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Santiago Cuervo - Academia.edu

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class="uploads-container" id="social-redesign-work-container"><div class="upload-header"><h2 class="ds2-5-heading-sans-serif-xs">Uploads</h2></div><div class="documents-container backbone-social-profile-documents" style="width: 100%;"><div class="u-taCenter"></div><div class="profile--tab_content_container js-tab-pane tab-pane active" id="all"><div class="profile--tab_heading_container js-section-heading" data-section="Papers" id="Papers"><h3 class="profile--tab_heading_container">Papers by Santiago Cuervo</h3></div><div class="js-work-strip profile--work_container" data-work-id="90855838"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855838/Emergent_cooperation_through_mutual_information_maximization"><img alt="Research paper thumbnail of Emergent cooperation through mutual information maximization" class="work-thumbnail" src="https://attachments.academia-assets.com/94302584/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855838/Emergent_cooperation_through_mutual_information_maximization">Emergent cooperation through mutual information maximization</a></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="4bc4d31b1d003afd9639fc4c6a138e50" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302584,&quot;asset_id&quot;:90855838,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302584/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa 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interact among them to work efficiently. With this in mind, we propose a decentralized deep reinforcement learning algorithm for the design of cooperative multi-agent systems. The algorithm is based on the hypothesis that highly correlated actions are a feature of cooperative systems, and hence, we propose the insertion of an auxiliary objective of maximization of the mutual information between the actions of agents in the learning problem. Our system is applied to a social dilemma, a problem whose optimal solution requires that agents cooperate to maximize a macroscopic performance function despite the divergent individual objectives of each agent. By comparing the performance of the proposed system to a system without the auxiliary objective, we conclude that the maximization of mutual information among agents promotes the emergence of cooperation in social dilemmas.","publication_date":{"day":21,"month":6,"year":2020,"errors":{}},"grobid_abstract_attachment_id":94302584},"translated_abstract":null,"internal_url":"https://www.academia.edu/90855838/Emergent_cooperation_through_mutual_information_maximization","translated_internal_url":"","created_at":"2022-11-15T11:55:48.097-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":94302584,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302584/thumbnails/1.jpg","file_name":"2006.11769.pdf","download_url":"https://www.academia.edu/attachments/94302584/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Emergent_cooperation_through_mutual_info.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302584/2006.11769-libre.pdf?1668542894=\u0026response-content-disposition=attachment%3B+filename%3DEmergent_cooperation_through_mutual_info.pdf\u0026Expires=1732746820\u0026Signature=U0DYqGqlNtxjCgZTjg6ZtibQC~hgJoqCD0jJarN1ImwNQqNd9gsGWTq6LdC6-iKxpGIW5Fi8CvC27bx-u0LFyrpjeiajjOjidIehMKRjjHucYV5KcDKrVxGcQDLbN7Uu4NcrO1q2Sv7IMG~4SMPuYbkoD6l5jIc97F3m~OsLvYS7xuiAC0DgXUhawBy~HfYP6Gnmi0O8kC2IqGE1J1FmfNOTVpCUygB~-~piNKZ~Yjy7EZcUgmonvcBRptv3JPOiSdIwIbdhluaVARQIWf62mjXykjw4pWqdsO5FfDfh~j0yVkb5k-s4G-TL4vR4zD3zBZe4Decj7Lj6bkLZA8Ih-w__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Emergent_cooperation_through_mutual_information_maximization","translated_slug":"","page_count":20,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago 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<div class="js-work-strip profile--work_container" data-work-id="90855837"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855837/Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech"><img alt="Research paper thumbnail of Variable-rate hierarchical CPC leads to acoustic unit discovery in speech" class="work-thumbnail" src="https://attachments.academia-assets.com/94302582/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855837/Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech">Variable-rate hierarchical CPC leads to acoustic unit discovery in speech</a></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="2ef105e4a59ed622a168b95cf9d62ce4" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302582,&quot;asset_id&quot;:90855837,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302582/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855837"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855837"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855837; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855837]").text(description); $(".js-view-count[data-work-id=90855837]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855837; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855837']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); 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{"id":90855837,"title":"Variable-rate hierarchical CPC leads to acoustic unit discovery in speech","translated_title":"","metadata":{"grobid_abstract":"The success of deep learning comes from its ability to capture the hierarchical structure of data by learning high-level representations defined in terms of low-level ones. In this paper we explore self-supervised learning of hierarchical representations of speech by applying multiple levels of Contrastive Predictive Coding (CPC). We observe that simply stacking two CPC models does not yield significant improvements over single-level architectures. Inspired by the fact that speech is often described as a sequence of discrete units unevenly distributed in time, we propose a model in which the output of a low-level CPC module is non-uniformly downsampled to directly minimize the loss of a high-level CPC module. The latter is designed to also enforce a prior of separability and discreteness in its representations by enforcing dissimilarity of successive high-level representations through focused negative sampling, and by quantization of the prediction targets. 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Nature based solutions for winery wastewater valorisation" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855823/Nature_based_solutions_for_winery_wastewater_valorisation">Nature based solutions for winery wastewater valorisation</a></div><div class="wp-workCard_item"><span>Ecological Engineering</span><span>, 2021</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation o...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). The WETWINE plant is located in Tomino (Pontevedra, Spain) and is being validated at the demo-scale at Santiago Ruiz Winery (NW Spain). The plant consisted of a HUSB reactor for removing suspended solids and hydrolyse organic matter, followed by two vertical subsurface flow constructed wetland (VF) operating in parallel and to provide further treatment, a horizontal subsurface flow constructed wetland (HF) operating in series. After two years of continuous monitoring and regardless in the variation of flow and load, the hybrid system achieved average removal efficiencies of over 93% for total suspended solids and chemical oxygen demand, receiving an overall surface loading of up to 115 g COD/m2·d. Total nitrogen removal reached 62% with an average concertation of 21 mg N/ L. The WETWINE plant was also able to increased the pH in the effluent from 5.5 at the influent to 7.2.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855823"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855823"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855823; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855823]").text(description); $(".js-view-count[data-work-id=90855823]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855823; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855823']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855823, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855823]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855823,"title":"Nature based solutions for winery wastewater valorisation","translated_title":"","metadata":{"abstract":"Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). 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The WETWINE plant was also able to increased the pH in the effluent from 5.5 at the influent to 7.2.","publisher":"Elsevier BV","publication_date":{"day":null,"month":null,"year":2021,"errors":{}},"publication_name":"Ecological Engineering"},"translated_abstract":"Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). The WETWINE plant is located in Tomino (Pontevedra, Spain) and is being validated at the demo-scale at Santiago Ruiz Winery (NW Spain). The plant consisted of a HUSB reactor for removing suspended solids and hydrolyse organic matter, followed by two vertical subsurface flow constructed wetland (VF) operating in parallel and to provide further treatment, a horizontal subsurface flow constructed wetland (HF) operating in series. 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How...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. However, the underlying mechanisms are not fully understood, and the existing reports only deal with soil-grown plants. Thus, the purpose of this experiment was to assess whether or not MTW affects main physiological processes (gas exchange, biomass accumulation and water potential) in tomato plants whose water supply was only MTW. Two experiments were done in hydroponic semi-controlled conditions, consisting of a loop system with permanent recirculation of water through a non-uniform magnet. The plants grown under MTW showed a significant increase in chlorophyll content, photosynthesis and transpiration at high light irradiances, although the increase in stomatal conductance was less significant. MTW also increased fruit fresh biomass, number of fruits and root dry biomass in 61.7 %, 85.3 % and 30.3 % respectively, but this was only achieved at natural sunlight conditions. Moreover, treate...