<?xml version="1.0" encoding="UTF-8"?>
<!DOCTYPE article PUBLIC "-//NLM//DTD JATS (Z39.96) Journal Publishing DTD v1.2 20190208//EN" "https://jats.nlm.nih.gov/publishing/1.2/JATS-journalpublishing1.dtd">
<article xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:mml="http://www.w3.org/1998/Math/MathML" article-type="brief-report" dtd-version="1.2" xml:lang="en">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">IJOMS</journal-id>
<journal-title-group><journal-title>International Journal of Oceanography Marine Studies</journal-title></journal-title-group>
<publisher><publisher-name>Thomson &amp; Ryberg Publications</publisher-name></publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.62715/ijoms.2026.v1.i1.pp26-30</article-id>
<article-id pub-id-type="publisher-id">45ebe3264a</article-id>
<article-categories><subj-group subj-group-type="heading"><subject>Short Communication</subject></subj-group></article-categories>
<title-group><article-title>Microplastic Counts in Zooplankton Tows From an Upwelling Region Off West Africa: A Technical Note on Sampling and Interpretation</article-title></title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes"><name><surname>Chukwu</surname><given-names>Nurlan</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1">*</xref></contrib>
<contrib contrib-type="author"><name><surname>Grigoryan</surname><given-names>Sebastien</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib>
<contrib contrib-type="author"><name><surname>Gauthier</surname><given-names>Katarzyna</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib>
<aff id="aff1"><label>1</label>Department of Geology, Carpathian Institute for Advanced Geology, Taiwan</aff>
<aff id="aff2"><label>2</label>Department of Geology, Amazon School of Geology, Spain</aff>
<aff id="aff3"><label>3</label>Department of Geology, Sharavati Research Institute of Geology, Trinidad and Tobago</aff>
</contrib-group>
<author-notes><corresp id="cor1">* Correspondence: <email>nurlan.chukwu@carpathian.edu</email></corresp></author-notes>
<pub-date pub-type="epub" iso-8601-date="2026-02-25"><day>25</day><month>02</month><year>2026</year></pub-date>
<volume>1</volume>
<issue>1</issue>
<fpage>26</fpage>
<lpage>30</lpage>
<history>
<date date-type="received" iso-8601-date="2025-10-26"><day>26</day><month>10</month><year>2025</year></date>
<date date-type="accepted" iso-8601-date="2025-12-25"><day>25</day><month>12</month><year>2025</year></date>
</history>
<permissions><copyright-statement>© 2026 The Author(s)</copyright-statement><copyright-year>2026</copyright-year><license license-type="open-access" xlink:href="https://creativecommons.org/licenses/by/4.0/"><license-p>This is an open access article distributed under the Creative Commons Attribution 4.0 International License (CC BY 4.0).</license-p></license></permissions>
<self-uri xlink:href="https://trpub.org/article.php?id=45ebe3264a"/>
<abstract><p>Zooplankton nets are towed routinely on fisheries and oceanographic cruises in the Canary Current upwelling system off north-west Africa, and the samples they bring up contain synthetic particles and fibres alongside the animals. Counting those particles is an attractive way to obtain microplastic data from a region where dedicated surveys are few, because the ship time, the nets and often the archived samples already exist. This technical note considers what such counts can and cannot show. It reports no new measurements. It explains why a plankton net is an imperfect microplastic sampler, how the mesh and the dense blooms typical of upwelling affect what is retained, and how the offshore movement of surface water and its return at fronts are expected to shape where buoyant particles collect. It distinguishes three quantities that are often confused: particles per volume of water, particles relative to plankton biomass, and particles found inside the animals. The note then summarises the contamination controls and polymer confirmation that published quality criteria require, and suggests a minimum set of information that should accompany any count taken from a zooplankton tow so that results from different cruises and laboratories off West Africa can be compared.</p></abstract>
<kwd-group kwd-group-type="author">
