APECS Portugal</title>
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	<link>https://apecsportugal.pt</link>
	<description>Um site para os jovens cientistas e dos jovens cientistas para o Mundo</description>
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	<url>https://apecsportugal.pt/wp-content/uploads/2022/10/APECS-PT-icon-150x150.jpg</url>
	<title>Environmental contaminants &#8211; APECS Portugal</title>
	<link>https://apecsportugal.pt</link>
	<width>32</width>
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</image> 
	<item>
		<title>Trace elements in soils of the Antarctic ice-free areas: Insights on natural geochemical values, anthropogenic impact and possible remobilisation upon permafrost thaw</title>
		<link>https://apecsportugal.pt/en/2026/02/27/trace-elements-in-soils-of-the-antarctic-ice-free-areas-insights-on-natural-geochemical-values-anthropogenic-impact-and-possible-remobilisation-upon-permafrost-thaw/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Fri, 27 Feb 2026 14:07:08 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Climate changes]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=8117</guid>

					<description><![CDATA[Antarctica’s ice-free areas represent less than 0.5% of the continent’s surface, yet they host nearly all terrestrial biodiversity and most human infrastructure, such as scientific stations and former sites of human activity. These regions are both ecologically sensitive and particularly vulnerable to the effects of climate change. In this study, the researchers carried out a [&#8230;]]]></description>
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<p>Antarctica’s ice-free areas represent less than 0.5% of the continent’s surface, yet they host nearly all terrestrial biodiversity and most human infrastructure, such as scientific stations and former sites of human activity. These regions are both ecologically sensitive and particularly vulnerable to the effects of climate change.</p>



<p>In this study, the researchers carried out a comprehensive review of trace elements in soils from Antarctica’s ice-free areas, examining concentrations in pristine zones and in areas influenced by human activity, with special emphasis on the impact of permafrost thaw on their mobilization. Antarctica was divided into six regions with similar climatic and environmental characteristics, allowing results to be compared, natural and anthropogenic sources of contaminants to be distinguished, and vulnerable areas requiring future monitoring to be identified.</p>



<p>The results showed that the active layer of permafrost controls the accumulation and mobility of trace elements in Antarctic soils and that permafrost thaw associated with climate change can remobilize previously retained contaminants, increasing their environmental availability.</p>



<p>Furthermore, concentrations of elements such as Hg, Pb, Cd, Cu, Cr, and Ni arise from both natural and anthropogenic sources. In the South Shetland Islands, particularly on King George Island, higher values are recorded near scientific stations, waste sites, fuel spills, and other human infrastructures, whereas on Deception Island, volcanic activity leads to naturally elevated concentrations of Hg and As, with permafrost potentially acting as a temporary reservoir for these elements (Fig. 1). Scientists also noted that glacier retreat, increasing active-layer thickness, and permafrost degradation are altering hydrological dynamics and contaminant transport.</p>



<p>The combined effects of human pressure and climate change pose a growing risk to terrestrial and coastal ecosystems, underscoring the need for continuous monitoring.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full"><img fetchpriority="high" decoding="async" width="738" height="591" src="https://apecsportugal.pt/wp-content/uploads/2026/02/image.png" alt="" class="wp-image-8114" srcset="https://apecsportugal.pt/wp-content/uploads/2026/02/image.png 738w, https://apecsportugal.pt/wp-content/uploads/2026/02/image-300x240.png 300w" sizes="(max-width: 738px) 100vw, 738px" /><figcaption class="wp-element-caption"><em><strong>Figure 1:</strong> <em>Sites in the South Shetland Islands with reports on trace element concentrations. Red dots represent areas where trace element concentrations were affected by anthropogenic impact and green dots reflect natural concentrations.</em></em></figcaption></figure>
</div>


<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p>Source: Zilhão, H., Cesário, R., Vieira, G. &amp; Canário, J. (2025). Trace elements in soils of the Antarctic ice-free areas: Insights on natural geochemical values, anthropogenic impact and possible remobilisation upon permafrost thaw. <em>Earth-Science Reviews</em>, 268.</p>



<p>Author: Diana Vaz</p>



<p></p>
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			</item>
		<item>
		<title>Mercury Concentrations, Habitat and Trophic Position of Antimora rostrata and Macrourus holotrachys from South Georgia (Southern Ocean)</title>
		<link>https://apecsportugal.pt/en/2025/11/28/mercury-concentrations-habitat-and-trophic-position-of-antimora-rostrata-and-macrourus-holotrachys-from-south-georgia-southern-ocean/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Fri, 28 Nov 2025 10:50:37 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Food chain]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=7949</guid>

					<description><![CDATA[Mercury (Hg) is considered a neurotoxin capable of severely harming wildlife, including marine ecosystems. It has a high dispersal capacity through atmospheric and oceanic currents, allowing it to reach remote regions across the globe, such as the Southern Ocean, where it accumulates in marine food webs. Despite its ecological relevance, little was known about Hg [&#8230;]]]></description>
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<p>Mercury (Hg) is considered a neurotoxin capable of severely harming wildlife, including marine ecosystems. It has a high dispersal capacity through atmospheric and oceanic currents, allowing it to reach remote regions across the globe, such as the Southern Ocean, where it accumulates in marine food webs. Despite its ecological relevance, little was known about Hg concentrations in deep-sea fishes from this region.</p>



<p>In this study, researchers analysed two deep-sea fish species from South Georgia: <em>Antimora rostrata</em> (blue antimora), a more pelagic species, and <em>Macrourus holotrachys</em> (bigeye grenadier), a demersal species. In 2020, individuals were collected and four tissues (muscle, brain, liver and gills) were analysed, along with stable isotopes, to determine the habitat and trophic position of each species.</p>