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="f4ba848f57a818e4c567d5c7e994d537" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302613,&quot;asset_id&quot;:90855819,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302613/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855819"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855819"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855819; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855819]").text(description); $(".js-view-count[data-work-id=90855819]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855819; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855819']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855819, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "f4ba848f57a818e4c567d5c7e994d537" } } $('.js-work-strip[data-work-id=90855819]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855819,"title":"Biomass accumulation and physiological responses of tomato plants to magnetically–treated water in hydroponic conditions","translated_title":"","metadata":{"abstract":"Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855818"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators"><img alt="Research paper thumbnail of Diffuse methane emissions abatement by organic and inorganic packed biofilters: Assessment of operational and environmental indicators" class="work-thumbnail" src="https://attachments.academia-assets.com/94302608/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators">Diffuse methane emissions abatement by organic and inorganic packed biofilters: Assessment of operational and environmental indicators</a></div><div class="wp-workCard_item"><span>Journal of Cleaner Production</span><span>, 2017</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="74878a39745b9560f01561393dc59769" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302608,&quot;asset_id&quot;:90855818,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855818"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855818"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855818; 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The use of different packing materials including a mixture of pine bark, perlite and compost for the organic biofilter and polyurethane foam for the inorganic one was evaluated. The influence of other major variables on the removal efficiency such as nutrient requirements, operational conditions and long-term stability were also assessed in both configurations. The analysis of the biofilters operation proved that both configurations provided a feasible and stable performance in the treatment of diffuse methane emissions. Once the operational feasibility of both systems was proved, the environmental assessment was performed. The main hotspots found in the analysis were attributed to the requirement of nutrients, infrastructure, waste disposal and direct emissions to the atmosphere. A sensitivity analysis was performed in terms of nutrient supply and infrastructure material which revealed that special attention needs to be paid to the formulation of the nutrient solution in terms of concentration and source of nitrogen.","publication_date":{"day":null,"month":null,"year":2017,"errors":{}},"publication_name":"Journal of Cleaner Production","grobid_abstract_attachment_id":94302608},"translated_abstract":null,"internal_url":"https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators","translated_internal_url":"","created_at":"2022-11-15T11:55:22.761-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":94302608,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302608/thumbnails/1.jpg","file_name":"j.jclepro.2016.11.18520221115-1-1e0g4d0.pdf","download_url":"https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Diffuse_methane_emissions_abatement_by_o.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302608/j.jclepro.2016.11.18520221115-1-1e0g4d0-libre.pdf?1668542723=\u0026response-content-disposition=attachment%3B+filename%3DDiffuse_methane_emissions_abatement_by_o.pdf\u0026Expires=1732746820\u0026Signature=Lul6HHcKimiIMK90obSob2WoxXuv4iiJdr4rt9ifXcc~NaAlStUzk2TYW6iKxRIT1nqLhdtUlqnYgBwel~TIFAV1L0K-O0o1mHWmTD5R8ARTEF6bFNLVttair6V0cHiSqnxN4R08f30RdBGT0rOsAQw6~~gVcD4a3LLRMZdxc0d6ekFXazmuXvYY158ruzKDYI3kb7V9e5SvpvlMPtbGeuB6Vcx2GYXWUTLUN3xR36QZNJDbe0lzJbkvyHp9MOa-by0NYHNSgLDumipBEX2JcyBMqU8VzNeElpQsWwGpjPq1SNO43lGmiRq9HksRim-0jo~-JySMTNQHV4hQ0YYmiQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators","translated_slug":"","page_count":12,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[{"id":94302608,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302608/thumbnails/1.jpg","file_name":"j.jclepro.2016.11.18520221115-1-1e0g4d0.pdf","download_url":"https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Diffuse_methane_emissions_abatement_by_o.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302608/j.jclepro.2016.11.18520221115-1-1e0g4d0-libre.pdf?1668542723=\u0026response-content-disposition=attachment%3B+filename%3DDiffuse_methane_emissions_abatement_by_o.pdf\u0026Expires=1732746820\u0026Signature=Lul6HHcKimiIMK90obSob2WoxXuv4iiJdr4rt9ifXcc~NaAlStUzk2TYW6iKxRIT1nqLhdtUlqnYgBwel~TIFAV1L0K-O0o1mHWmTD5R8ARTEF6bFNLVttair6V0cHiSqnxN4R08f30RdBGT0rOsAQw6~~gVcD4a3LLRMZdxc0d6ekFXazmuXvYY158ruzKDYI3kb7V9e5SvpvlMPtbGeuB6Vcx2GYXWUTLUN3xR36QZNJDbe0lzJbkvyHp9MOa-by0NYHNSgLDumipBEX2JcyBMqU8VzNeElpQsWwGpjPq1SNO43lGmiRq9HksRim-0jo~-JySMTNQHV4hQ0YYmiQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":55,"name":"Environmental Engineering","url":"https://www.academia.edu/Documents/in/Environmental_Engineering"},{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":1584,"name":"Cleaner Production","url":"https://www.academia.edu/Documents/in/Cleaner_Production"},{"id":14085,"name":"Waste Management","url":"https://www.academia.edu/Documents/in/Waste_Management"},{"id":96825,"name":"Manufacturing Engineering","url":"https://www.academia.edu/Documents/in/Manufacturing_Engineering"},{"id":337999,"name":"Perlite","url":"https://www.academia.edu/Documents/in/Perlite"},{"id":554780,"name":"Interdisciplinary Engineering","url":"https://www.academia.edu/Documents/in/Interdisciplinary_Engineering"},{"id":555091,"name":"Compost","url":"https://www.academia.edu/Documents/in/Compost"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"}],"urls":[{"id":26007888,"url":"https://api.elsevier.com/content/article/PII:S0959652616320479?httpAccept=text/plain"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855816"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation"><img alt="Research paper thumbnail of Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation">Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation</a></div><div class="wp-workCard_item"><span>Environmental Technology</span><span>, 2016</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">ABSTRACT There is growing international concern about the increasing levels of greenhouse gases i...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855816"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855816"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855816; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855816]").text(description); $(".js-view-count[data-work-id=90855816]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855816; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855816']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855816, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855816]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855816,"title":"Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation","translated_title":"","metadata":{"abstract":"ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.","publisher":"Informa UK Limited","publication_date":{"day":null,"month":null,"year":2016,"errors":{}},"publication_name":"Environmental Technology"},"translated_abstract":"ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.","internal_url":"https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation","translated_internal_url":"","created_at":"2022-11-15T11:55:19.087-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[],"research_interests":[{"id":48,"name":"Engineering","url":"https://www.academia.edu/Documents/in/Engineering"},{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":523,"name":"Chemistry","url":"https://www.academia.edu/Documents/in/Chemistry"},{"id":26327,"name":"Medicine","url":"https://www.academia.edu/Documents/in/Medicine"},{"id":47884,"name":"Biological Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":58054,"name":"Environmental Sciences","url":"https://www.academia.edu/Documents/in/Environmental_Sciences"},{"id":88280,"name":"Environmental Technology","url":"https://www.academia.edu/Documents/in/Environmental_Technology"},{"id":122404,"name":"Nitrate","url":"https://www.academia.edu/Documents/in/Nitrate"},{"id":151091,"name":"Nitrogen","url":"https://www.academia.edu/Documents/in/Nitrogen"},{"id":156347,"name":"Methane","url":"https://www.academia.edu/Documents/in/Methane"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"},{"id":803011,"name":"Aeration","url":"https://www.academia.edu/Documents/in/Aeration"}],"urls":[{"id":26007887,"url":"http://www.tandfonline.com/doi/pdf/10.1080/09593330.2015.1135996"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855814"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions"><img alt="Research paper thumbnail of EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions">EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions</a></div><div class="wp-workCard_item"><span>Water, Air, &amp;amp; Soil Pollution</span><span>, 2015</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was car...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855814"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855814"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855814; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855814]").text(description); $(".js-view-count[data-work-id=90855814]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855814; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855814']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855814, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855814]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855814,"title":"EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions","translated_title":"","metadata":{"abstract":"Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.","publisher":"Springer Science and Business Media LLC","publication_date":{"day":null,"month":null,"year":2015,"errors":{}},"publication_name":"Water, Air, \u0026amp; Soil Pollution"},"translated_abstract":"Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.","internal_url":"https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions","translated_internal_url":"","created_at":"2022-11-15T11:55:14.372-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":523,"name":"Chemistry","url":"https://www.academia.edu/Documents/in/Chemistry"},{"id":15836,"name":"Environmental Chemistry","url":"https://www.academia.edu/Documents/in/Environmental_Chemistry"},{"id":28235,"name":"Multidisciplinary","url":"https://www.academia.edu/Documents/in/Multidisciplinary"},{"id":156347,"name":"Methane","url":"https://www.academia.edu/Documents/in/Methane"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"}],"urls":[{"id":26007886,"url":"http://link.springer.com/content/pdf/10.1007/s11270-015-2576-2.pdf"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855813"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855813/Characterization_and_biological_abatement_of_diffuse_methane_emissions_and_odour_in_an_innovative_wastewater_treatment_plant"><img alt="Research paper thumbnail of Characterization and biological abatement of diffuse methane emissions and odour in an innovative wastewater treatment plant" class="work-thumbnail" src="https://attachments.academia-assets.com/94302601/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855813/Characterization_and_biological_abatement_of_diffuse_methane_emissions_and_odour_in_an_innovative_wastewater_treatment_plant">Characterization and biological abatement