<kwd>Microplastics</kwd>
<kwd>Zooplankton</kwd>
<kwd>Canary Current</kwd>
<kwd>Coastal upwelling</kwd>
<kwd>Plankton nets</kwd>
<kwd>Contamination control</kwd>
</kwd-group>
</article-meta>
</front>
<body>
<sec id="sec1"><title>1. Introduction</title>
<p>The coast from Morocco to Senegal and Guinea borders one of the four great eastern boundary upwelling systems. Trade winds drive surface water offshore, cold nutrient-rich water rises to replace it, and the resulting production supports large stocks of sardine, sardinella and horse mackerel. Upwelling is permanent off Mauritania and seasonal to the north and south, and the system is strongly structured by capes, filaments and fronts (Arístegui et al., 2009). Zooplankton are sampled here regularly in support of fisheries assessment, usually with vertical or oblique tows of fine-meshed nets.</p>
<p>Those samples have a second potential use. Thompson et al. (2004) showed, using archived material from the Continuous Plankton Recorder, that plankton samples collected for another purpose can yield a history of microplastic in the sea. Zooplankton also ingest microplastic particles in laboratory exposures (Cole et al., 2013), and ingestion has been confirmed in copepods and euphausiids caught at sea (Desforges et al., 2015). For a region with little dedicated monitoring, counting plastic in existing tows is an obvious step. This note sets out the conditions under which such counts are meaningful. It is a commentary on method and presents no data.</p>
</sec>
<sec id="sec2"><title>2. The Net as a Microplastic Sampler</title>
<p>A plankton net retains what is larger than its mesh and passes most of what is smaller. Standard zooplankton nets have meshes of roughly 200 micrometres, and the manta and neuston nets normally used for floating plastic are coarser still (Harris et al., 2000; Hidalgo-Ruz et al., 2012). Since small particles greatly outnumber large ones, the mesh largely determines the count: Lindeque et al. (2020) compared nets of different mesh towed together and found that finer nets captured far higher concentrations. Fibres complicate matters further, because a long thin fibre may pass end-on through a mesh that its length would not. A count is therefore a property of the water and the net together, and cannot be compared with a count made using a different mesh without qualification.</p>
<p>Upwelling adds a difficulty of its own. Blooms of chain-forming diatoms and swarms of gelatinous animals clog fine meshes within minutes. A clogged net filters less water than its flowmeter may indicate, and it retains particles smaller than its nominal mesh, so that the volume and the size cut-off both drift during a tow. Short tows, a flowmeter mounted in the mouth, and a record of net condition on recovery are the practical safeguards. Vertical hauls through the whole water column raise a further point: they integrate over depth, whereas buoyant polymers concentrate at the surface, and a surface tow and a vertical haul at the same station measure different things.</p>
</sec>
<sec id="sec3"><title>3. What Upwelling Does to the Distribution</title>
<p>Buoyant particles follow the surface flow. In an upwelling cell that flow is directed offshore, which should carry floating plastic away from the coast and leave freshly upwelled water comparatively clean, while convergent fronts and the edges of filaments gather floating material together with plankton. The expected pattern is therefore patchy and tied to hydrography, not a smooth gradient from land. Kanhai et al. (2017) sampled subsurface water along a latitudinal transect of the Atlantic that crossed the upwelling system off south-western Africa and examined upwelling among the factors that might affect abundance. For West Africa the practical lesson is that each tow should be placed in its oceanographic setting, with temperature, salinity and chlorophyll recorded, and that a single station cannot represent the region.</p>