<p>The results showed that:</p>



<ul class="wp-block-list">
<li>Muscle was the tissue with the highest mercury concentrations in both species.</li>



<li><em>A. rostrata</em> consistently showed lower concentrations than <em>M. holotrachys</em>.</li>



<li>Only in <em>M. holotrachys</em> did Hg concentrations increase with body length and weight, suggesting bioaccumulation throughout life</li>



<li>Differences also reflected habitat use, since the demersal species (<em>M. holotrachys</em>) is more closely associated with benthic food webs, which are generally richer in Hg.</li>



<li><em>A. rostrata</em> occupies a lower trophic level than <em>M. holotrachys</em>.</li>
</ul>



<p>Unexpectedly, the brain showed high Hg concentrations, raising questions about potential neurotoxic effects in these fishes and their predators.</p>



<p>These results reveal that different feeding strategies and habitats shape contaminant accumulation in deep-sea species, with implications for ecosystem health and for top predators that depend on them.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full"><img decoding="async" width="796" height="378" src="https://apecsportugal.pt/wp-content/uploads/2025/11/image.png" alt="" class="wp-image-7945" srcset="https://apecsportugal.pt/wp-content/uploads/2025/11/image.png 796w, https://apecsportugal.pt/wp-content/uploads/2025/11/image-300x142.png 300w, https://apecsportugal.pt/wp-content/uploads/2025/11/image-768x365.png 768w" sizes="(max-width: 796px) 100vw, 796px" /><figcaption class="wp-element-caption"><strong>Figure 1:</strong> Mercury concentrations (Mean ± 1 SD, µg g<sup>-1</sup> dw) in different tissues (Muscle, Brain, Liver and Gills) of <em>Antimora rostrata</em> and <em>Macrourus holotrachys</em>. Different lowercase (for <em>Antimora rostrata</em>) and uppercase (for <em>Macrourus holotrachys</em>) letters above bars indicate significant differences among tissues in each species (Friedman test with Nemenyi post hoc test, p &lt; 0.05). * between bars indicate differences between the same tissue in both species (Mann-Whitney test, p &lt; 0.0001).</figcaption></figure>
</div>

<div class="wp-block-image">
<figure class="aligncenter size-full"><img decoding="async" width="886" height="442" src="https://apecsportugal.pt/wp-content/uploads/2025/11/image-1.png" alt="" class="wp-image-7946" srcset="https://apecsportugal.pt/wp-content/uploads/2025/11/image-1.png 886w, https://apecsportugal.pt/wp-content/uploads/2025/11/image-1-300x150.png 300w, https://apecsportugal.pt/wp-content/uploads/2025/11/image-1-768x383.png 768w" sizes="(max-width: 886px) 100vw, 886px" /><figcaption class="wp-element-caption"><strong>Figure 2:</strong> δ<sup>13</sup>C and δ<sup>15</sup>N values in the muscle of <em>Antimora rostrata</em> (n = 23) and <em>Macrourus holotrachys</em> (n = 22) from South Georgia. Mean ± standard deviation.</figcaption></figure>
</div>


<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p><strong>Source: </strong>Vaz, D. B., Queirós, J. P., Xavier, J. C., Bustamante, P., Abreu, J., Pereira, E., Hollyman, P. R., Coelho, J. P. &amp; Seco, J. (2025). Mercury Concentrations, Habitat and Trophic Position of <em>Antimora Rostrata</em> and <em>Macrourus Holotrachys</em> from South Georgia (Southern Ocean). <em>Marine Pollution Bulletin</em>. DOI:10.2139/ssrn.5360416</p>



<p><strong>Author:</strong> Diana</p>



<p></p>
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		<item>
		<title>Decreasing mercury concentrations in beaks of the giant warty squid Moroteuthopsis longimana in the Scotia Sea since the 1970s</title>
		<link>https://apecsportugal.pt/en/2025/09/23/decreasing-mercury-concentrations-in-beaks-of-the-giant-warty-squid-moroteuthopsis-longimana-in-the-scotia-sea-since-the-1970s/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Tue, 23 Sep 2025 13:52:16 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Food chain]]></category>
		<category><![CDATA[Marine species]]></category>
		<category><![CDATA[Oceans]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=7830</guid>

					<description><![CDATA[The giant warty squid (Moroteuthopsis longimana), a deep-sea species from the Scotia Sea in the Southern Ocean, might be a key to assay to track one of the planet’s most concerning pollutants: mercury. Mercury is a toxic element that bioaccumulates in marine food webs, reaching higher concentrations in predators and posing risks to both wildlife [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>The giant warty squid (<em>Moroteuthopsis longimana</em>), a deep-sea species from the Scotia Sea in the Southern Ocean, might be a key to assay to track one of the planet’s most concerning pollutants: mercury. Mercury is a toxic element that bioaccumulates in marine food webs, reaching higher concentrations in predators and posing risks to both wildlife and human health.</p>



<p>Because squids are almost impossible to study alive, scientists have to rely on their beaks, hard structures that resist digestion and accumulate in the stomachs of predators to analyse their chemical signatures. In this study, researchers analysed squid beaks collected from the 1970s to the present day to measure mercury concentrations.</p>



<p>The results were remarkable, despite high mercury levels in the first two decades, concentration have been steadily <strong>decreasing over the past three decades</strong>. This trend suggests that global efforts to reduce mercury emissions, such as the International Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other Matter (1972)and improvements in industrial practices, are having measurable positive effects, even in remote ecosystems like the Southern Ocean (Figure 1).</p>


