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<article article-type="research-article" dtd-version="1.1" specific-use="sps-1.7" xml:lang="en" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink">
	<front>
		<journal-meta>
			<journal-id journal-id-type="publisher-id">dyna</journal-id>
			<journal-title-group>
				<journal-title>DYNA</journal-title>
				<abbrev-journal-title abbrev-type="publisher">Dyna rev.fac.nac.minas</abbrev-journal-title>
			</journal-title-group>
			<issn pub-type="ppub">0012-7353</issn>
			<publisher>
				<publisher-name>Universidad Nacional de Colombia</publisher-name>
			</publisher>
		</journal-meta>
		<article-meta>
			<article-id pub-id-type="doi">10.15446/dyna.v85n207.69309</article-id>
			<article-categories>
				<subj-group subj-group-type="heading">
					<subject>Artículos</subject>
				</subj-group>
			</article-categories>
			<title-group>
				<article-title>Effectiveness analysis of the ITM environmental programs: saving and efficient use of electric energy and water, and comprehensive solid waste management. A case study</article-title>
				<trans-title-group xml:lang="es">
					<trans-title>Análisis de la efectividad de los programas ambientales del ITM: uso eficiente y ahorro de energía eléctrica y agua, y el manejo integral de desechos sólidos. Caso de estudio</trans-title>
				</trans-title-group>
			</title-group>
			<contrib-group>
				<contrib contrib-type="author">
					<name>
						<surname>Aristizábal-Alzate</surname>
						<given-names>Carlo Esteban</given-names>
					</name>
					<xref ref-type="aff" rid="aff1"><sup>
 <italic>a</italic>
</sup></xref>
					<xref ref-type="aff" rid="aff2"><sup>
 <italic>b</italic>
</sup></xref>
				</contrib>
				<contrib contrib-type="author">
					<name>
						<surname>González-Manosalva</surname>
						<given-names>José Luis</given-names>
					</name>
					<xref ref-type="aff" rid="aff2"><sup>
 <italic>b</italic>
</sup></xref>
				</contrib>
			</contrib-group>
			<aff id="aff1">
				<label>a</label>
				<institution content-type="original"> Grupo de Investigación en Materiales y Energía (MATyER). Facultad de Ingeniería, Instituto Tecnológico Metropolitano de Medellín. Medellín, Colombia. carlosaristizabal207157@correo.itm.edu.co</institution>
				<institution content-type="normalized">Instituto Tecnológico Metropolitano</institution>
				<institution content-type="orgdiv2">Grupo de Investigación en Materiales y Energía (MATyER)</institution>
				<institution content-type="orgdiv1">Facultad de Ingeniería</institution>
				<institution content-type="orgname">Instituto Tecnológico Metropolitano de Medellín</institution>
				<addr-line>
					<city>Medellín</city>
				</addr-line>
				<country country="CO">Colombia</country>
				<email>carlosaristizabal207157@correo.itm.edu.co</email>
			</aff>
			<aff id="aff2">
				<label>b</label>
				<institution content-type="original"> Grupo de Investigación en Química Básica y Ambiente (ALQUIMIA). Facultad de Ciencias Exactas y Naturales, Instituto Tecnológico Metropolitano de Medellín, Medellín, Colombia. josegonzalez@itm.edu.co </institution>
				<institution content-type="normalized">Instituto Tecnológico Metropolitano</institution>
				<institution content-type="orgdiv2">Grupo de Investigación en Química Básica y Ambiente (ALQUIMIA)</institution>
				<institution content-type="orgdiv1">Facultad de Ciencias Exactas y Naturales</institution>
				<institution content-type="orgname">Instituto Tecnológico Metropolitano de Medellín</institution>
				<addr-line>
					<city>Medellín</city>
				</addr-line>
				<country country="CO">Colombia</country>
				<email>josegonzalez@itm.edu.co</email>
			</aff>
			<pub-date pub-type="epub-ppub">
				<season>Oct-Dec</season>
				<year>2018</year>
			</pub-date>
			<volume>85</volume>
			<issue>207</issue>
			<fpage>36</fpage>
			<lpage>43</lpage>
			<history>
				<date date-type="received">
					<day>07</day>
					<month>12</month>
					<year>2017</year>
				</date>
				<date date-type="rev-recd">
					<day>13</day>
					<month>08</month>
					<year>2018</year>
				</date>
				<date date-type="accepted">
					<day>24</day>
					<month>09</month>
					<year>2018</year>
				</date>
			</history>
			<permissions>
				<license license-type="open-access" xlink:href="https://creativecommons.org/licenses/by-nc-nd/4.0/" xml:lang="en">
					<license-p>This is an open-access article distributed under the terms of the Creative Commons Attribution License</license-p>
				</license>
			</permissions>
			<abstract>
				<title>Abstract</title>
				<p>Universities are complex organizations, so when implementing an EMS and adopting strategies, methodologies and programs they must involve the entire university system to minimize the negative impacts on the environment and, thus, lead the search for sustainable or carbon neutral organizations. Carbon Footprint was used as an indicator to measure the sustainability effectiveness of the environmental programs implemented and promoted by the EMS-ITM and how they mitigate the emission of GHGs. The calculation of this indicator was developed following ISO 14040-14044 and ISO 14064, for the ITM-Robledo campus and for the period 2015-2017. The results show the relevance and the reduction in the GHG emission levels achieved by the environmental programs studied, especially by the comprehensive solid waste management program, with which the highest levels of mitigation are achieved.</p>
			</abstract>