<p>Sources add a second layer of structure. Along this coast synthetic material enters the sea from a small number of cities and river mouths, from artisanal landing beaches, and from the industrial and artisanal fleets that work the shelf, whose ropes and netting are themselves polymer. Fragments and fibres of fishing gear should therefore be expected on the fishing grounds irrespective of distance from land, and a count that separates fibres, fragments, films and pellets, and records colour, says far more about origin than a single total. Seasonal sampling matters for the same reason: the wet season brings river discharge to the southern part of the region at a time when upwelling there is weak.</p>
<p>Counts can be expressed in several ways, which answer different questions. Table 1 sets them out. In highly productive water the ratio of plastic to plankton may be low even where the concentration per cubic metre is not, simply because there is so much plankton, and the reverse holds in the oligotrophic water offshore.</p>
<table-wrap id="tbl1"><label>Table 1</label><caption><p>Ways of expressing microplastic counts from a zooplankton tow and what each can support</p></caption><table frame="hsides" rules="groups"><thead><tr><th>Quantity</th><th>What it describes</th><th>Main caveat</th></tr></thead><tbody><tr><td>Particles per cubic metre</td><td>Concentration in the water sampled</td><td>Depends on mesh, clogging and flowmeter accuracy</td></tr><tr><td>Particles per unit area of sea surface</td><td>Load in a surface tow</td><td>Sensitive to wind mixing during the tow</td></tr><tr><td>Particles relative to plankton biomass or number</td><td>Encounter rate for planktivores</td><td>Driven as much by plankton as by plastic</td></tr><tr><td>Particles per individual animal</td><td>Ingestion by a named taxon</td><td>Needs rinsed, individually picked animals and blanks</td></tr><tr><td>Proportion by shape and polymer</td><td>Likely sources</td><td>Only valid for spectroscopically confirmed particles</td></tr></tbody></table></table-wrap>
</sec>
<sec id="sec4"><title>4. From Sample to Count</title>
<p>Most of the error in microplastic work arises after the net is on deck, and Figure 1 follows a sample through the stages at which a count can be inflated or reduced. Particles in the cod end are a mixture of those free in the water and those inside or stuck to animals, and the two can be separated only if animals are picked out and rinsed before digestion. To free ingested particles the tissue must be dissolved without damaging the polymers. Strong acids destroy some plastics, and Cole et al. (2014) showed that enzymatic digestion removes most biological material from plankton-rich samples while leaving microplastic intact. Formalin-preserved archive samples can be examined, but the history of the jars and lids must be considered.</p>
<fig id="fig1"><label>Figure 1</label><caption><p>Stages between the tow and the reported count, with the main risk to the count at each stage</p></caption><graphic xlink:href="IJOMS_V1I1_2026_05_Figure1.png" mimetype="image" mime-subtype="png"/></fig>
<p>Contamination is the central problem for fibres. Clothing, ropes, the net itself and laboratory air all shed them, and Woodall et al. (2015) set out forensic-style precautions: cotton clothing of known colour, covered samples, filtered reagents, and blanks exposed alongside every sample. A critical review of studies of biota found that few met basic quality criteria, and it proposed a scoring scheme covering sampling, laboratory conditions, blanks, positive controls and polymer identification (Hermsen et al., 2018). Visual identification alone misclassifies many particles, natural fibres and fragments of shell among them, so that a defined subsample must be confirmed by infrared or Raman spectroscopy (Hidalgo-Ruz et al., 2012). On a fisheries vessel, fragments of the ship&#x27;s own paint and net twine are likely contaminants, and reference scrapings should be taken for comparison.</p>
<p>Losses deserve the same attention as additions. Particles adhere to the net, to sieves and to the walls of digestion vessels, and the smallest are easily overlooked under a dissecting microscope. The usual check is a positive control: a known number of reference particles of several polymers and shapes is added to a plankton sample, carried through the whole procedure and counted at the end. The recovery obtained should be stated with the results, and counts should not be adjusted upward for it without saying so.</p>
</sec>