<div class="wp-block-image">
<figure class="aligncenter size-full"><img loading="lazy" decoding="async" width="604" height="370" src="https://apecsportugal.pt/wp-content/uploads/2025/09/image.png" alt="" class="wp-image-7827" srcset="https://apecsportugal.pt/wp-content/uploads/2025/09/image.png 604w, https://apecsportugal.pt/wp-content/uploads/2025/09/image-300x184.png 300w" sizes="(max-width: 604px) 100vw, 604px" /><figcaption class="wp-element-caption"><strong>Figure 1:</strong> Boxplot of mercury (Hg) concentrations in the lower beaks of the giant warty squid M. longimana sampled over 5 decades.</figcaption></figure>
</div>


<p>Cephalopods like&nbsp;<em>M. longimana</em>&nbsp;can be valuable bioindicators as they occupy a central position in marine food webs, linking smaller prey such as crustaceans and fish to large predators like seals and whales. Moreover, their short lifespan and rapid make them excellent “record keepers” of environmental conditions giving researchers a unique window into pollutant trends.</p>



<p>By turning squid beaks into environmental archives, scientists have provided evidence that pollution can decline when collective action is taken. These results bring hope, but also serve as a reminder of the need to sustain global commitments to pollution reduction to safeguard ecosystems.</p>



<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p><strong>Source:</strong> Sara Lopes-Santos, José C. Xavier, José Abreu, José Seco, João P. Coelho, Eduarda Pereira, Richard A. Phillips, José P. Queirós, Decreasing mercury concentrations in beaks of the giant warty squid <em>Moroteuthopsis longimana</em> in the Scotia Sea (Southern Ocean) since the 1970s, Marine Pollution Bulletin, Volume 221, 2025, 118578, ISSN 0025-326X</p>



<p><strong>Author:</strong> Lucas</p>



<p></p>
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		<item>
		<title>The Squid Beaks Theory: Unravelling the mystery of mercury concentrations in the muscle of Morotheutopsis longimana</title>
		<link>https://apecsportugal.pt/en/2024/12/31/the-squid-beaks-theory-unravelling-the-mystery-of-mercury-concentrations-in-the-muscle-of-morotheutopsis-longimana/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Tue, 31 Dec 2024 14:33:21 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Food chain]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=7232</guid>

					<description><![CDATA[Mercury (Hg) is a toxic metal, which as seen its concentrations increase in the environment due to anthropogenic activities. It bioaccumulates in organisms throughout life and biomagnifies in food webs, reaching high concentrations in some top predators. To understand the threat of Hg to these predators, monitor Hg concentrations in organisms at intermediate trophic levels [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>Mercury (Hg) is a toxic metal, which as seen its concentrations increase in the environment due to anthropogenic activities. It bioaccumulates in organisms throughout life and biomagnifies in food webs, reaching high concentrations in some top predators. To understand the threat of Hg to these predators, monitor Hg concentrations in organisms at intermediate trophic levels it is essential, as they are crucial factors in the trophic transfer of Hg. But how do we monitor Hg in elusive species such as Southern Ocean squid? The answer lies in their beaks, which are chitin structures resistant to digestion, that accumulate in the stomachs of predators and can be collected in regurgitations or after the animal&#8217;s death.</p>



<p>One such squid species,<em> Moroteuhopsis longimana</em>, inhabits the deep waters of the Southern Ocean and can reach more than 2 meters in total length. It bioaccumulates Hg throughout its life and is an important prey item for several top predators such as seabirds, marine mammals and fish, so understanding its role in the transfer of Hg in the food web is crucial. However, there is still a lack of knowledge about the relationship between Hg concentrations in <em>M. longimana</em> beaks and muscle (the main tissue consumed by the predators), which this study aims to analyse.</p>



<p>To do that, 21 buccal masses of <em>M. longimana</em> collected from the stomach of the Antarctic toothfish (<em>Dissostichus&nbsp;</em>mawson). For total Hg analysis, the upper and lower beaks were sectioned into the wing (W) and hood tip (H), and the remainder of the lower (L) and upper (U) beaks (Figure 1). A portion of the buccal mass muscle (M) was also collected for analysis.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full"><img loading="lazy" decoding="async" width="562" height="273" src="https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142319.png" alt="" class="wp-image-7229" srcset="https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142319.png 562w, https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142319-300x146.png 300w" sizes="(max-width: 562px) 100vw, 562px" /><figcaption class="wp-element-caption"><strong>Figure 1 &#8211; </strong>Moroteuthopsis longimana beak sections analysed for Hg and lower rostral length (LRL). W: wing; H: hood tip; L: lower beak; U: upper beak.</figcaption></figure>
</div>


<p>Results showed that Hg concentrations in the muscle are ~100 times higher than in the whole beaks (U and L) and ~50 times higher than in the W and H sections (Figure 2). Inter-tissue variability in Hg concentrations confirms that the concentration of Hg in the beak does not reflect directly those in the muscle.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full is-resized"><img loading="lazy" decoding="async" width="512" height="467" src="https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142200.png" alt="" class="wp-image-7228" style="width:558px;height:auto" srcset="https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142200.png 512w, https://apecsportugal.pt/wp-content/uploads/2024/12/Captura-de-ecra-2024-12-31-142200-300x274.png 300w" sizes="(max-width: 512px) 100vw, 512px" /><figcaption class="wp-element-caption"><strong>Figure 2 &#8211; </strong>Total mercury (Hg) concentrations in beak sections and muscle (buccal mass) of Moroteuthopsis longimana. Bars with different letters are statistically different. Values are mean ± SD.</figcaption></figure>
</div>


<p>However, a positive relationship was found between Hg concentrations in the wing (W) and muscle (M), translated by the following equation:</p>



<p class="has-text-align-center"><strong><em>Hg<sub>músculo</sub>&nbsp;=&nbsp;34.88 Hg<sub>asa&nbsp;</sub>+&nbsp;0.12</em></strong><em></em></p>