			<trans-abstract xml:lang="es">
				<title>Resumen</title>
				<p>Las universidades son organizaciones complejas, por lo que deben implementar un SGA y adoptar estrategias, metodologías y programas que involucren a todo el sistema universitario, con el fin de reducir al máximo los impactos negativos sobre el medio ambiente y así, liderar la tendencia que busca organizaciones sostenibles o carbono neutro. La Huella de Carbono se utilizó como indicador para medir la eficacia de la sostenibilidad de los programas ambientales implementados y promocionados por el SGA-ITM, y como estos mitigan la emisión de GEI. El cálculo de este indicador se desarrolló siguiendo la norma ISO 14040-14044 y la ISO 14064, para la sede ITM-Robledo y para el período 2015-2017. Los resultados muestran la relevancia y la reducción en los niveles de emisión de GEI, logrados por los programas ambientales estudiados, sobresaliendo el programa de manejo integral de residuos sólidos, con el cual se logran los mayores niveles de mitigación.</p>
			</trans-abstract>
			<kwd-group xml:lang="en">
				<title><bold>
 <italic>Keywords</italic>:</bold></title>
				<kwd>environmental program</kwd>
				<kwd>carbon footprint</kwd>
				<kwd>GHG mitigation</kwd>
				<kwd>effectiveness</kwd>
				<kwd>sustainability</kwd>
			</kwd-group>
			<kwd-group xml:lang="es">
				<title><bold>
 <italic>Palabras clave</italic>:</bold></title>
				<kwd>programa ambiental</kwd>
				<kwd>huella de carbono</kwd>
				<kwd>mitigación de GEI</kwd>
				<kwd>eficacia</kwd>
				<kwd>sostenibilidad</kwd>
			</kwd-group>
			<counts>
				<fig-count count="15"/>
				<table-count count="7"/>
				<equation-count count="1"/>
				<ref-count count="18"/>
				<page-count count="8"/>
			</counts>
		</article-meta>
	</front>
	<body>
		<sec sec-type="intro">
			<title>1. Introduction<xref ref-type="fn" rid="fn1"><sup>1</sup></xref>
			</title>
			<p>Similar to a society, the operation and maintenance of a university is a process of socioeconomic metabolism, in a network of complex interactions involving its processes and actors, taking various raw materials, energy and water and transforming them into products, services and waste. [<xref ref-type="bibr" rid="B1">1</xref>]. The adoption and implementation of a comprehensive environmental model, known as the Environmental Management System (EMS), is proposed to improve sustainability in academic institutions and for the reasons expounded above, as it can identify and address, in a systematic way, the various dimensions involved in the operation of the organization [<xref ref-type="bibr" rid="B1">1</xref>,<xref ref-type="bibr" rid="B2">2</xref>].</p>
			<p>Using an EMS framework and rigorous and diligent studies, the thorough evaluation and consequent assessment of the Metropolitan Technological Institute of Medellín (ITM), was able to determine its most significant environmental aspects and impacts, developing for each of them an Objective, a Goal and a Program.</p>
			<p>The purpose of the implementation of the different Environmental Programs is to promote sustainable development with reference to the ITM’s environmental policy, through the execution of programs aimed at the prevention and minimization of negative environmental impacts and the optimization of the use of resources in institutional processes, promoting environmental responsibility among the ITM community members, within the framework of fulfilling current environmental normativity. The environmental programs, being the objects of study of the present analysis, are listed hereafter:</p>
			<sec>
				<title>- <bold>Efficient Use of Water and Water Saving Program</bold></title>
				<p>The purpose of this program is to promote a gradual standard of efficient water use within the ITM and to minimize the consumption of this natural resource.</p>
			</sec>
			<sec>
				<title>- <bold>Efficient use of electricity and energy saving program</bold></title>
				<p>The purpose of the implementation of this program is to promote a gradual standard of efficient electricity use within the ITM and minimize the consumption of this energy resource.</p>
			</sec>
			<sec>
				<title>- <bold>Comprehensive management of solid waste program</bold></title>
				<p>Established with the purpose of promoting the comprehensive management of the Institutions’ waste, while being able to identify the amount of solid waste generated by each member of the ITM community and to assess the effectiveness of the actions undertaken to reduce waste generation or keep waste generation at a minimum where possible. In addition, the program will help to identify the proportion of recyclable material within the total waste generated and the effectiveness of the actions taken to maximize recyclable materials.</p>
				<p>This article analyzes the Robledo campus and each of the programs, starting with a comparison between the different instances of electricity and water consumption, and the report of the solid waste generation, for each month of the years 2015 and 2016, along with the information provided for the current year. Subsequently, a study of the sustainability and effectiveness of each program is carried out, based on sustainability indicators such as a decrease in the carbon footprint. The intention here is to show a positive environmental impact caused by the implementation of environmental programs within the ITM and the effectiveness of the measures applied by the EMS-ITM, as a step towards a carbon neutral institution.</p>