of diffuse methane emissions and odour in an innovative wastewater treatment plant</a></div><div class="wp-workCard_item"><span>Environmental Technology</span><span>, 2015</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="ee46151c4df385fb5e37493649898134" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302601,&quot;asset_id&quot;:90855813,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302601/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855813"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855813"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855813; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855813]").text(description); $(".js-view-count[data-work-id=90855813]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855813; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855813']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855813, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "ee46151c4df385fb5e37493649898134" } } $('.js-work-strip[data-work-id=90855813]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855813,"title":"Characterization and biological abatement of diffuse methane emissions and odour in an innovative wastewater treatment plant","translated_title":"","metadata":{"publisher":"Informa UK Limited","grobid_abstract":"An innovative and patented process for medium-high strength sewage which comprises an anaerobic step followed by a hybrid anoxic-aerobic chamber and a final ultrafiltration stage was characterized in terms of methane fugitive emissions as well as odours. The operation at ambient temperature implies higher methane content in the liquid anaerobic effluent, which finally causes concentrations around 0.01-2.4% in the off-gas released in the anoxic-aerobic chamber (1.25% average). Mass balances indicate that these emissions account for up to 30-35% of the total methane generated in the anaerobic reactor. A conventional biofilter (BF) operated at an empty bed residence time of 4 min was used to treat these emissions for 70 d. In spite of the fluctuations in the methane inlet concentrations derived from the operation of the wastewater treatment plant (WWTP), it was possible to operate at pseudo-steady-state conditions, achieving average removal efficiencies of 76.5% and maximum elimination capacities of 30.1 g m −3 h −1. Odour removal was quantified as 99.1%. Fluorescence in situ hybridization probes as well as metabolic activity assays demonstrated the suitability of the biomass developed in the WWTP as inoculum to start up the BF due to the presence of methanotrophic bacteria.","publication_date":{"day":null,"month":null,"year":2015,"errors":{}},"publication_name":"Environmental 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data-work-id="90855812"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855812/Oral_and_Poster_Papers_Submitted_for_Presentation_at_the_5th_Congress_of_the_EUGMS_Geriatric_Medicine_in_a_Time_of_Generational_Shift_September_3_6_2008_Copenhagen_Denmark"><img alt="Research paper thumbnail of Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855812/Oral_and_Poster_Papers_Submitted_for_Presentation_at_the_5th_Congress_of_the_EUGMS_Geriatric_Medicine_in_a_Time_of_Generational_Shift_September_3_6_2008_Copenhagen_Denmark">Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark</a></div><div class="wp-workCard_item"><span>The Journal of Nutrition Health and Aging</span><span>, 2008</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Recent demographic evolution has changed the trends of the two fundamental variables - natality a...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Recent demographic evolution has changed the trends of the two fundamental variables - natality and mortality - with a new slope noted. It was thus made possible for a new age structure pattern, very different from the previous one, to appear. According to the 1956 census, the ...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855812"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855812"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855812; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855812]").text(description); $(".js-view-count[data-work-id=90855812]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855812; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855812']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855812, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855812]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855812,"title":"Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark","translated_title":"","metadata":{"abstract":"Recent demographic evolution has changed the trends of the two fundamental variables - natality and mortality - with a new slope noted. 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Among activities included in a long-term in...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Fascioliasis is widespread in livestock in Argentina. Among activities included in a long-term initiative to ascertain which are the fascioliasis areas of most concern, studies were performed in a recreational farm, including liver fluke infection in different domestic animal species, classification of the lymnaeid vector and verification of natural transmission of fascioliasis by identification of the intramolluscan trematode larval stages found in naturally infected snails. The high prevalences in the domestic animals appeared related to only one lymnaeid species present. Lymnaeid and trematode classification was verified by means of nuclear ribosomal DNA and mitochondrial DNA marker sequencing. Complete sequences of 18S rRNA gene and rDNA ITS-2 and ITS-1, and a fragment of the mtDNA cox1 gene demonstrate that the Argentinian lymnaeid belongs to the species Lymnaea neotropica. Redial larval stages found in a L. neotropica specimen were ascribed to Fasciola hepatica after analysis of the complete ITS-1 sequence. The finding of L. neotropica is the first of this lymnaeid species not only in Argentina but also in Southern Cone countries. The total absence of nucleotide differences between the sequences of specimens from Argentina and the specimens from the Peruvian type locality at the levels of rDNA 18S, ITS-2 and ITS-1, and the only one mutation at the mtDNA cox1 gene suggest a very recent spread. The ecological characteristics of this lymnaeid, living in small, superficial water collections frequented by livestock, suggest that it may be carried from one place to another by remaining in dried mud stuck to the feet of transported animals. The presence of L. neotropica adds pronounced complexity to the transmission and epidemiology of fascioliasis in Argentina, due to the great difficulties in distinguishing, by traditional malacological methods, between the three similar lymnaeid species of the controversial Galba/Fossaria group present in this country: L. viatrix, Galba truncatula and L. neotropica. It also poses a problem with regard to the use, for lymnaeid vector species discrimination, of several molecular techniques which do not show sufficient accuracy, as those relying on the 18S rRNA gene or parts of it, because both L. neotropica and L. viatrix present identical 18S sequence.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855811"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855811"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855811; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855811]").text(description); $(".js-view-count[data-work-id=90855811]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855811; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855811']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855811, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855811]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855811,"title":"Fascioliasis transmission by Lymnaea neotropica confirmed by nuclear rDNA and mtDNA sequencing in Argentina","translated_title":"","metadata":{"abstract":"Fascioliasis is widespread in livestock in Argentina. 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The finding of L. neotropica is the first of this lymnaeid species not only in Argentina but also in Southern Cone countries. The total absence of nucleotide differences between the sequences of specimens from Argentina and the specimens from the Peruvian type locality at the levels of rDNA 18S, ITS-2 and ITS-1, and the only one mutation at the mtDNA cox1 gene suggest a very recent spread. The ecological characteristics of this lymnaeid, living in small, superficial water collections frequented by livestock, suggest that it may be carried from one place to another by remaining in dried mud stuck to the feet of transported animals. The presence of L. neotropica adds pronounced complexity to the transmission and epidemiology of fascioliasis in Argentina, due to the great difficulties in distinguishing, by traditional malacological methods, between the three similar lymnaeid species of the controversial Galba/Fossaria group present in this country: L. viatrix, Galba truncatula and L. neotropica. It also poses a problem with regard to the use, for lymnaeid vector species discrimination, of several molecular techniques which do not show sufficient accuracy, as those relying on the 18S rRNA gene or parts of it, because both L. neotropica and L. viatrix present identical 18S sequence.","publisher":"Elsevier BV","publication_date":{"day":null,"month":null,"year":2009,"errors":{}},"publication_name":"Veterinary Parasitology"},"translated_abstract":"Fascioliasis is widespread in livestock in Argentina. Among activities included in a long-term initiative to ascertain which are the fascioliasis areas of most concern, studies were performed in a recreational farm, including liver fluke infection in different domestic animal species, classification of the lymnaeid vector and verification of natural transmission of fascioliasis by identification of the intramolluscan trematode larval stages found in naturally infected snails. The high prevalences in the domestic animals appeared related to only one lymnaeid species present. Lymnaeid and trematode classification was verified by means of nuclear ribosomal DNA and mitochondrial DNA marker sequencing. Complete sequences of 18S rRNA gene and rDNA ITS-2 and ITS-1, and a fragment of the mtDNA cox1 gene demonstrate that the Argentinian lymnaeid belongs to the species Lymnaea neotropica. Redial larval stages found in a L. neotropica specimen were ascribed to Fasciola hepatica after analysis of the complete ITS-1 sequence. The finding of L. neotropica is the first of this lymnaeid species not only in Argentina but also in Southern Cone countries. The total absence of nucleotide differences between the sequences of specimens from Argentina and the specimens from the Peruvian type locality at the levels of rDNA 18S, ITS-2 and ITS-1, and the only one mutation at the mtDNA cox1 gene suggest a very recent spread. The ecological characteristics of this lymnaeid, living in small, superficial water collections frequented by livestock, suggest that it may be carried from one place to another by remaining in dried mud stuck to the feet of transported animals. The presence of L. neotropica adds pronounced complexity to the transmission and epidemiology of fascioliasis in Argentina, due to the great difficulties in distinguishing, by traditional malacological methods, between the three similar lymnaeid species of the controversial Galba/Fossaria group present in this country: L. viatrix, Galba truncatula and L. neotropica. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855805"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855805/Biotransformation_of_aromatic_compounds_from_wastewaters_containing_N_and_or_S_by_nitrification_denitrification_a_review"><img alt="Research paper thumbnail of Biotransformation of aromatic compounds from wastewaters containing N and/or S, by nitrification/denitrification: a review" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855805/Biotransformation_of_aromatic_compounds_from_wastewaters_containing_N_and_or_S_by_nitrification_denitrification_a_review">Biotransformation of aromatic compounds from wastewaters containing N and/or S, by nitrification/denitrification: a review</a></div><div class="wp-workCard_item"><span>Reviews in Environmental Science and Bio/Technology</span><span>, 2009</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">This review presents progress made over the last decades in the understanding of the metabolic ca...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">This review presents progress made over the last decades in the understanding of the metabolic capabilities of nitrifying and denitrifying microorganisms for the biotransformation of nitrogen, sulfur, and carbon compounds present in wastewaters. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855803"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855803/Human_fascioliasis_in_Argentina_retrospective_overview_critical_analysis_and_baseline_for_future_research"><img alt="Research paper thumbnail of Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research" class="work-thumbnail" src="https://attachments.academia-assets.com/94302562/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855803/Human_fascioliasis_in_Argentina_retrospective_overview_critical_analysis_and_baseline_for_future_research">Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research</a></div><div class="wp-workCard_item"><span>Parasites &amp;amp; Vectors</span><span>, 2011</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">In Argentina, human fascioliasis has never been adequately analysed, although having a physiograp...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">In Argentina, human fascioliasis has never been adequately analysed, although having a physiography, climate, animal prevalences and lymnaeids similar to those of countries where the disease is endemic such as Bolivia, Peru and Chile. We performed a literature search identifying 58 reports accounting for 619 cases, involving 13 provinces, their majority (97.7%) from high altitudes, in central mountainous areas and Andean valleys, concentrated in Cordoba (430 cases), Catamarca (73), San Luis (29) and Mendoza (28), the remaining provinces being rarely affected. This distribution does not fit that of animal fascioliasis. Certain aspects (higher prevalence in females in a local survey, although a trend non-significant throughout Argentina) but not others (patient&amp;#39;s age 3-95 years, mean 37.1 years) resemble human endemics in Andean countries, although the lack of intensity studies and surveys in rural areas does not allow for an adequate evaluation. Human infection occurs mainly in J...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="fa154a12300428800865fcb788ba8da2" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302562,&quot;asset_id&quot;:90855803,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302562/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855803"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855803"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855803; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855803]").text(description); $(".js-view-count[data-work-id=90855803]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855803; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855803']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855803, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "fa154a12300428800865fcb788ba8da2" } } $('.js-work-strip[data-work-id=90855803]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855803,"title":"Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research","translated_title":"","metadata":{"abstract":"In Argentina, human fascioliasis has never been adequately analysed, although having a physiography, climate, animal prevalences and lymnaeids similar to those of countries where the disease is endemic such as Bolivia, Peru and Chile. 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By comparing the performance of the proposed system to a system without the auxiliary objective, we conclude that the maximization of mutual information among agents promotes the emergence of cooperation in social 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<div class="js-work-strip profile--work_container" data-work-id="90855837"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855837/Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech"><img alt="Research paper thumbnail of Variable-rate hierarchical CPC leads to acoustic unit discovery in speech" class="work-thumbnail" src="https://attachments.academia-assets.com/94302582/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855837/Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech">Variable-rate hierarchical CPC leads to acoustic unit discovery in speech</a></div><div class="wp-workCard_item wp-workCard--actions"><span 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{"id":90855837,"title":"Variable-rate hierarchical CPC leads to acoustic unit discovery in speech","translated_title":"","metadata":{"grobid_abstract":"The success of deep learning comes from its ability to capture the hierarchical structure of data by learning high-level representations defined in terms of low-level ones. In this paper we explore self-supervised learning of hierarchical representations of speech by applying multiple levels of Contrastive Predictive Coding (CPC). We observe that simply stacking two CPC models does not yield significant improvements over single-level architectures. Inspired by the fact that speech is often described as a sequence of discrete units unevenly distributed in time, we propose a model in which the output of a low-level CPC module is non-uniformly downsampled to directly minimize the loss of a high-level CPC module. The latter is designed to also enforce a prior of separability and discreteness in its representations by enforcing dissimilarity of successive high-level representations through focused negative sampling, and by quantization of the prediction targets. Accounting for the structure of the speech signal improves upon single-level CPC features and enhances the disentanglement of the learned representations, as measured by downstream speech recognition tasks, while resulting in a meaningful segmentation of the signal that closely resembles phone boundaries. Preprint. Under review.","publication_date":{"day":5,"month":6,"year":2022,"errors":{}},"grobid_abstract_attachment_id":94302582},"translated_abstract":null,"internal_url":"https://www.academia.edu/90855837/Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech","translated_internal_url":"","created_at":"2022-11-15T11:55:47.916-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":94302582,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302582/thumbnails/1.jpg","file_name":"2206.02211.pdf","download_url":"https://www.academia.edu/attachments/94302582/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Variable_rate_hierarchical_CPC_leads_to.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302582/2206.02211-libre.pdf?1668542716=\u0026response-content-disposition=attachment%3B+filename%3DVariable_rate_hierarchical_CPC_leads_to.pdf\u0026Expires=1732746820\u0026Signature=CclNEiqjqDnYkHerj8uq-~czJ1Wiw3xnJlHeVPSSrjhzC5IMa9CZEf~KWe2eLZN1cVbn96qFPy4-4SLdWhtOy8~ab1jDf8XXsCKhrs7Ck2~z7wsLaL2G4-8l3XKREZJvgTQ4w9qO9G6TBraFGXhdLbil0M22Jbvho1OkRkM3u8XA1E~rjVBNMxcHOCsjPSlyjvLHIdFuT5Ep-8vm4ccN3~bpD8uCYKyO1MyBUYinyNhK6y~v4qR3sWKV1HHLKHahpn72ATLLbB0TE4C3KFnkCkKCw6PCfERMBZ18cqQgWBgdaNcfMaQsq8iD42sx7nu9O50Be-YeAv~j74j4wRmZiw__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Variable_rate_hierarchical_CPC_leads_to_acoustic_unit_discovery_in_speech","translated_slug":"","page_count":11,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[{"id":94302582,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302582/thumbnails/1.jpg","file_name":"2206.02211.pdf","download_url":"https://www.academia.edu/attachments/94302582/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Variable_rate_hierarchical_CPC_leads_to.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302582/2206.02211-libre.pdf?1668542716=\u0026response-content-disposition=attachment%3B+filename%3DVariable_rate_hierarchical_CPC_leads_to.pdf\u0026Expires=1732746820\u0026Signature=CclNEiqjqDnYkHerj8uq-~czJ1Wiw3xnJlHeVPSSrjhzC5IMa9CZEf~KWe2eLZN1cVbn96qFPy4-4SLdWhtOy8~ab1jDf8XXsCKhrs7Ck2~z7wsLaL2G4-8l3XKREZJvgTQ4w9qO9G6TBraFGXhdLbil0M22Jbvho1OkRkM3u8XA1E~rjVBNMxcHOCsjPSlyjvLHIdFuT5Ep-8vm4ccN3~bpD8uCYKyO1MyBUYinyNhK6y~v4qR3sWKV1HHLKHahpn72ATLLbB0TE4C3KFnkCkKCw6PCfERMBZ18cqQgWBgdaNcfMaQsq8iD42sx7nu9O50Be-YeAv~j74j4wRmZiw__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":422,"name":"Computer Science","url":"https://www.academia.edu/Documents/in/Computer_Science"},{"id":93217,"name":"Segmentation","url":"https://www.academia.edu/Documents/in/Segmentation"}],"urls":[{"id":26007900,"url":"http://arxiv.org/abs/2206.02211"}]}, dispatcherData: dispatcherData }); 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class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">La industria Huilense y su desarrollo, comparten bienestar provisto por los procesos academicos, a estos les competente la insercion y el manejo de la automatizacion en procesos manufactureros, con el proposito de obtener eficacia, eficiencia y efectividad, para el proceso industrial de clasificar los productos por color se encuentra la posibilidad de obtener un proceso optimizado, la estacion didactica de seleccion de objetos por color es una herramienta basada en el control automatizado de procesos, es un sistema electronico embebido, que realiza las actividades de transporte, sensado, paletizado y almacenaje de objetos, clasifica objetos en cuatro (4) colores del espectro de luz visible, en el sensado RGB del color, el color a sensar es parametrizable en cualquier color requerido, dando la posibilidad a la estacion de clasificar variados objetos, la estacion didactica cuenta con interfaz 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Nature based solutions for winery wastewater valorisation" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855823/Nature_based_solutions_for_winery_wastewater_valorisation">Nature based solutions for winery wastewater valorisation</a></div><div class="wp-workCard_item"><span>Ecological Engineering</span><span>, 2021</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation o...