<p>This equation suggests that mercury concentration in the wing can be used as a proxy for Hg concentration in the muscle of <em>M. longimana</em>. However, it should only be used for adult individuals, as this study only used fully chitinized adult beaks.</p>



<p>Future studies can now use this equation to estimate the Hg concentration in the muscle of other <em>M. longimana</em>, through the analysis of the Hg concentration in the beak wing, providing a means of assessing the levels, transport and fate of Hg in within Southern Ocean ecosystem.</p>



<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p><strong>Source:</strong> Lopes-Santos S, Xavier JC, Seco J, Coelho JP, Hollyman PR, Pereira E, Phillips RA, Queirós JP (2025) Squid beaks as a proxy for mercury concentrations in muscle of the giant warty squid Moroteuthopsis longimana. Marine Environmental Research 204:106841.</p>



<p><strong>Author:</strong> Sara Santos</p>



<p></p>
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			</item>
		<item>
		<title>Mercury Biomagnification Antarctic Food Web</title>
		<link>https://apecsportugal.pt/en/2024/10/27/mercury-biomagnification-antarctic-food-web/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Sun, 27 Oct 2024 12:21:31 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Climate changes]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Food chain]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=7213</guid>

					<description><![CDATA[The article examines how climate change and warming Southern Ocean waters can increase the availability of mercury (Hg) in the Antarctic marine food web, due to the release of ice-stored Hg and higher methylation rates by microorganisms. The research focused on the biomagnification of Hg in the food web of the Antarctic Peninsula, one of [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>The article examines how climate change and warming Southern Ocean waters can increase the availability of mercury (Hg) in the Antarctic marine food web, due to the release of ice-stored Hg and higher methylation rates by microorganisms. The research focused on the biomagnification of Hg in the food web of the Antarctic Peninsula, one of the fastest warming regions in the world. Using stable isotopes of carbon (δ13C) and nitrogen (δ15N) to estimate feeding habitats and trophic levels, respectively, total Hg (T-Hg) concentrations were measured in various species, from Antarctic krill <em>Euphausia superba</em> to predators such as penguins, seabirds, and marine mammals (Figure 1).</p>


<div class="wp-block-image">
<figure class="aligncenter size-full is-resized"><img loading="lazy" decoding="async" width="838" height="582" src="https://apecsportugal.pt/wp-content/uploads/2024/10/image.png" alt="" class="wp-image-7211" style="width:840px;height:auto" srcset="https://apecsportugal.pt/wp-content/uploads/2024/10/image.png 838w, https://apecsportugal.pt/wp-content/uploads/2024/10/image-300x208.png 300w, https://apecsportugal.pt/wp-content/uploads/2024/10/image-768x533.png 768w" sizes="(max-width: 838px) 100vw, 838px" /><figcaption class="wp-element-caption">Figure  1: Schematic representation of possible mercury biomagnification pathways along the Southern Ocean food web.</figcaption></figure>
</div>


<p>The study measured stable isotope signatures and Hg concentrations in different species, including chinstrap penguins, skuas, gulls, southern giant petrels, and southern elephant seals. Significant differences in δ13C values among species were observed, with considerable overlap between seabird species and seals. Differences in δ15N values reflected variations in diet and trophic position. The lowest Hg concentrations were found in krill (0.007 ± 0.008 μg∙g–1) and the highest in southern giant petrels (12.090 ± 14.177 μg∙g–1).</p>



<p>Results showed a positive relationship between Hg concentrations and trophic levels, with Hg biomagnifying nearly twice at each trophic level. The study suggests that trophic interactions are the major pathways for Hg biomagnification in Southern Ocean ecosystems. The research also highlights that Hg concentrations may increase in marine organisms due to global warming, which enhances Hg methylation and its availability in low-oxygen waters. Long-lived, high trophic level predators, such as some seabirds and seals, are particularly vulnerable to the effects of Hg.</p>



<p>The study concludes that Hg biomagnification in the food webs of the Antarctic Peninsula results in high Hg burdens in top predators. As global temperatures rise, Hg concentrations are expected to increase, potentially causing significant negative effects on Antarctic organisms. The article emphasises the need for further studies to fully understand how taxonomic, geographic, and ecological differences influence Hg dynamics in the marine ecosystems of the Antarctic Peninsula.</p>



<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p><strong>Source: </strong>Matias, R. S., Guímaro, H. R., Bustamante, P., Seco, J., Chipev, N., Fragão, J., &#8230; &amp; Xavier, J. C. (2022). Mercury biomagnification in an Antarctic food web of the Antarctic Peninsula. <em>Environmental Pollution</em>, <em>304</em>, 119199.</p>



<p><strong>DOI: </strong>10.1016/j.envpol.2022.119199</p>



<p><strong>Author:</strong> Laura Lopes</p>



<p></p>
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		<item>
		<title>Will Arctic shipping destroy the ecosystem?</title>
		<link>https://apecsportugal.pt/en/2024/06/24/will-arctic-shipping-destroy-the-ecosystem/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Mon, 24 Jun 2024 19:33:47 +0000</pubDate>
				<category><![CDATA[Artic]]></category>
		<category><![CDATA[Conservation]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=7098</guid>

