{"id":1606,"date":"2026-02-27T17:10:33","date_gmt":"2026-02-27T17:10:33","guid":{"rendered":"https:\/\/gaeatech.com\/wordpress\/?p=1606"},"modified":"2026-03-26T04:31:33","modified_gmt":"2026-03-26T04:31:33","slug":"how-to-use-passive-sinks-pollutev8","status":"publish","type":"post","link":"https:\/\/gaeatech.com\/knowledge-center\/how-to-use-passive-sinks-pollutev8\/","title":{"rendered":"How Can I Use Passive Sinks in POLLUTEv8?"},"content":{"rendered":"\n<p>When modeling complex contaminant transport, particularly in modern landfill designs, the&nbsp;Passive Sink&nbsp;feature in <a href=\"https:\/\/www.gaeatech.com\/pollute.php\">POLLUTEv8<\/a> is an essential tool for representing secondary containment systems. Unlike active collection systems that may have varying mechanical withdrawal rates, a passive sink allows you to model layers\u2014such as a secondary leachate collection system\u2014where contaminants are removed through natural drainage or predefined design parameters.<\/p>\n\n\n\n<h3 class=\"wp-block-heading\" id=\"h-understanding-the-passive-sink-feature\">Understanding the Passive Sink Feature<\/h3>\n\n\n\n<p>In POLLUTEv8, the passive sink is categorized as a&nbsp;special feature&nbsp;used to simulate the removal of a contaminant species from a specific layer within your model. This is most commonly applied to:<\/p>\n\n\n\n<ul class=\"wp-block-list\">\n<li><strong>Secondary Leachate Collection Systems:<\/strong>&nbsp;Modeling a granular layer (e.g., 0.3 m thick) that sits beneath a primary liner.<\/li>\n\n\n\n<li><strong>Leak Detection Systems:<\/strong>&nbsp;Calculating how much of a finite mass of contaminant is captured before reaching the underlying aquifer.<\/li>\n<\/ul>\n\n\n\n<h3 class=\"wp-block-heading\" id=\"h-steps-to-implement-a-passive-sink\">Steps to Implement a Passive Sink<\/h3>\n\n\n\n<p>To use this feature in your simulation, follow these general steps based on typical model configurations:<\/p>\n\n\n\n<ol class=\"wp-block-list\">\n<li><strong>Define Your Layers:<\/strong>&nbsp;Establish your stratigraphic column, including the primary liner, the granular drainage layer (the sink), and the underlying natural geological units.<\/li>\n\n\n\n<li><strong>Select the Passive Sink Special Feature:<\/strong>&nbsp;Within the POLLUTEv8 interface, navigate to the special features section and select the &#8220;Passive Sink&#8221; option.<\/li>\n\n\n\n<li><strong>Configure Layer Parameters:<\/strong>&nbsp;In the example of a secondary leachate collection system, you must specify the thickness and properties of the granular layer.<\/li>\n\n\n\n<li><strong>Set Boundary Conditions:<\/strong>&nbsp;Ensure your model includes appropriate top and bottom boundary conditions, such as a&nbsp;Finite Mass Top Boundary&nbsp;for the contaminant source and a&nbsp;Fixed Outflow Velocity&nbsp;or constant concentration for the bottom aquifer.<\/li>\n\n\n\n<li><strong>Run the Analysis:<\/strong>&nbsp;POLLUTEv8 uses a 1.5-dimensional solution to the advection-dispersion equation, providing fast and accurate results without the need for time-marching procedures.<\/li>\n<\/ol>\n\n\n\n<h3 class=\"wp-block-heading\" id=\"h-why-use-passive-sinks-over-active-sinks\">Why Use Passive Sinks Over Active Sinks?<\/h3>\n\n\n\n<p>While active sampling or collection involves mechanical forces or power sources, passive sinks in modeling represent systems that operate based on their physical structure and environmental conditions. Using this feature allows for a more nuanced and realistic representation of how engineered barriers perform over long-term environmental scenarios.