<sec id="sec5"><title>5. Minimum Information to Report</title>
<p>Comparability across cruises depends less on a single agreed method than on complete reporting. A count from a zooplankton tow should state the net type, mouth area and mesh; whether the tow was vertical, oblique or at the surface, and over what depth; the volume filtered and how it was measured; the wind and sea state; the hydrographic setting of the station relative to the upwelling front; the preservation and digestion used; the lower size limit actually counted; the number and results of procedural blanks, with any correction applied; and the proportion of particles confirmed by spectroscopy. Ingestion should be reported per individual of a named taxon and life stage, with the number of animals examined, and kept separate from the count of free particles. Reviews of zooplankton and microplastic have noted how often such details are missing and how much this limits synthesis (Botterell et al., 2019).</p>
</sec>
<sec id="sec6"><title>6. Conclusion</title>
<p>Zooplankton tows off West Africa are a ready source of microplastic observations in an under-sampled and productive part of the ocean, and archived collections may extend the record backward. Their value depends on recognising that the net was designed for animals, that upwelling circulation makes the distribution of floating particles patchy, and that blooms change what a net retains. Counts reported with mesh, volume, setting, blanks and polymer confirmation can be compared and built upon. Counts reported without them add numbers to the literature but little knowledge.</p>
</sec>
<sec id="sec7"><title>Conflict of interest</title>
<p>To be declared by the author(s) before publication.</p>
</sec>
<sec id="sec8"><title>Funding</title>
<p>To be declared by the author(s) before publication.</p>
</sec>
</body>
<back>
<ref-list><title>References</title>
<ref id="ref1"><label>1</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Arístegui, J., Barton, E.D., Álvarez-Salgado, X.A., Santos, A.M.P., Figueiras, F.G., Kifani, S. et al.</string-name></person-group> (<year>2009</year>). <article-title>Sub-regional ecosystem variability in the Canary Current upwelling</article-title>. <source>Progress in Oceanography</source>, <volume>83(1-4)</volume>, <fpage>33-48</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.pocean.2009.07.031">https://doi.org/10.1016/j.pocean.2009.07.031</ext-link></mixed-citation></ref>
<ref id="ref2"><label>2</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Botterell, Z.L.R., Beaumont, N., Dorrington, T., Steinke, M., Thompson, R.C. and Lindeque, P.K.</string-name></person-group> (<year>2019</year>). <article-title>Bioavailability and effects of microplastics on marine zooplankton: A review</article-title>. <source>Environmental Pollution</source>, <volume>245</volume>, <fpage>98-110</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.envpol.2018.10.065">https://doi.org/10.1016/j.envpol.2018.10.065</ext-link></mixed-citation></ref>
<ref id="ref3"><label>3</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Cole, M., Lindeque, P., Fileman, E., Halsband, C., Goodhead, R., Moger, J. and Galloway, T.S.</string-name></person-group> (<year>2013</year>). <article-title>Microplastic ingestion by zooplankton</article-title>. <source>Environmental Science &amp; Technology</source>, <volume>47(12)</volume>, <fpage>6646-6655</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1021/es400663f">https://doi.org/10.1021/es400663f</ext-link></mixed-citation></ref>
<ref id="ref4"><label>4</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Cole, M., Webb, H., Lindeque, P.K., Fileman, E.S., Halsband, C. and Galloway, T.S.</string-name></person-group> (<year>2014</year>). <article-title>Isolation of microplastics in biota-rich seawater samples and marine organisms</article-title>. <source>Scientific Reports</source>, <volume>4</volume>, <fpage>4528</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1038/srep04528">https://doi.org/10.1038/srep04528</ext-link></mixed-citation></ref>