					<description><![CDATA[Global warming has caused rapid warming in the Arctic region and continued melting of ice and snow, making Arctic shipping a reality and significantly increasing the navigability of the region&#8217;s sea routes. Between 1979 and 2018, the safe area for shipping in the Arctic increased by 35 %, sparking interest in new trade routes and [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>Global warming has caused rapid warming in the Arctic region and continued melting of ice and snow, making Arctic shipping a reality and significantly increasing the navigability of the region&#8217;s sea routes. Between 1979 and 2018, the safe area for shipping in the Arctic increased by 35 %, sparking interest in new trade routes and exploitation of natural resources (Figure 1). However, increased shipping in the Arctic raises environmental concerns due to pollutants and other negative impacts that threaten the fragile Arctic ecosystem.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full is-resized"><img loading="lazy" decoding="async" width="773" height="770" src="https://apecsportugal.pt/wp-content/uploads/2024/06/Picture1.jpg" alt="" class="wp-image-7095" style="width:448px;height:auto" srcset="https://apecsportugal.pt/wp-content/uploads/2024/06/Picture1.jpg 773w, https://apecsportugal.pt/wp-content/uploads/2024/06/Picture1-300x300.jpg 300w, https://apecsportugal.pt/wp-content/uploads/2024/06/Picture1-150x150.jpg 150w, https://apecsportugal.pt/wp-content/uploads/2024/06/Picture1-768x765.jpg 768w" sizes="(max-width: 773px) 100vw, 773px" /><figcaption class="wp-element-caption">Figure 1: Extent of the Arctic Circle and Arctic routes.</figcaption></figure>
</div>


<p>The impact of shipping in the Arctic is extensive, and three main areas stand out: on water bodies, atmospheric emissions, and animal survival.</p>



<p>Impacts on water bodies include pollution from anti-fouling paints, which release copper and microplastics that affect the growth and survival of marine life, inhibit reproduction, and cause deformities. In addition, oil spills pollute coastlines and beaches, affecting animal health, reproductive cycles and mobility, leading to the death of many species. Introducing non-native species (NNS) leads to loss of biodiversity and local extinctions. Sewage discharges also lead to pollution, depletion of dissolved oxygen, red tides and toxicological effects on the Arctic ecosystem.</p>



<p>Impacts on atmospheric emissions encompass air pollution and changes in atmospheric composition due to ship emissions, which disrupt radiative forcing (RF), accelerate Arctic warming, cause acid rain, and eutrophication of seawater.</p>



<p>Impacts on animal survival involve noise pollution, which disrupts Arctic animals&#8217; communication, altering behavioural patterns and potentially causing temporary or permanent hearing loss. Light pollution disrupts the orientation of marine animals and causes collisions, especially between birds.</p>



<p>To mitigate these negative impacts, it is essential to adopt technical and operational solutions for ships, as well as to formulate stricter standards and rules for Arctic shipping activities.</p>



<p>Reference: Xinli Qi, Zhenfu Li, Changping Zhao, Qiqi Zhang, Yutao Zhou, Environmental impacts of Arctic shipping activities: A review, Ocean &amp; Coastal Management, Volume 247, 2024, 106936, ISSN 0964-5691</p>



<p><a href="https://doi.org/10.1016/j.ocecoaman.2023.106936">https://doi.org/10.1016/j.ocecoaman.2023.106936</a></p>



<p>Author: Rita Quelha</p>
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		<title>Adélie penguin as bioindicator of mercury concentrations</title>
		<link>https://apecsportugal.pt/en/2023/12/15/adelie-penguin-as-bioindicator-of-mercury-concentrations/</link>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Fri, 15 Dec 2023 00:00:37 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Food chain]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=6780</guid>

					<description><![CDATA[Since the Industrial Revolution, mercury (Hg) concentrations in the environment have been increasing due to anthropogenic activities. The toxic effect that this metal has on animals and humans led to the adoption of the Minamata Convention on Mercury by more than 140 countries in 2013, to protect human health and the environment. Hg disperses throughout [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>Since the Industrial Revolution, mercury (Hg) concentrations in the environment have been increasing due to anthropogenic activities. The toxic effect that this metal has on animals and humans led to the adoption of the Minamata Convention on Mercury by more than 140 countries in 2013, to protect human health and the environment. Hg disperses throughout the world through atmospheric currents, depositing even in the most remote places, such as the polar regions.</p>



<p>Seabirds, as top predators, reflect the Hg contamination that is present in their marine food web, through biomagnification processes. Their main form of Hg excretion is through moulting. Within seabirds, the Adelie penguin (<em>Pygoscelis adeliae</em>) (Figure 1) has a set of ideal characteristics to be used as a bioindicator for Hg concentrations in Antarctic food webs, since it has a circumpolar distribution and is the most common and abundant penguin species on the Antarctic continent.</p>


<div class="wp-block-image">
<figure class="aligncenter size-large"><img loading="lazy" decoding="async" width="1024" height="683" src="https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia-1024x683.jpg" alt="" class="wp-image-6777" srcset="https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia-1024x683.jpg 1024w, https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia-300x200.jpg 300w, https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia-768x512.jpg 768w, https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia-391x260.jpg 391w, https://apecsportugal.pt/wp-content/uploads/2023/12/Pinguim-de-adelia.jpg 1072w" sizes="(max-width: 1024px) 100vw, 1024px" /><figcaption class="wp-element-caption">Figura 1 &#8211; Adélie penguin (Pixabay).</figcaption></figure>
</div>


<p></p>



<p>For the circumpolar assessment of Hg concentrations, feather samples were collected from 538 individuals (490 adults of reproductive age and 48 pre-fledging chicks) between 2005 and 2021 in 24 colonies around the continent. Total mercury (T-Hg) concentrations were evaluated for each sample. Values of the isotopes δ<sup>13</sup>C and δ<sup>15</sup>N were also determined on the feathers and used as proxies for the feeding habitat and trophic position of the penguins, respectively.</p>



<p>At the circumpolar level, Hg contamination proved to be relatively homogeneous between the different regions assessed. However, a Hg hotspot was observed in the Ross Sea (Figure 2), associated with a higher trophic position of Adélie penguins, likely due to a higher proportion of fish in their diets.</p>