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). The WETWINE plant is located in Tomino (Pontevedra, Spain) and is being validated at the demo-scale at Santiago Ruiz Winery (NW Spain). The plant consisted of a HUSB reactor for removing suspended solids and hydrolyse organic matter, followed by two vertical subsurface flow constructed wetland (VF) operating in parallel and to provide further treatment, a horizontal subsurface flow constructed wetland (HF) operating in series. After two years of continuous monitoring and regardless in the variation of flow and load, the hybrid system achieved average removal efficiencies of over 93% for total suspended solids and chemical oxygen demand, receiving an overall surface loading of up to 115 g COD/m2·d. Total nitrogen removal reached 62% with an average concertation of 21 mg N/ L. The WETWINE plant was also able to increased the pH in the effluent from 5.5 at the influent to 7.2.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855823"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855823"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855823; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855823]").text(description); $(".js-view-count[data-work-id=90855823]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855823; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855823']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855823, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855823]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855823,"title":"Nature based solutions for winery wastewater valorisation","translated_title":"","metadata":{"abstract":"Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). The WETWINE plant is located in Tomino (Pontevedra, Spain) and is being validated at the demo-scale at Santiago Ruiz Winery (NW Spain). The plant consisted of a HUSB reactor for removing suspended solids and hydrolyse organic matter, followed by two vertical subsurface flow constructed wetland (VF) operating in parallel and to provide further treatment, a horizontal subsurface flow constructed wetland (HF) operating in series. After two years of continuous monitoring and regardless in the variation of flow and load, the hybrid system achieved average removal efficiencies of over 93% for total suspended solids and chemical oxygen demand, receiving an overall surface loading of up to 115 g COD/m2·d. Total nitrogen removal reached 62% with an average concertation of 21 mg N/ L. The WETWINE plant was also able to increased the pH in the effluent from 5.5 at the influent to 7.2.","publisher":"Elsevier BV","publication_date":{"day":null,"month":null,"year":2021,"errors":{}},"publication_name":"Ecological Engineering"},"translated_abstract":"Abstract To valorise winery treated wastewater and to produce suitable water for the irrigation of vineyards, or other factory operations, the WETWINE project set up a combination of a hydrolytic up-flow sludge blanket (HUSB) reactor and constructed wetlands (CW). The WETWINE plant is located in Tomino (Pontevedra, Spain) and is being validated at the demo-scale at Santiago Ruiz Winery (NW Spain). The plant consisted of a HUSB reactor for removing suspended solids and hydrolyse organic matter, followed by two vertical subsurface flow constructed wetland (VF) operating in parallel and to provide further treatment, a horizontal subsurface flow constructed wetland (HF) operating in series. After two years of continuous monitoring and regardless in the variation of flow and load, the hybrid system achieved average removal efficiencies of over 93% for total suspended solids and chemical oxygen demand, receiving an overall surface loading of up to 115 g COD/m2·d. Total nitrogen removal reached 62% with an average concertation of 21 mg N/ L. The WETWINE plant was also able to increased the pH in the effluent from 5.5 at the influent to 7.2.","internal_url":"https://www.academia.edu/90855823/Nature_based_solutions_for_winery_wastewater_valorisation","translated_internal_url":"","created_at":"2022-11-15T11:55:30.620-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Nature_based_solutions_for_winery_wastewater_valorisation","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[],"research_interests":[{"id":48,"name":"Engineering","url":"https://www.academia.edu/Documents/in/Engineering"},{"id":79,"name":"Ecological Engineering","url":"https://www.academia.edu/Documents/in/Ecological_Engineering"},{"id":400,"name":"Earth Sciences","url":"https://www.academia.edu/Documents/in/Earth_Sciences"},{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":58054,"name":"Environmental Sciences","url":"https://www.academia.edu/Documents/in/Environmental_Sciences"},{"id":352779,"name":"Winery","url":"https://www.academia.edu/Documents/in/Winery"},{"id":951369,"name":"Valorisation","url":"https://www.academia.edu/Documents/in/Valorisation"}],"urls":[{"id":26007892,"url":"https://api.elsevier.com/content/article/PII:S092585742100166X?httpAccept=text/xml"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855819"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855819/Biomass_accumulation_and_physiological_responses_of_tomato_plants_to_magnetically_treated_water_in_hydroponic_conditions"><img alt="Research paper thumbnail of Biomass accumulation and physiological responses of tomato plants to magnetically–treated water in hydroponic conditions" class="work-thumbnail" src="https://attachments.academia-assets.com/94302613/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855819/Biomass_accumulation_and_physiological_responses_of_tomato_plants_to_magnetically_treated_water_in_hydroponic_conditions">Biomass accumulation and physiological responses of tomato plants to magnetically–treated water in hydroponic conditions</a></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. How...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. However, the underlying mechanisms are not fully understood, and the existing reports only deal with soil-grown plants. Thus, the purpose of this experiment was to assess whether or not MTW affects main physiological processes (gas exchange, biomass accumulation and water potential) in tomato plants whose water supply was only MTW. Two experiments were done in hydroponic semi-controlled conditions, consisting of a loop system with permanent recirculation of water through a non-uniform magnet. The plants grown under MTW showed a significant increase in chlorophyll content, photosynthesis and transpiration at high light irradiances, although the increase in stomatal conductance was less significant. MTW also increased fruit fresh biomass, number of fruits and root dry biomass in 61.7 %, 85.3 % and 30.3 % respectively, but this was only achieved at natural sunlight conditions. Moreover, treate...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="f4ba848f57a818e4c567d5c7e994d537" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302613,&quot;asset_id&quot;:90855819,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302613/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855819"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855819"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855819; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855819]").text(description); $(".js-view-count[data-work-id=90855819]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855819; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855819']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855819, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "f4ba848f57a818e4c567d5c7e994d537" } } $('.js-work-strip[data-work-id=90855819]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855819,"title":"Biomass accumulation and physiological responses of tomato plants to magnetically–treated water in hydroponic conditions","translated_title":"","metadata":{"abstract":"Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. However, the underlying mechanisms are not fully understood, and the existing reports only deal with soil-grown plants. Thus, the purpose of this experiment was to assess whether or not MTW affects main physiological processes (gas exchange, biomass accumulation and water potential) in tomato plants whose water supply was only MTW. Two experiments were done in hydroponic semi-controlled conditions, consisting of a loop system with permanent recirculation of water through a non-uniform magnet. The plants grown under MTW showed a significant increase in chlorophyll content, photosynthesis and transpiration at high light irradiances, although the increase in stomatal conductance was less significant. MTW also increased fruit fresh biomass, number of fruits and root dry biomass in 61.7 %, 85.3 % and 30.3 % respectively, but this was only achieved at natural sunlight conditions. Moreover, treate...","publisher":"Cold Spring Harbor Laboratory","publication_date":{"day":null,"month":null,"year":2021,"errors":{}}},"translated_abstract":"Magnetically-treated water (MTW) has been reported to enhance biomass accumulation in plants. However, the underlying mechanisms are not fully understood, and the existing reports only deal with soil-grown plants. Thus, the purpose of this experiment was to assess whether or not MTW affects main physiological processes (gas exchange, biomass accumulation and water potential) in tomato plants whose water supply was only MTW. Two experiments were done in hydroponic semi-controlled conditions, consisting of a loop system with permanent recirculation of water through a non-uniform magnet. The plants grown under MTW showed a significant increase in chlorophyll content, photosynthesis and transpiration at high light irradiances, although the increase in stomatal conductance was less significant. MTW also increased fruit fresh biomass, number of fruits and root dry biomass in 61.7 %, 85.3 % and 30.3 % respectively, but this was only achieved at natural sunlight conditions. Moreover, treate...","internal_url":"https://www.academia.edu/90855819/Biomass_accumulation_and_physiological_responses_of_tomato_plants_to_magnetically_treated_water_in_hydroponic_conditions","translated_internal_url":"","created_at":"2022-11-15T11:55:26.683-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":94302613,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302613/thumbnails/1.jpg","file_name":"2021.09.21.461287.full.pdf","download_url":"https://www.academia.edu/attachments/94302613/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Biomass_accumulation_and_physiological_r.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302613/2021.09.21.461287.full-libre.pdf?1668542722=\u0026response-content-disposition=attachment%3B+filename%3DBiomass_accumulation_and_physiological_r.pdf\u0026Expires=1732746820\u0026Signature=OL7spgl-1eJKz~wrYQODb3aanRMDDNap1K~Mcyub2a1KbBY6kN9JV~SLZJv0qQrmPxVQlT746tT~amrowbCTQEOrW4O7i0FHSka4rl7jlTu9QUrkcN9REZXwQtfZOZDPcN864ZCtanbKWmaqho8qJM5kzrvdnlou4jrIJJXxVji9V~Cq0wgRyiCI35Kntl0ViEovrkCB7pGfMC66ncpjwAFIhkl-bhScEHVJBBJhJ3-NTKD5TboroKFNAWj7ezTrNXf~08NPW7-sgTlHDrez5lHK8RW-TElNTadtkiySTgvWq1sCK-jLT0UjaOc-nPnOYj4mXtB5XekBRsCViejlQg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Biomass_accumulation_and_physiological_responses_of_tomato_plants_to_magnetically_treated_water_in_hydroponic_conditions","translated_slug":"","page_count":19,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[{"id":94302613,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302613/thumbnails/1.jpg","file_name":"2021.09.21.461287.full.pdf","download_url":"https://www.academia.edu/attachments/94302613/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Biomass_accumulation_and_physiological_r.