<?xml version="1.0" encoding="UTF-8"?><?xml-stylesheet type="text/xsl" href="static/style.xsl"?><OAI-PMH xmlns="http://www.openarchives.org/OAI/2.0/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/ http://www.openarchives.org/OAI/2.0/OAI-PMH.xsd"><responseDate>2026-09-20T03:28:55Z</responseDate><request verb="GetRecord" identifier="oai:dspace.mit.edu:1721.1/31143" metadataPrefix="dim">https://dspace.mit.edu/server/oai/request</request><GetRecord><record><header><identifier>oai:dspace.mit.edu:1721.1/31143</identifier><datestamp>2022-01-13T07:54:23Z</datestamp><setSpec>com_1721.1_7582</setSpec><setSpec>com_1721.1_7581</setSpec><setSpec>col_1721.1_131023</setSpec></header><metadata><dim:dim xmlns:dim="http://www.dspace.org/xmlns/dspace/dim" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xmlns:doc="http://www.lyncode.com/xoai" xsi:schemaLocation="http://www.dspace.org/xmlns/dspace/dim http://www.dspace.org/schema/dim.xsd">
   <dim:field mdschema="dc" element="contributor" qualifier="advisor" lang="en_US">Harold Hemond.</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="author" lang="en_US">Peterson, Eliza J. R. (Eliza Jane Reader), 1979-</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="other" lang="en_US">Massachusetts Institute of Technology. Dept. of Civil and Environmental Engineering.</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="department">Massachusetts Institute of Technology. Department of Civil and Environmental Engineering</dim:field>
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   <dim:field mdschema="dc" element="date" qualifier="accessioned">2006-02-02T18:52:24Z</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="available">2006-02-02T18:52:24Z</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="copyright" lang="en_US">2005</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="issued" lang="en_US">2005</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="uri">http://hdl.handle.net/1721.1/31143</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="oclc" lang="en_US">61184873</dim:field>
   <dim:field mdschema="dc" element="description" lang="en_US">Thesis (S.M.)--Massachusetts Institute of Technology, Dept. of Civil and Environmental Engineering, 2005.</dim:field>
   <dim:field mdschema="dc" element="description" lang="en_US">Includes bibliographical references (leaves 94-96).</dim:field>
   <dim:field mdschema="dc" element="description" qualifier="abstract" lang="en_US">The profiles of CH₄ and CO₂ obtained by the use of a novel sampler, along with the profiles for nitrate (NO₃⁻), sulfate (So₄³⁻)and iron (Fe²⁺) were used to estimate the rates of the various anaerobic decomposition reactions during spring and fall stratification in Upper Mystic Lake. The equivalent electron and carbon flow of the reactions were also calculated to obtain a mass balance within the hypolimnia of UML. From the calculations, the approximate organic carbon decomposition rate, measured as CO₂ accumulation, was 7.54 mmol m⁻² d⁻¹. The amount of decomposition from the reactions involving nitrate, sulfate, iron and methane formation together accounted for 80% of the total organic carbon decomposition. Therefore, 20% of the CO₂ accumulation in UML could not be accounted for. Possible explanations for the excess CO₂ production could be the formation of reduced iron minerals and/or the loss of methane due to ebullition and oxidation. Such explanations suggest future studies of UML to better resolve the electron budget. In order to study the redox balance in Upper Mystic Lake, a method was devised for precisely sampling dissolved gases in the water column. Like other stratified lakes, UML has a large amount of anaerobic metabolism of organic matter occurring in the sediments and a subsequent accumulation of methane (CH₄) and carbon dioxide (CO₂) in the hypolimnia. Previously, limnological sampling for dissolved gases involved filling glass bottles with water pumped from depth using a peristaltic pump; however, such methods introduce the potential for gas exchange with the atmosphere. Therefore, there was a need for a dissolved gas sampler that could be used to obtain samples at precise depth intervals while at the same time isolating the samples from outside influences.</dim:field>
   <dim:field mdschema="dc" element="description" qualifier="statementofresponsibility" lang="en_US">by Eliza J.R. Peterson.</dim:field>
   <dim:field mdschema="dc" element="description" qualifier="degree" lang="en_US">S.M.</dim:field>
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   <dim:field mdschema="dc" element="publisher" lang="en_US">Massachusetts Institute of Technology</dim:field>
   <dim:field mdschema="dc" element="rights" lang="en_US">M.I.T. theses are protected by copyright. They may be viewed from this source for any purpose, but reproduction or distribution in any format is prohibited without written permission. See provided URL for inquiries about permission.</dim:field>
   <dim:field mdschema="dc" element="rights" qualifier="uri">http://dspace.mit.edu/handle/1721.1/7582</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_US">Civil and Environmental Engineering.</dim:field>
   <dim:field mdschema="dc" element="title" lang="en_US">Carbon and electron flow via methanogenesis, So₄²⁻, NO₃⁻ and Fe³⁺ reduction in the anoxic hypolimnia of upper Mystic Lake</dim:field>
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   	&lt;Title>Carbon and electron flow via methanogenesis, So₄²⁻, NO₃⁻ and Fe³⁺ reduction in the anoxic hypolimnia of upper Mystic Lake&lt;/Title>
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   	&lt;PublicationDate>2005&lt;/PublicationDate>
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        	&lt;DisplayName>Peterson, Eliza J. R. (Eliza Jane Reader), 1979-&lt;/DisplayName>
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    &lt;Keyword>Civil and Environmental Engineering.&lt;/Keyword>
   	&lt;Abstract>The profiles of CH₄ and CO₂ obtained by the use of a novel sampler, along with the profiles for nitrate (NO₃⁻), sulfate (So₄³⁻)and iron (Fe²⁺) were used to estimate the rates of the various anaerobic decomposition reactions during spring and fall stratification in Upper Mystic Lake. The equivalent electron and carbon flow of the reactions were also calculated to obtain a mass balance within the hypolimnia of UML. From the calculations, the approximate organic carbon decomposition rate, measured as CO₂ accumulation, was 7.54 mmol m⁻² d⁻¹. The amount of decomposition from the reactions involving nitrate, sulfate, iron and methane formation together accounted for 80% of the total organic carbon decomposition. Therefore, 20% of the CO₂ accumulation in UML could not be accounted for. Possible explanations for the excess CO₂ production could be the formation of reduced iron minerals and/or the loss of methane due to ebullition and oxidation. Such explanations suggest future studies of UML to better resolve the electron budget. In order to study the redox balance in Upper Mystic Lake, a method was devised for precisely sampling dissolved gases in the water column. Like other stratified lakes, UML has a large amount of anaerobic metabolism of organic matter occurring in the sediments and a subsequent accumulation of methane (CH₄) and carbon dioxide (CO₂) in the hypolimnia. Previously, limnological sampling for dissolved gases involved filling glass bottles with water pumped from depth using a peristaltic pump; however, such methods introduce the potential for gas exchange with the atmosphere. Therefore, there was a need for a dissolved gas sampler that could be used to obtain samples at precise depth intervals while at the same time isolating the samples from outside influences.&lt;/Abstract>
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