<div class="wp-block-image">
<figure class="aligncenter size-full"><img loading="lazy" decoding="async" width="610" height="553" src="https://apecsportugal.pt/wp-content/uploads/2023/12/Variacao-espacial-nas-concentracoes-de-Hg-nas-penas-de-pinguins-de-adelia.png" alt="" class="wp-image-6778" srcset="https://apecsportugal.pt/wp-content/uploads/2023/12/Variacao-espacial-nas-concentracoes-de-Hg-nas-penas-de-pinguins-de-adelia.png 610w, https://apecsportugal.pt/wp-content/uploads/2023/12/Variacao-espacial-nas-concentracoes-de-Hg-nas-penas-de-pinguins-de-adelia-300x272.png 300w" sizes="(max-width: 610px) 100vw, 610px" /><figcaption class="wp-element-caption">Figure 2 &#8211; Spatial variation in feather Hg concentrations of (a) adult and (b) chick Adélie penguins in 24 Antarctic colonies. The color gradient represents increasing concentrations of Hg. The sample size (n) is indicated by the size of the circles and triangles. The average position of the Polar Front (dashed black line) reflects the northern limit of the Adélie penguin&#8217;s distribution.</figcaption></figure>
</div>


<p></p>



<p>It is essential to continue monitoring Hg concentrations to assess the effectiveness of the Minamata Convention on Mercury. Large-scale assessments are extremely important to monitor the contamination status of Antarctic food webs over time, and also to assess global trends, taking into account the climate change context.</p>



<p></p>



<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p>Author: Sara Santos</p>



<p>Source: Cusset, F., Bustamante, P., Carravieri, A. <em>et al.</em> Circumpolar assessment of mercury contamination: the Adélie penguin as a bioindicator of Antarctic marine ecosystems. <em>Ecotoxicology</em> <strong>32</strong>, 1024–1049 (2023). https://doi.org/10.1007/s10646-023-02709-9</p>



<p>DOI: <a href="https://doi.org/10.1007/s10646-023-02709-9">https://doi.org/10.1007/s10646-023-02709-9</a></p>
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		<title>A microplastic-free case?</title>
		<link>https://apecsportugal.pt/en/2023/04/15/a-microplastic-free-case/</link>
					<comments>https://apecsportugal.pt/en/2023/04/15/a-microplastic-free-case/#respond</comments>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Sat, 15 Apr 2023 18:01:00 +0000</pubDate>
				<category><![CDATA[Artic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<guid isPermaLink="false">https://apecsportugal.pt/?p=6277</guid>

					<description><![CDATA[The presence of microplastics in marine organisms is a growing concern worldwide, as these materials can have harmful effects on animal health and the ecosystem as a whole. The selected study of this month focused on the analysis of microplastics’ presence in the adipose tissue of ringed seals (Pusa hispida) in the Arctic. Between 2017 [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>The presence of microplastics in marine organisms is a growing concern worldwide, as these materials can have harmful effects on animal health and the ecosystem as a whole. The selected study of this month focused on the analysis of microplastics’ presence in the adipose tissue of ringed seals (<em>Pusa hispida</em>) in the Arctic.</p>



<p>Between 2017 and 2019, samples from the adipose tissue of ringed seals captured by indigenous hunters from western Canada were examined. The technique used for the analysis has a capacity to detect microplastic particles as small as 10 microns. Surprisingly, the results indicated that none of the samples contained detectable microplastics. This differs from previous studies that found high levels of microplastics in the adipose tissue of other seal species, such as ribbon seals.</p>



<p>Fibers are usually the most common type of microplastics found in marine mammals, followed by fragments and films. Even though the researchers have found small plastic based fibers in the samples, it is believed that their origin is based on contamination during sample handling in the laboratory. Cohen’s D, or standardized mean difference, is a common way to test whether an effect size is significant, statistically speaking, which in this case related to the ingestion of microplastic particles. In this study, with a sample size of content from 10 seal individuals, the observed effect was 0.37. For that value to be sifnificant, the sample would have to be composed of 91 individuals, being that with the 10 individuals examined, the effect would only be significant with a Cohen’s D value of at least 1.16 (blue and red lines, respectively, Fig.1).</p>


<div class="wp-block-image">
<figure class="aligncenter size-large is-resized"><img loading="lazy" decoding="async" src="https://apecsportugal.pt/wp-content/uploads/2023/04/Ciencia-as-Claras-Abril-1024x596.png" alt="" class="wp-image-6275" width="768" height="447" srcset="https://apecsportugal.pt/wp-content/uploads/2023/04/Ciencia-as-Claras-Abril-1024x596.png 1024w, https://apecsportugal.pt/wp-content/uploads/2023/04/Ciencia-as-Claras-Abril-300x175.png 300w, https://apecsportugal.pt/wp-content/uploads/2023/04/Ciencia-as-Claras-Abril-768x447.png 768w, https://apecsportugal.pt/wp-content/uploads/2023/04/Ciencia-as-Claras-Abril.png 1028w" sizes="(max-width: 768px) 100vw, 768px" /><figcaption class="wp-element-caption">Fig.1 With an increase in sample size, the required effect size for statistical significance decreases.</figcaption></figure>
</div>


<p>According to the researchers, the absence of microplastics in ringed seals in this study may be related to a small ingestion of plastic particles, compared with other marine fauna. Their main food supply is composed by fish, which presents a far less probability of microplastic ingestion, contrary to a diet dominated by benthic invertebrates. However, it is also possible that the technique used for analysis may not have been the most sensible to detect plastic particles with smaller dimensions, or that the study region in Canada is not exposed to the same levels of microplastics as other areas.</p>