<ref id="ref5"><label>5</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Desforges, J.-P.W., Galbraith, M. and Ross, P.S.</string-name></person-group> (<year>2015</year>). <article-title>Ingestion of microplastics by zooplankton in the Northeast Pacific Ocean</article-title>. <source>Archives of Environmental Contamination and Toxicology</source>, <volume>69(3)</volume>, <fpage>320-330</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1007/s00244-015-0172-5">https://doi.org/10.1007/s00244-015-0172-5</ext-link></mixed-citation></ref>
<ref id="ref6"><label>6</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Harris, R., Wiebe, P., Lenz, J., Skjoldal, H.R. and Huntley, M. (eds)</string-name></person-group> (<year>2000</year>). <article-title>ICES Zooplankton Methodology Manual</article-title>. <source>Academic Press, London</source></mixed-citation></ref>
<ref id="ref7"><label>7</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Hermsen, E., Mintenig, S.M., Besseling, E. and Koelmans, A.A.</string-name></person-group> (<year>2018</year>). <article-title>Quality criteria for the analysis of microplastic in biota samples: A critical review</article-title>. <source>Environmental Science &amp; Technology</source>, <volume>52(18)</volume>, <fpage>10230-10240</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1021/acs.est.8b01611">https://doi.org/10.1021/acs.est.8b01611</ext-link></mixed-citation></ref>
<ref id="ref8"><label>8</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Hidalgo-Ruz, V., Gutow, L., Thompson, R.C. and Thiel, M.</string-name></person-group> (<year>2012</year>). <article-title>Microplastics in the marine environment: A review of the methods used for identification and quantification</article-title>. <source>Environmental Science &amp; Technology</source>, <volume>46(6)</volume>, <fpage>3060-3075</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1021/es2031505">https://doi.org/10.1021/es2031505</ext-link></mixed-citation></ref>
<ref id="ref9"><label>9</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Kanhai, L.D.K., Officer, R., Lyashevska, O., Thompson, R.C. and O&#x27;Connor, I.</string-name></person-group> (<year>2017</year>). <article-title>Microplastic abundance, distribution and composition along a latitudinal gradient in the Atlantic Ocean</article-title>. <source>Marine Pollution Bulletin</source>, <volume>115(1-2)</volume>, <fpage>307-314</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.marpolbul.2016.12.025">https://doi.org/10.1016/j.marpolbul.2016.12.025</ext-link></mixed-citation></ref>
<ref id="ref10"><label>10</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Lindeque, P.K., Cole, M., Coppock, R.L., Lewis, C.N., Miller, R.Z., Watts, A.J.R. et al.</string-name></person-group> (<year>2020</year>). <article-title>Are we underestimating microplastic abundance in the marine environment? A comparison of microplastic capture with nets of different mesh-size</article-title>. <source>Environmental Pollution</source>, <volume>265</volume>, <fpage>114721</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.envpol.2020.114721">https://doi.org/10.1016/j.envpol.2020.114721</ext-link></mixed-citation></ref>
<ref id="ref11"><label>11</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Thompson, R.C., Olsen, Y., Mitchell, R.P., Davis, A., Rowland, S.J., John, A.W.G., McGonigle, D. and Russell, A.E.</string-name></person-group> (<year>2004</year>). <article-title>Lost at sea: Where is all the plastic?</article-title>. <source>Science</source>, <volume>304(5672)</volume>, <fpage>838</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1126/science.1094559">https://doi.org/10.1126/science.1094559</ext-link></mixed-citation></ref>
<ref id="ref12"><label>12</label><mixed-citation publication-type="other"><person-group person-group-type="author"><string-name>Woodall, L.C., Gwinnett, C., Packer, M., Thompson, R.C., Robinson, L.F. and Paterson, G.L.J.</string-name></person-group> (<year>2015</year>). <article-title>Using a forensic science approach to minimize environmental contamination and to identify microfibres in marine sediments</article-title>. <source>Marine Pollution Bulletin</source>, <volume>95(1)</volume>, <fpage>40-46</fpage> <ext-link ext-link-type="uri" xlink:href="https://doi.org/10.1016/j.marpolbul.2015.04.044">https://doi.org/10.1016/j.marpolbul.2015.04.044</ext-link></mixed-citation></ref>
</ref-list>
</back>
</article>