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302613/2021.09.21.461287.full-libre.pdf?1668542722=\u0026response-content-disposition=attachment%3B+filename%3DBiomass_accumulation_and_physiological_r.pdf\u0026Expires=1732746820\u0026Signature=OL7spgl-1eJKz~wrYQODb3aanRMDDNap1K~Mcyub2a1KbBY6kN9JV~SLZJv0qQrmPxVQlT746tT~amrowbCTQEOrW4O7i0FHSka4rl7jlTu9QUrkcN9REZXwQtfZOZDPcN864ZCtanbKWmaqho8qJM5kzrvdnlou4jrIJJXxVji9V~Cq0wgRyiCI35Kntl0ViEovrkCB7pGfMC66ncpjwAFIhkl-bhScEHVJBBJhJ3-NTKD5TboroKFNAWj7ezTrNXf~08NPW7-sgTlHDrez5lHK8RW-TElNTadtkiySTgvWq1sCK-jLT0UjaOc-nPnOYj4mXtB5XekBRsCViejlQg__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":5345,"name":"Photosynthesis","url":"https://www.academia.edu/Documents/in/Photosynthesis"},{"id":7710,"name":"Biology","url":"https://www.academia.edu/Documents/in/Biology"},{"id":126935,"name":"Xylem","url":"https://www.academia.edu/Documents/in/Xylem"},{"id":212488,"name":"Transpiration","url":"https://www.academia.edu/Documents/in/Transpiration"},{"id":2021433,"name":"Stomatal Conductance","url":"https://www.academia.edu/Documents/in/Stomatal_Conductance"}],"urls":[{"id":26007889,"url":"https://syndication.highwire.org/content/doi/10.1101/2021.09.21.461287"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855818"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators"><img alt="Research paper thumbnail of Diffuse methane emissions abatement by organic and inorganic packed biofilters: Assessment of operational and environmental indicators" class="work-thumbnail" src="https://attachments.academia-assets.com/94302608/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators">Diffuse methane emissions abatement by organic and inorganic packed biofilters: Assessment of operational and environmental indicators</a></div><div class="wp-workCard_item"><span>Journal of Cleaner Production</span><span>, 2017</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="74878a39745b9560f01561393dc59769" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302608,&quot;asset_id&quot;:90855818,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855818"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855818"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855818; 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The use of different packing materials including a mixture of pine bark, perlite and compost for the organic biofilter and polyurethane foam for the inorganic one was evaluated. The influence of other major variables on the removal efficiency such as nutrient requirements, operational conditions and long-term stability were also assessed in both configurations. The analysis of the biofilters operation proved that both configurations provided a feasible and stable performance in the treatment of diffuse methane emissions. Once the operational feasibility of both systems was proved, the environmental assessment was performed. The main hotspots found in the analysis were attributed to the requirement of nutrients, infrastructure, waste disposal and direct emissions to the atmosphere. A sensitivity analysis was performed in terms of nutrient supply and infrastructure material which revealed that special attention needs to be paid to the formulation of the nutrient solution in terms of concentration and source of nitrogen.","publication_date":{"day":null,"month":null,"year":2017,"errors":{}},"publication_name":"Journal of Cleaner Production","grobid_abstract_attachment_id":94302608},"translated_abstract":null,"internal_url":"https://www.academia.edu/90855818/Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators","translated_internal_url":"","created_at":"2022-11-15T11:55:22.761-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[{"id":94302608,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302608/thumbnails/1.jpg","file_name":"j.jclepro.2016.11.18520221115-1-1e0g4d0.pdf","download_url":"https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Diffuse_methane_emissions_abatement_by_o.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302608/j.jclepro.2016.11.18520221115-1-1e0g4d0-libre.pdf?1668542723=\u0026response-content-disposition=attachment%3B+filename%3DDiffuse_methane_emissions_abatement_by_o.pdf\u0026Expires=1732746820\u0026Signature=Lul6HHcKimiIMK90obSob2WoxXuv4iiJdr4rt9ifXcc~NaAlStUzk2TYW6iKxRIT1nqLhdtUlqnYgBwel~TIFAV1L0K-O0o1mHWmTD5R8ARTEF6bFNLVttair6V0cHiSqnxN4R08f30RdBGT0rOsAQw6~~gVcD4a3LLRMZdxc0d6ekFXazmuXvYY158ruzKDYI3kb7V9e5SvpvlMPtbGeuB6Vcx2GYXWUTLUN3xR36QZNJDbe0lzJbkvyHp9MOa-by0NYHNSgLDumipBEX2JcyBMqU8VzNeElpQsWwGpjPq1SNO43lGmiRq9HksRim-0jo~-JySMTNQHV4hQ0YYmiQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"slug":"Diffuse_methane_emissions_abatement_by_organic_and_inorganic_packed_biofilters_Assessment_of_operational_and_environmental_indicators","translated_slug":"","page_count":12,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[{"id":94302608,"title":"","file_type":"pdf","scribd_thumbnail_url":"https://attachments.academia-assets.com/94302608/thumbnails/1.jpg","file_name":"j.jclepro.2016.11.18520221115-1-1e0g4d0.pdf","download_url":"https://www.academia.edu/attachments/94302608/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMCw4LjIyMi4yMDguMTQ2&","bulk_download_file_name":"Diffuse_methane_emissions_abatement_by_o.pdf","bulk_download_url":"https://d1wqtxts1xzle7.cloudfront.net/94302608/j.jclepro.2016.11.18520221115-1-1e0g4d0-libre.pdf?1668542723=\u0026response-content-disposition=attachment%3B+filename%3DDiffuse_methane_emissions_abatement_by_o.pdf\u0026Expires=1732746820\u0026Signature=Lul6HHcKimiIMK90obSob2WoxXuv4iiJdr4rt9ifXcc~NaAlStUzk2TYW6iKxRIT1nqLhdtUlqnYgBwel~TIFAV1L0K-O0o1mHWmTD5R8ARTEF6bFNLVttair6V0cHiSqnxN4R08f30RdBGT0rOsAQw6~~gVcD4a3LLRMZdxc0d6ekFXazmuXvYY158ruzKDYI3kb7V9e5SvpvlMPtbGeuB6Vcx2GYXWUTLUN3xR36QZNJDbe0lzJbkvyHp9MOa-by0NYHNSgLDumipBEX2JcyBMqU8VzNeElpQsWwGpjPq1SNO43lGmiRq9HksRim-0jo~-JySMTNQHV4hQ0YYmiQ__\u0026Key-Pair-Id=APKAJLOHF5GGSLRBV4ZA"}],"research_interests":[{"id":55,"name":"Environmental Engineering","url":"https://www.academia.edu/Documents/in/Environmental_Engineering"},{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":1584,"name":"Cleaner Production","url":"https://www.academia.edu/Documents/in/Cleaner_Production"},{"id":14085,"name":"Waste Management","url":"https://www.academia.edu/Documents/in/Waste_Management"},{"id":96825,"name":"Manufacturing Engineering","url":"https://www.academia.edu/Documents/in/Manufacturing_Engineering"},{"id":337999,"name":"Perlite","url":"https://www.academia.edu/Documents/in/Perlite"},{"id":554780,"name":"Interdisciplinary Engineering","url":"https://www.academia.edu/Documents/in/Interdisciplinary_Engineering"},{"id":555091,"name":"Compost","url":"https://www.academia.edu/Documents/in/Compost"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"}],"urls":[{"id":26007888,"url":"https://api.elsevier.com/content/article/PII:S0959652616320479?httpAccept=text/plain"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855816"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation"><img alt="Research paper thumbnail of Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation">Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation</a></div><div class="wp-workCard_item"><span>Environmental Technology</span><span>, 2016</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">ABSTRACT There is growing international concern about the increasing levels of greenhouse gases i...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855816"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855816"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855816; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855816]").text(description); $(".js-view-count[data-work-id=90855816]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855816; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855816']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855816, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855816]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855816,"title":"Identifying the limitations of conventional biofiltration of diffuse methane emissions at long-term operation","translated_title":"","metadata":{"abstract":"ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.","publisher":"Informa UK Limited","publication_date":{"day":null,"month":null,"year":2016,"errors":{}},"publication_name":"Environmental Technology"},"translated_abstract":"ABSTRACT There is growing international concern about the increasing levels of greenhouse gases in the atmosphere, particularly CO2 and methane. The emissions of methane derived from human activities are associated with large flows and very low concentrations, such as those emitted from landfills and wastewater treatment plants, among others. The present work was focused on the biological methane degradation at diffuse concentrations (0.2% vv−1) in a conventional biofilter using a mixture of compost, perlite and bark chips as carrier. An extensive characterization of the process was carried out at long-term operation (250 days) in a fully monitored pilot plant, achieving stable conditions during the entire period. Operational parameters such as waterings, nitrogen addition and inlet loads and contact time influences were evaluated. Obtained results indicate that empty bed residence times within 4–8 min are crucial to maximize elimination rates. Waterings and the type of nitrogen supplied in the nutrient solution (ammonia or nitrate) have a strong impact on the biofilter performance. The better results compatible with a stable operation were achieved using nitrate, with elimination capacities up to 7.6 ± 1.1 g CH4 m−3 h−1. The operation at low inlet concentrations (IC) implied that removal rates obtained were quite limited (ranging 3–8 g CH4 m−3 h−1); however, these results could be significantly increased (up to 20.6 g CH4 m−3 h−1) at higher IC, which indicates that the mass transfer from the gas to the liquid layer surrounding the biofilm is a key limitation of the process.","internal_url":"https://www.academia.edu/90855816/Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation","translated_internal_url":"","created_at":"2022-11-15T11:55:19.087-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"Identifying_the_limitations_of_conventional_biofiltration_of_diffuse_methane_emissions_at_long_term_operation","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[],"research_interests":[{"id":48,"name":"Engineering","url":"https://www.academia.edu/Documents/in/Engineering"},{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":523,"name":"Chemistry","url":"https://www.academia.edu/Documents/in/Chemistry"},{"id":26327,"name":"Medicine","url":"https://www.academia.edu/Documents/in/Medicine"},{"id":47884,"name":"Biological Sciences","url":"https://www.academia.edu/Documents/in/Biological_Sciences"},{"id":58054,"name":"Environmental Sciences","url":"https://www.academia.edu/Documents/in/Environmental_Sciences"},{"id":88280,"name":"Environmental Technology","url":"https://www.academia.edu/Documents/in/Environmental_Technology"},{"id":122404,"name":"Nitrate","url":"https://www.academia.edu/Documents/in/Nitrate"},{"id":151091,"name":"Nitrogen","url":"https://www.academia.edu/Documents/in/Nitrogen"},{"id":156347,"name":"Methane","url":"https://www.academia.edu/Documents/in/Methane"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"},{"id":803011,"name":"Aeration","url":"https://www.academia.edu/Documents/in/Aeration"}],"urls":[{"id":26007887,"url":"http://www.tandfonline.com/doi/pdf/10.1080/09593330.2015.1135996"}]}, dispatcherData: dispatcherData }); $(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855814"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions"><img alt="Research paper thumbnail of EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions">EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions</a></div><div class="wp-workCard_item"><span>Water, Air, &amp;amp; Soil Pollution</span><span>, 2015</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was car...