<\/p>\n\n\n\n<hr class=\"wp-block-separator has-alpha-channel-opacity\"\/>\n\n\n\n<h3 class=\"wp-block-heading\" id=\"h-the-governing-equation-with-a-passive-sink\">The Governing Equation with a Passive Sink<\/h3>\n\n\n\n<p>To understand how POLLUTEv8 handles a&nbsp;Passive Sink, it is important to look at how the software modifies the standard advection-dispersion equation. Instead of contaminants simply passing through a layer, a &#8220;removal term&#8221; is added to simulate the lateral drainage of the secondary collection system.<\/p>\n\n\n\n<p>In a standard layer, the transport is governed by the 1D advection-dispersion equation. However, within a&nbsp;Passive Sink&nbsp;layer, POLLUTEv8 incorporates a sink term (S<math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>) to represent the mass removed:<\/p>\n\n\n\n<p><math data-latex=\" \\frac{\\partial c}{\\partial t} = D \\frac{\\partial^2 c}{\\partial z^2} - v \\frac{\\partial c}{\\partial z} - \\frac{Q_{sink}}{n \\cdot H_s} c \"><semantics><mrow><mfrac><mrow><mi>\u2202<\/mi><mi>c<\/mi><\/mrow><mrow><mi>\u2202<\/mi><mi>t<\/mi><\/mrow><\/mfrac><mo>=<\/mo><mi>D<\/mi><mfrac><mrow><msup><mi>\u2202<\/mi><mn>2<\/mn><\/msup><mi>c<\/mi><\/mrow><mrow><mi>\u2202<\/mi><msup><mi>z<\/mi><mn>2<\/mn><\/msup><\/mrow><\/mfrac><mo>\u2212<\/mo><mi>v<\/mi><mfrac><mrow><mi>\u2202<\/mi><mi>c<\/mi><\/mrow><mrow><mi>\u2202<\/mi><mi>z<\/mi><\/mrow><\/mfrac><mo>\u2212<\/mo><mfrac><msub><mi>Q<\/mi><mrow><mi>s<\/mi><mi>i<\/mi><mi>n<\/mi><mi>k<\/mi><\/mrow><\/msub><mrow><mi>n<\/mi><mo>\u22c5<\/mo><msub><mi>H<\/mi><mi>s<\/mi><\/msub><\/mrow><\/mfrac><mi>c<\/mi><\/mrow><annotation encoding=\"application\/x-tex\"> \\frac{\\partial c}{\\partial t} = D \\frac{\\partial^2 c}{\\partial z^2} &#8211; v \\frac{\\partial c}{\\partial z} &#8211; \\frac{Q_{sink}}{n \\cdot H_s} c <\/annotation><\/semantics><\/math><\/p>\n\n\n\n<p>Where:<\/p>\n\n\n\n<ul class=\"wp-block-list\">\n<li>c = Contaminant concentration <math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/li>\n\n\n\n<li>D\u00a0= Hydrodynamic dispersion coefficient <math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/li>\n\n\n\n<li><em>v<math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/em>\u00a0= Advective velocity <math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/li>\n\n\n\n<li>S= The rate of contaminant removal per unit volume<\/li>\n<\/ul>\n\n\n\n<h4 class=\"wp-block-heading\" id=\"h-calculating-the-removal-rate-q-sink\"><strong>Calculating the Removal Rate (Q<sub>sink<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>)<\/strong><\/h4>\n\n\n\n<p>The software calculates the rate of mass removal based on the inflow and outflow velocities of the specific layer. If the Darcy velocity entering the top of the sink is&nbsp;v<sub>in<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>&nbsp;and the velocity leaving the bottom of the sink is&nbsp;v<sub>out<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>, the flow captured by the sink (Q<sub>sink<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>) is defined as:<\/p>\n\n\n\n<p><math data-latex=\"Q_{sink} = v_{in} - v_{out} \"><semantics><mrow><msub><mi>Q<\/mi><mrow><mi>s<\/mi><mi>i<\/mi><mi>n<\/mi><mi>k<\/mi><\/mrow><\/msub><mo>=<\/mo><msub><mi>v<\/mi><mrow><mi>i<\/mi><mi>n<\/mi><\/mrow><\/msub><mo>\u2212<\/mo><msub><mi>v<\/mi><mrow><mi>o<\/mi><mi>u<\/mi><mi>t<\/mi><\/mrow><\/msub><\/mrow><annotation encoding=\"application\/x-tex\">Q_{sink} = v_{in} &#8211; v_{out} <\/annotation><\/semantics><\/math><\/p>\n\n\n\n<p>In a typical secondary leachate collection system,&nbsp;v<sub>out<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>&nbsp;is often much smaller than&nbsp; v<sub>in<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>&nbsp;(due to the efficiency of the secondary liner), meaning most of the contaminant mass entering the layer is &#8220;diverted&#8221; out of the 1D model domain.