<p>Although this study provides us with good news on this microplastic free ringed seal population in western Canada, it is still important to remember that other studies of the same kind have found high levels of microplastics in other populations around the world. Therefore, it is crucial to continue researching the presence and effects of microplastics in marine ecosystems in order to better understand their impacts and take measures to protect marine life and human health.</p>



<p>Overall, this study highlights the need for continued research on microplastics and their effects on marine organisms. It also emphasizes the importance of taking action to reduce the amount of plastic pollution in the ocean, through measures such as reducing plastic use and improving waste management systems. By working together to address this global issue, we can help protect marine ecosystems and the animals that rely on them for survival!&nbsp;</p>



<hr class="wp-block-separator has-alpha-channel-opacity"/>



<p>Source: Jardine, A.M., Provencher, J.F., Insley, S.J., Tauzer, L., Halliday, W.D., Bourdages, M.P.T., Houde, M., Muir, D., Vermaire, J.C. (2023). No accumulation of microplastics detected in western Canadian ringed seals (Pusa hispida). Mar Pollut Bull. 2023 Mar;188:114692 </p>



<p>DOI: 10.1016/j.marpolbul.2023.114692</p>



<p>Author: Laura Lopes</p>
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		<title>Plastics in Antarctica? What we know</title>
		<link>https://apecsportugal.pt/en/2022/08/15/plastics-in-antarctica-what-we-know/</link>
					<comments>https://apecsportugal.pt/en/2022/08/15/plastics-in-antarctica-what-we-know/#respond</comments>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Mon, 15 Aug 2022 01:17:43 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Conservation]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<guid isPermaLink="false">http://site-teste.infinityfreeapp.com/?p=3882</guid>

					<description><![CDATA[Antarctica and the Southern Ocean, continue to be one of the most remote places on the planet. However, as a consequence of human growth, these places are also increasingly subject to the pressures of anthropogenic activities. In this context, numerous studies have documented plastic pollution in the recent decades, to better understand the scale of [&#8230;]]]></description>
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<p id="viewer-foo">Antarctica and the Southern Ocean, continue to be one of the most remote places on the planet. However, as a consequence of human growth, these places are also increasingly subject to the pressures of anthropogenic activities.</p>



<p id="viewer-4r9ju">In this context, numerous studies have documented plastic pollution in the recent decades, to better understand the scale of this problem.</p>



<p id="viewer-4siea">The most common thinking in society, when talking about plastic, is as large objects such as bottles, bags, among others, yet, the problem of plastics is more serious due to its fragmentation, which ends up producing thousands of small pieces, many almost or even invisible to the naked eye. There are different categories, but these can be from nano-plastics (&lt; 1 nanometre) or macro-plastics (&gt; 10 millimetres).</p>



<p id="viewer-tlp4">This study thus reveals an overview of the current state of plastics in Antarctica, the possible sources, impacts and measures that are being taken. Nano-plastics usually are originated in commercial products and their consequent fragmentation, in pharmaceutical activity, detergents, cosmetics, etc. Although remote, a considerable part of the occurrence in Antarctica is brought by oceanic and atmospheric currents, which end up aggregating marine “garbage” more strongly in some regions than others. Currently, the Antarctic Peninsula region, in the Atlantic sector of the Southern Ocean, is the most affected region in Antarctica, and the one that suffers the most human pressure. In addition to the origins mentioned above, fishing and tourism are also a major source of plastic pollution in the Southern Ocean.</p>



<p id="viewer-73lig">In addition to their presence, in the oceans, ice shelves, continents and Antarctic islands, the ingestion of plastics has already across the different species have also been documented, from birds (i.e.: albatrosses, penguins), fish (i.e.: icefish, cod from Patagonia), benthos (sea urchin), etc.</p>



<div class="wp-block-image"><figure class="aligncenter size-full is-resized"><img loading="lazy" decoding="async" src="https://apecsportugal.pt//wp-content/uploads/2022/08/1-s2.0-S2772735122000488-gr2.jpg" alt="" class="wp-image-3877" width="518" height="317" srcset="https://apecsportugal.pt/wp-content/uploads/2022/08/1-s2.0-S2772735122000488-gr2.jpg 690w, https://apecsportugal.pt/wp-content/uploads/2022/08/1-s2.0-S2772735122000488-gr2-300x183.jpg 300w" sizes="(max-width: 518px) 100vw, 518px" /><figcaption>Figure 1 – Distribution of the various areas and species where the presence and ingestion of plastics in Antarctica and the Southern Ocean have already been documented.</figcaption></figure></div>



<p id="viewer-36j2k">Among the impacts, plastic can serve as a carrier of bacteria and pathogens, which do not normally occur in Antarctica, and thus have serious consequences for the local fauna and flora. Ingestion by different species can also bring health risks to the animals themselves since many of these plastics have toxic chemicals in their composition. On the other hand, the ingestion of large pieces, such as ropes, fishing nets, lines, has already caused the death of countless individuals, or strangulation situations that cause serious wounds and inflammation.</p>



<p id="viewer-1i0uj">Currently, with the recognition of this problem, many of the most active players in this region have been creating conditions and measures aimed at reducing the introduction of plastic in this crucial area of planet Earth. As an example, the Scientific Committee on Antarctica Research (SCAR) created in 2018 a working group exclusively dedicated to understanding and evaluating the different sources, distribution and occurrence of plastic. The Antarctic Treaty itself is also integrating this new challenge, and its Annex IV already mentions the total ban on any plastic disposal in Antarctic waters. In turn, the Convention for the Conservation of Antarctic Marine Living Resources (CCAMLR) has imposed the reduction of various plastic objects to the minimum possible in fishing activities. Finally, tourism has increasingly carried out educational activities in this area, cleaning coastal areas, and supporting research and conservation in this regard.</p>