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855814"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855814"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855814; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855814]").text(description); $(".js-view-count[data-work-id=90855814]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855814; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855814']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855814, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855814]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855814,"title":"EPS and SMP as Stability Indicators During the Biofiltration of Diffuse Methane Emissions","translated_title":"","metadata":{"abstract":"Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.","publisher":"Springer Science and Business Media LLC","publication_date":{"day":null,"month":null,"year":2015,"errors":{}},"publication_name":"Water, Air, \u0026amp; Soil Pollution"},"translated_abstract":"Biofiltration of an air stream polluted with diffuse CH4 concentrations of 0.19 % (v v−1) was carried out. These emissions can be encountered at different industrial facilities such as wastewater treatment plants and landfills. The effect of ammonium supplied in the nutrient solution was studied in a range from 0 to 1 g N-NH4+ L−1, taking account its effect on CH4 removal efficiency (RE), CO2 production, ammonium conversion and the occurrence of exopolymeric substances. Additional batch assays were performed in order to evaluate the most suitable pH and temperature ranges for the biomass used as inoculum. A conventional biofilter was operated along 225 days achieving maximum CH4 elimination capacities of up to 11.2 g CH4 m-3 h−1, corresponding to REs of 62 %, using 0.52 g N L−1 of ammonia as nitrogen source in the nutrient solution and operating at an empty bed residence time of 4.4 min. CO2 production values confirmed that most of this elimination was biological and not absorption into the liquid phase. The occurrence of instability periods resulted in a clear increase of the soluble microbial products (SMPs) contained in the liquid phase, especially in the protein fraction, which could be used as a monitoring tool to follow the stress conditions of the biofilter. Results indicate interesting links between the performance of the biofilter and the presence of extracellular polysaccharide and protein concentration in the liquid phase, with increasing concentrations detected when the process was not stable.","internal_url":"https://www.academia.edu/90855814/EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions","translated_internal_url":"","created_at":"2022-11-15T11:55:14.372-08:00","preview_url":null,"current_user_can_edit":null,"current_user_is_owner":null,"owner_id":140931819,"coauthors_can_edit":true,"document_type":"paper","co_author_tags":[],"downloadable_attachments":[],"slug":"EPS_and_SMP_as_Stability_Indicators_During_the_Biofiltration_of_Diffuse_Methane_Emissions","translated_slug":"","page_count":null,"language":"en","content_type":"Work","owner":{"id":140931819,"first_name":"Santiago","middle_initials":null,"last_name":"Cuervo","page_name":"SantiagoCuervo19","domain_name":"independent","created_at":"2020-01-05T13:41:16.079-08:00","display_name":"Santiago Cuervo","url":"https://independent.academia.edu/SantiagoCuervo19"},"attachments":[],"research_interests":[{"id":402,"name":"Environmental Science","url":"https://www.academia.edu/Documents/in/Environmental_Science"},{"id":523,"name":"Chemistry","url":"https://www.academia.edu/Documents/in/Chemistry"},{"id":15836,"name":"Environmental Chemistry","url":"https://www.academia.edu/Documents/in/Environmental_Chemistry"},{"id":28235,"name":"Multidisciplinary","url":"https://www.academia.edu/Documents/in/Multidisciplinary"},{"id":156347,"name":"Methane","url":"https://www.academia.edu/Documents/in/Methane"},{"id":743608,"name":"Biofilter","url":"https://www.academia.edu/Documents/in/Biofilter"}],"urls":[{"id":26007886,"url":"http://link.springer.com/content/pdf/10.1007/s11270-015-2576-2.pdf"}]}, dispatcherData: dispatcherData }); 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The operation at ambient temperature implies higher methane content in the liquid anaerobic effluent, which finally causes concentrations around 0.01-2.4% in the off-gas released in the anoxic-aerobic chamber (1.25% average). Mass balances indicate that these emissions account for up to 30-35% of the total methane generated in the anaerobic reactor. A conventional biofilter (BF) operated at an empty bed residence time of 4 min was used to treat these emissions for 70 d. In spite of the fluctuations in the methane inlet concentrations derived from the operation of the wastewater treatment plant (WWTP), it was possible to operate at pseudo-steady-state conditions, achieving average removal efficiencies of 76.5% and maximum elimination capacities of 30.1 g m −3 h −1. Odour removal was quantified as 99.1%. 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data-work-id="90855812"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855812/Oral_and_Poster_Papers_Submitted_for_Presentation_at_the_5th_Congress_of_the_EUGMS_Geriatric_Medicine_in_a_Time_of_Generational_Shift_September_3_6_2008_Copenhagen_Denmark"><img alt="Research paper thumbnail of Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855812/Oral_and_Poster_Papers_Submitted_for_Presentation_at_the_5th_Congress_of_the_EUGMS_Geriatric_Medicine_in_a_Time_of_Generational_Shift_September_3_6_2008_Copenhagen_Denmark">Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark</a></div><div class="wp-workCard_item"><span>The Journal of Nutrition Health and Aging</span><span>, 2008</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">Recent demographic evolution has changed the trends of the two fundamental variables - natality a...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Recent demographic evolution has changed the trends of the two fundamental variables - natality and mortality - with a new slope noted. It was thus made possible for a new age structure pattern, very different from the previous one, to appear. According to the 1956 census, the ...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855812"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855812"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855812; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855812]").text(description); $(".js-view-count[data-work-id=90855812]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855812; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855812']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855812, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855812]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855812,"title":"Oral and Poster Papers Submitted for Presentation at the 5th Congress of the EUGMS “Geriatric Medicine in a Time of Generational Shift September 3–6, 2008 Copenhagen, Denmark","translated_title":"","metadata":{"abstract":"Recent demographic evolution has changed the trends of the two fundamental variables - natality and mortality - with a new slope noted. 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Among activities included in a long-term in...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">Fascioliasis is widespread in livestock in Argentina. Among activities included in a long-term initiative to ascertain which are the fascioliasis areas of most concern, studies were performed in a recreational farm, including liver fluke infection in different domestic animal species, classification of the lymnaeid vector and verification of natural transmission of fascioliasis by identification of the intramolluscan trematode larval stages found in naturally infected snails. The high prevalences in the domestic animals appeared related to only one lymnaeid species present. Lymnaeid and trematode classification was verified by means of nuclear ribosomal DNA and mitochondrial DNA marker sequencing. Complete sequences of 18S rRNA gene and rDNA ITS-2 and ITS-1, and a fragment of the mtDNA cox1 gene demonstrate that the Argentinian lymnaeid belongs to the species Lymnaea neotropica. Redial larval stages found in a L. neotropica specimen were ascribed to Fasciola hepatica after analysis of the complete ITS-1 sequence. The finding of L. neotropica is the first of this lymnaeid species not only in Argentina but also in Southern Cone countries. The total absence of nucleotide differences between the sequences of specimens from Argentina and the specimens from the Peruvian type locality at the levels of rDNA 18S, ITS-2 and ITS-1, and the only one mutation at the mtDNA cox1 gene suggest a very recent spread. The ecological characteristics of this lymnaeid, living in small, superficial water collections frequented by livestock, suggest that it may be carried from one place to another by remaining in dried mud stuck to the feet of transported animals. The presence of L. neotropica adds pronounced complexity to the transmission and epidemiology of fascioliasis in Argentina, due to the great difficulties in distinguishing, by traditional malacological methods, between the three similar lymnaeid species of the controversial Galba/Fossaria group present in this country: L. viatrix, Galba truncatula and L. neotropica. It also poses a problem with regard to the use, for lymnaeid vector species discrimination, of several molecular techniques which do not show sufficient accuracy, as those relying on the 18S rRNA gene or parts of it, because both L. neotropica and L. viatrix present identical 18S sequence.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855811"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855811"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855811; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855811]").text(description); $(".js-view-count[data-work-id=90855811]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855811; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855811']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855811, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855811]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855811,"title":"Fascioliasis transmission by Lymnaea neotropica confirmed by nuclear rDNA and mtDNA sequencing in Argentina","translated_title":"","metadata":{"abstract":"Fascioliasis is widespread in livestock in Argentina. 