<\/p>\n\n\n\n<h4 class=\"wp-block-heading\" id=\"h-impact-on-the-finite-mass-boundary\">Impact on the Finite Mass Boundary<\/h4>\n\n\n\n<p>If you are using a&nbsp;Finite Mass Top Boundary, the total mass remaining in the landfill (M<sub>t<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>) at any time (t<math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>) is adjusted by the mass exiting through the sink. The conservation of mass is expressed as:<\/p>\n\n\n\n<p><math data-latex=\"M(t) = M_0 - \\int_{0}^{t} \\left[ f_{sink}(\\tau) + f_{base}(\\tau) \\right] d\\tau\"><semantics><mrow><mi>M<\/mi><mo form=\"prefix\" stretchy=\"false\">(<\/mo><mi>t<\/mi><mo form=\"postfix\" stretchy=\"false\">)<\/mo><mo>=<\/mo><msub><mi>M<\/mi><mn>0<\/mn><\/msub><mo>\u2212<\/mo><msubsup><mo movablelimits=\"false\">\u222b<\/mo><mn>0<\/mn><mi>t<\/mi><\/msubsup><mrow><mo fence=\"true\" form=\"prefix\">[<\/mo><msub><mi>f<\/mi><mrow><mi>s<\/mi><mi>i<\/mi><mi>n<\/mi><mi>k<\/mi><\/mrow><\/msub><mo form=\"prefix\" stretchy=\"false\">(<\/mo><mi>\u03c4<\/mi><mo form=\"postfix\" stretchy=\"false\">)<\/mo><mo>+<\/mo><msub><mi>f<\/mi><mrow><mi>b<\/mi><mi>a<\/mi><mi>s<\/mi><mi>e<\/mi><\/mrow><\/msub><mo form=\"prefix\" stretchy=\"false\">(<\/mo><mi>\u03c4<\/mi><mo form=\"postfix\" stretchy=\"false\">)<\/mo><mo fence=\"true\" form=\"postfix\">]<\/mo><\/mrow><mi>d<\/mi><mi>\u03c4<\/mi><\/mrow><annotation encoding=\"application\/x-tex\">M(t) = M_0 &#8211; \\int_{0}^{t} \\left[ f_{sink}(\\tau) + f_{base}(\\tau) \\right] d\\tau<\/annotation><\/semantics><\/math><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/p>\n\n\n\n<p>Where:<\/p>\n\n\n\n<ul class=\"wp-block-list\">\n<li>M<sub>0<math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/sub>\u00a0= Initial mass of contaminant.<\/li>\n\n\n\n<li>f<sub>sink<math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math><\/sub>\u00a0= Mass flux removed by the passive sink.<\/li>\n\n\n\n<li>f<sub>base<\/sub><math xmlns=\"http:\/\/www.w3.org\/1998\/Math\/MathML\"><semantics><\/semantics><\/math>\u00a0= Mass flux passing into the underlying aquifer.<\/li>\n<\/ul>\n\n\n\n<hr class=\"wp-block-separator has-alpha-channel-opacity\"\/>\n\n\n\n<h3 class=\"wp-block-heading\" id=\"h-summary\">Summary<\/h3>\n\n\n\n<p>The&nbsp;Passive Sink&nbsp;feature in&nbsp;GAEA Technologies POLLUTEv8&nbsp;is used to model secondary leachate collection and leak detection systems. By defining a specific layer as a sink, users can accurately simulate the removal of contaminants as they migrate through a landfill&#8217;s engineered barriers toward an aquifer. This feature is a critical component of advanced contaminant transport modeling, ensuring realistic performance assessments of composite liners and multiple barrier systems.<\/p>\n\n\n\n<p><\/p>\n","protected":false},"excerpt":{"rendered":"<p>When modeling complex contaminant transport, particularly in modern landfill designs, the&nbsp;Passive Sink&nbsp;feature in POLLUTEv8 is an essential tool for representing secondary containment systems. Unlike active collection systems that may have varying mechanical withdrawal rates, a passive sink allows you to model layers\u2014such as a secondary leachate collection system\u2014where contaminants are removed through natural drainage or [&hellip;]<\/p>\n","protected":false},"author":1,"featured_media":91250,"comment_status":"open","ping_status":"open","sticky":false,"template":"","format":"standard","meta":{"_jetpack_memberships_contains_paid_content":false,"footnotes":""},"categories":[1204,726],"tags":[678,674,192,675,677,676,549],"class_list":["post-1606","post","type-post","status-publish","format-standard","has-post-thumbnail","hentry","category-contaminant-transport-modeling-tutorials","category-training-and-tutorials","tag-advection-dispersion-equation","tag-contaminant-migration","tag-gaea-technologies","tag-landfill-modeling","tag-leachate-collection","tag-passive-sink","tag-pollutev8"],"yoast_head":"<!-- This site is optimized with the Yoast SEO Premium plugin v27.4 (Yoast SEO v27.4) - 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