<p id="viewer-4dre2">Ahead, there is still the challenge of understanding as best as possible the real effects that plastic will have in this region, and how we can effectively mitigate it. However, stakeholders, from governments, companies, tourism, science, are moving in the direction to fight this problem together.</p>



<p id="viewer-6dmd">&#8212;&#8212;&#8212;&#8212;&#8211;</p>



<p id="viewer-bmsbh"><strong>Source:</strong> Caruso, G., Bergami, E., Singh, N., &amp; Corsi, I. (2022). Plastic occurrence, sources, and impacts in Antarctic environment and biota. Water Biology and Security, 100034. <a rel="noreferrer noopener" href="https://doi.org/10.1016/j.watbs.2022.100034" target="_blank">https://doi.org/10.1016/j.watbs.2022.100034</a></p>



<p id="viewer-7jj2g"><strong>Authors:</strong> Diana Rodrigues and José Abreu</p>
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		<title>Persistent organic pollutants: Implications for Antarctic ecosystems</title>
		<link>https://apecsportugal.pt/en/2022/05/15/persistent-organic-pollutants-implications-for-antarctic-ecosystems/</link>
					<comments>https://apecsportugal.pt/en/2022/05/15/persistent-organic-pollutants-implications-for-antarctic-ecosystems/#respond</comments>
		
		<dc:creator><![CDATA[APECS]]></dc:creator>
		<pubDate>Sun, 15 May 2022 23:47:00 +0000</pubDate>
				<category><![CDATA[Antartic]]></category>
		<category><![CDATA[Environmental contaminants]]></category>
		<category><![CDATA[Monitorization]]></category>
		<guid isPermaLink="false">http://site-teste.infinityfreeapp.com/?p=3026</guid>

					<description><![CDATA[In recent years there has been an increase in the number of scientists and tourists in the Antarctic region, which has led to a significant increase in the anthropogenic footprint in the Antarctic ecosystem. In recent years, several studies have detected macro and microplastics, persistent organic pollutants (POPs), and pharmaceutical and personal care products (PPCPs) [&#8230;]]]></description>
										<content:encoded><![CDATA[
<p>In recent years there has been an increase in the number of scientists and tourists in the Antarctic region, which has led to a significant increase in the anthropogenic footprint in the Antarctic ecosystem. In recent years, several studies have detected macro and microplastics, persistent organic pollutants (POPs), and pharmaceutical and personal care products (PPCPs) in polar ecosystems. However, regarding POPs and PPCPs, little is known about their presence in organisms along food chains, especially in the phytoplankton community, which is the base of the marine food web.</p>



<div class="wp-block-image"><figure class="aligncenter size-full"><img loading="lazy" decoding="async" width="360" height="245" src="https://apecsportugal.pt//wp-content/uploads/2022/06/d5d705_69221ed7ace94e0ca377b170b3ce8795mv2.webp" alt="" class="wp-image-3024" srcset="https://apecsportugal.pt/wp-content/uploads/2022/06/d5d705_69221ed7ace94e0ca377b170b3ce8795mv2.webp 360w, https://apecsportugal.pt/wp-content/uploads/2022/06/d5d705_69221ed7ace94e0ca377b170b3ce8795mv2-300x204.webp 300w" sizes="(max-width: 360px) 100vw, 360px" /><figcaption>Tourism in Antarctica. Photograph of Peter Prokosch</figcaption></figure></div>



<p id="viewer-4le58">In a recent study, young Portuguese scientists used mass spectrophotometry techniques in order to carry out the first screening for the presence of emerging contaminants (such as POPs and PPCPs) in the phytoplankton community of a remote island in Antarctica, which is visited by tourist and scientists, thus providing important information about the human footprint left in these remote ecosystems.</p>



<p id="viewer-beei">More than 70 persistent pollutants of human origin (including POPs and PPCPs, among others) were detected. Overall, the variety of compounds detected, as well as their uses, may be linked to both terrestrial and marine activities, thus highlighting the anthropogenic contribution to the Antarctic ecosystem. The detection of these compounds at the base of the Antarctic food chain, which can be potentially toxic depending on their concentration, could have very serious implications for the entire trophic structure of the ecosystem, putting the various organisms at risk.</p>



<p id="viewer-795be">That said, this study emphasizes the knowledge gap that exists regarding the potentially toxic effects that these pollutants can have on the various organisms in the Antarctic food chain. It also emphasizes the need to review the guidelines imposed by the Antarctic Treaty and by the Environmental Protection Protocol to the Antarctic Treaty, so that there is a control and/or avoidance of the proliferation of these and other PPCPs in remote environments as unique as is the case of Antarctica.</p>



<p id="viewer-f140a">&#8212;&#8212;&#8212;&#8212;&#8212;&#8212;&#8212;</p>



<p id="viewer-d3bgf"><strong>Source:</strong>Duarte, B., Gameiro, C., Matos, A. R., Figueiredo, A., Silva, M. S., Cordeiro, C., Caçador, I., Reis-Santos, P., Fonseca, V., &amp; Cabrita, M. T. (2021). First screening of biocides, persistent organic pollutants, pharmaceutical and personal care products in Antarctic phytoplankton from Deception Island by FT-ICR-MS. <em>Chemosphere</em>, <em>274</em>, 129860. <a href="https://www.sciencedirect.com/science/article/abs/pii/S0045653521003295?via%3Dihub" target="_blank" rel="noreferrer noopener"><u>https://doi.org/10.1016/j.chemosphere.2021.129860</u></a></p>



<p id="viewer-agomk"><strong>Author: </strong>Joana Fragão</p>
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