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The finding of L. neotropica is the first of this lymnaeid species not only in Argentina but also in Southern Cone countries. The total absence of nucleotide differences between the sequences of specimens from Argentina and the specimens from the Peruvian type locality at the levels of rDNA 18S, ITS-2 and ITS-1, and the only one mutation at the mtDNA cox1 gene suggest a very recent spread. The ecological characteristics of this lymnaeid, living in small, superficial water collections frequented by livestock, suggest that it may be carried from one place to another by remaining in dried mud stuck to the feet of transported animals. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855805"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855805/Biotransformation_of_aromatic_compounds_from_wastewaters_containing_N_and_or_S_by_nitrification_denitrification_a_review"><img alt="Research paper thumbnail of Biotransformation of aromatic compounds from wastewaters containing N and/or S, by nitrification/denitrification: a review" class="work-thumbnail" src="https://a.academia-assets.com/images/blank-paper.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855805/Biotransformation_of_aromatic_compounds_from_wastewaters_containing_N_and_or_S_by_nitrification_denitrification_a_review">Biotransformation of aromatic compounds from wastewaters containing N and/or S, by nitrification/denitrification: a review</a></div><div class="wp-workCard_item"><span>Reviews in Environmental Science and Bio/Technology</span><span>, 2009</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">This review presents progress made over the last decades in the understanding of the metabolic ca...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">This review presents progress made over the last decades in the understanding of the metabolic capabilities of nitrifying and denitrifying microorganisms for the biotransformation of nitrogen, sulfur, and carbon compounds present in wastewaters. There are nowadays still many discoveries to be made about the metabolism, phylogeny and ecological behavior of bacteria that play an important role in the nitrogen cycle.</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855805"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855805"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855805; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855805]").text(description); $(".js-view-count[data-work-id=90855805]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855805; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855805']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855805, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (false){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "-1" } } $('.js-work-strip[data-work-id=90855805]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855805,"title":"Biotransformation of aromatic compounds from wastewaters containing N and/or S, by nitrification/denitrification: a review","translated_title":"","metadata":{"abstract":"This review presents progress made over the last decades in the understanding of the metabolic capabilities of nitrifying and denitrifying microorganisms for the biotransformation of nitrogen, sulfur, and carbon compounds present in wastewaters. 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$(this).data('initialized', true); } }); $a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855803"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855803/Human_fascioliasis_in_Argentina_retrospective_overview_critical_analysis_and_baseline_for_future_research"><img alt="Research paper thumbnail of Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research" class="work-thumbnail" src="https://attachments.academia-assets.com/94302562/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855803/Human_fascioliasis_in_Argentina_retrospective_overview_critical_analysis_and_baseline_for_future_research">Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research</a></div><div class="wp-workCard_item"><span>Parasites &amp;amp; Vectors</span><span>, 2011</span></div><div class="wp-workCard_item"><span class="js-work-more-abstract-truncated">In Argentina, human fascioliasis has never been adequately analysed, although having a physiograp...</span><a class="js-work-more-abstract" data-broccoli-component="work_strip.more_abstract" data-click-track="profile-work-strip-more-abstract" href="javascript:;"><span> more </span><span><i class="fa fa-caret-down"></i></span></a><span class="js-work-more-abstract-untruncated hidden">In Argentina, human fascioliasis has never been adequately analysed, although having a physiography, climate, animal prevalences and lymnaeids similar to those of countries where the disease is endemic such as Bolivia, Peru and Chile. We performed a literature search identifying 58 reports accounting for 619 cases, involving 13 provinces, their majority (97.7%) from high altitudes, in central mountainous areas and Andean valleys, concentrated in Cordoba (430 cases), Catamarca (73), San Luis (29) and Mendoza (28), the remaining provinces being rarely affected. This distribution does not fit that of animal fascioliasis. Certain aspects (higher prevalence in females in a local survey, although a trend non-significant throughout Argentina) but not others (patient&amp;#39;s age 3-95 years, mean 37.1 years) resemble human endemics in Andean countries, although the lack of intensity studies and surveys in rural areas does not allow for an adequate evaluation. Human infection occurs mainly in J...</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="fa154a12300428800865fcb788ba8da2" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302562,&quot;asset_id&quot;:90855803,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" href="https://www.academia.edu/attachments/94302562/download_file?st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&st=MTczMjc0MzIyMSw4LjIyMi4yMDguMTQ2&s=profile"><span><i class="fa fa-arrow-down"></i></span><span>Download</span></a><span class="wp-workCard--action visible-if-viewed-by-owner inline-block" style="display: none;"><span class="js-profile-work-strip-edit-button-wrapper profile-work-strip-edit-button-wrapper" data-work-id="90855803"><a class="js-profile-work-strip-edit-button" tabindex="0"><span><i class="fa fa-pencil"></i></span><span>Edit</span></a></span></span><span id="work-strip-rankings-button-container"></span></div><div class="wp-workCard_item wp-workCard--stats"><span><span><span class="js-view-count view-count u-mr2x" data-work-id="90855803"><i class="fa fa-spinner fa-spin"></i></span><script>$(function () { var workId = 90855803; window.Academia.workViewCountsFetcher.queue(workId, function (count) { var description = window.$h.commaizeInt(count) + " " + window.$h.pluralize(count, 'View'); $(".js-view-count[data-work-id=90855803]").text(description); $(".js-view-count[data-work-id=90855803]").attr('title', description).tooltip(); }); });</script></span></span><span><span class="percentile-widget hidden"><span class="u-mr2x work-percentile"></span></span><script>$(function () { var workId = 90855803; window.Academia.workPercentilesFetcher.queue(workId, function (percentileText) { var container = $(".js-work-strip[data-work-id='90855803']"); container.find('.work-percentile').text(percentileText.charAt(0).toUpperCase() + percentileText.slice(1)); container.find('.percentile-widget').show(); container.find('.percentile-widget').removeClass('hidden'); }); });</script></span><span><script>$(function() { new Works.PaperRankView({ workId: 90855803, container: "", }); });</script></span></div><div id="work-strip-premium-row-container"></div></div></div><script> require.config({ waitSeconds: 90 })(["https://a.academia-assets.com/assets/wow_profile-f77ea15d77ce96025a6048a514272ad8becbad23c641fc2b3bd6e24ca6ff1932.js","https://a.academia-assets.com/assets/work_edit-ad038b8c047c1a8d4fa01b402d530ff93c45fee2137a149a4a5398bc8ad67560.js"], function() { // from javascript_helper.rb var dispatcherData = {} if (true){ window.WowProfile.dispatcher = window.WowProfile.dispatcher || _.clone(Backbone.Events); dispatcherData = { dispatcher: window.WowProfile.dispatcher, downloadLinkId: "fa154a12300428800865fcb788ba8da2" } } $('.js-work-strip[data-work-id=90855803]').each(function() { if (!$(this).data('initialized')) { new WowProfile.WorkStripView({ el: this, workJSON: {"id":90855803,"title":"Human fascioliasis in Argentina: retrospective overview, critical analysis and baseline for future research","translated_title":"","metadata":{"abstract":"In Argentina, human fascioliasis has never been adequately analysed, although having a physiography, climate, animal prevalences and lymnaeids similar to those of countries where the disease is endemic such as Bolivia, Peru and Chile. 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$a.trackClickSource(".js-work-strip-work-link", "profile_work_strip") }); </script> <div class="js-work-strip profile--work_container" data-work-id="90855800"><div class="profile--work_thumbnail hidden-xs"><a class="js-work-strip-work-link" data-click-track="profile-work-strip-thumbnail" href="https://www.academia.edu/90855800/Rhodium_I_and_Rhodium_III_Complexes_Containing_the_Chiral_Ligand_2_6_Bis_4_S_isopropyloxazolin_2_yl_pyridine_Pybox_An_Unprecedented_Monohapto_Coordination_of_Pybox"><img alt="Research paper thumbnail of Rhodium(I) and Rhodium(III) Complexes Containing the Chiral Ligand 2,6-Bis[4‘( S )-isopropyloxazolin-2‘-yl]pyridine (Pybox):  An Unprecedented Monohapto Coordination of Pybox" class="work-thumbnail" src="https://attachments.academia-assets.com/94302595/thumbnails/1.jpg" /></a></div><div class="wp-workCard wp-workCard_itemContainer"><div class="wp-workCard_item wp-workCard--title"><a class="js-work-strip-work-link text-gray-darker" data-click-track="profile-work-strip-title" href="https://www.academia.edu/90855800/Rhodium_I_and_Rhodium_III_Complexes_Containing_the_Chiral_Ligand_2_6_Bis_4_S_isopropyloxazolin_2_yl_pyridine_Pybox_An_Unprecedented_Monohapto_Coordination_of_Pybox">Rhodium(I) and Rhodium(III) Complexes Containing the Chiral Ligand 2,6-Bis[4‘( S )-isopropyloxazolin-2‘-yl]pyridine (Pybox):  An Unprecedented Monohapto Coordination of Pybox</a></div><div class="wp-workCard_item"><span>Inorganic Chemistry</span><span>, 2002</span></div><div class="wp-workCard_item wp-workCard--actions"><span class="work-strip-bookmark-button-container"></span><a id="b8a48310399098bef2db2a4156270ea1" class="wp-workCard--action" rel="nofollow" data-click-track="profile-work-strip-download" data-download="{&quot;attachment_id&quot;:94302595,&quot;asset_id&quot;:90855800,&quot;asset_type&quot;:&quot;Work&quot;,&quot;button_location&quot;:&quot;profile&quot;}" 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