			</sec>
		</sec>
		<sec>
			<title><italic>1.1</italic>. <bold>
 <italic>Public services: water, electricity and sanitation</italic>
</bold></title>
			<p>The drinking water and electricity service is supplied and managed by Empresas Públicas de Medellín (EPM).</p>
			<p>The sanitation service is provided and managed by Empresas Varias de Medellín and consists of the collection, transport and final disposal into landfill. The landfill known as La Pradera is located within the jurisdiction of the municipality of Don Matías (Antioquia department), 60 km from the city of Medellín.</p>
			<p>In <xref ref-type="fig" rid="f1">Fig. 1</xref>, the make of garbage truck is shown to determine the type of fuel it consumes and its efficiency.</p>
			<p>
				<fig id="f1">
					<label>Figure 1</label>
					<caption>
						<title>Vehicles run on Natural Gas solid waste collection trucks of EMVARIAS of Medellín.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf1.png"/>
					<attrib><bold>Source:</bold> EPM</attrib>
				</fig>
			</p>
			<p>The information available on this type of vehicle and the closest approximation to the Medellín context is: <italic>“</italic>Kenworth T440 vehicle model 2017, equipped with a Cummins Westport natural gas engine of 320 Hp (horsepower) and 8900 cm<sup>3</sup>. The capacity of the natural gas tanks is 618 liters, equivalent to 155 m<sup>3</sup>, which gives an approximate range of 200 km.</p>
			<p>This truck complies with EPA 2016 emission regulations, has a six-speed Allison automatic transmission, ABS brakes, anti-skid control and differential lock. The compactor unit has a capacity of 20 cubic yards for an equivalent compaction of 12 Tons '' <bold>Source:</bold> TGI<xref ref-type="fn" rid="fn2"><sup>2</sup></xref>
			</p>
			<p>This information on the landfill and garbage collection vehicles is used to determine the Carbon Footprint associated with the transport of solid waste generated by the ITM and how, indirectly, the recycling and composting of organic waste reduces GHG emissions by subtracting the amount of solid waste that must be transported to landfill.</p>
		</sec>
		<sec>
			<title>2. <bold>Characterization of resource consumption and generation of waste</bold></title>
			<p>In this section, the consumption of electricity and water is described, as obtained from the invoices issued monthly by the suppliers of the different services mentioned for the years 2015, 2016 and 2017. The information is shown in <xref ref-type="fig" rid="f2">Fig. 2</xref> and in <xref ref-type="fig" rid="f3">Fig. 3</xref>.</p>
			<p>
				<fig id="f2">
					<label>Figure 2</label>
					<caption>
						<title>Water consumption (m<sup>3</sup>) of the ITM’s Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf2.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<fig id="f3">
					<label>Figure 3</label>
					<caption>
						<title>Electricity consumption (m<sup>3</sup>) of the ITM’s Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf3.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>The generation of solid waste by type is illustrated in <xref ref-type="fig" rid="f4">Figs. 4</xref>, <xref ref-type="fig" rid="f5">5</xref> and <xref ref-type="fig" rid="f6">6</xref>. It should be noted that in the present study the Hazardous Waste generated by the institution is not taken into account, since the data analyzed here from the collection company, as well as the emission factors, are for the final disposal of solid waste in a Non-Hazardous Waste Landfill.</p>
			<p>
				<fig id="f4">
					<label>Figure 4</label>
					<caption>
						<title>Generation of Ordinary Solid Waste from ITM’s Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf4.png"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<fig id="f5">
					<label>Figure 5</label>
					<caption>
						<title>Generation of Organic Solid Waste from ITM’s Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf5.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<fig id="f6">
					<label>Figure 6</label>
					<caption>
						<title>Generation of Recyclable Solids in the ITM’s Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf6.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
		</sec>
		<sec sec-type="methods">
			<title>3. <bold>Methodology</bold></title>
			<p>The aim of this section is to briefly describe what a Carbon Footprint is, its method of calculation and the data needed to calculate it. This because the objective of the implementation of the programs proposed by the ITM’s EMS is to make use of the resources and to dispose of waste in a rational and responsible manner, that is, to look beyond the economic interests in the potential savings achieved by minimizing the consumption of natural and energy resources, and the generation of solid waste that goes to landfill. Instead, the main purposes are to have a positive impact on the environment, to turn the ITM into a sustainable institution, to minimize the emission of pollutants, to establish clean, pleasant and suitable spaces for students and workers, and become a carbon neutral institution.</p>
			<sec>
				<title><italic>3.1.</italic> 
 <bold>
 <italic>Definition of Carbon Footprint</italic>
</bold></title>
				<p>As an indicator of sustainability, Carbon Footprint serves to determine total emissions of greenhouse gases (GHG), emitted by the direct or indirect effect of an individual, organization, event, product and/or service [<xref ref-type="bibr" rid="B3">3</xref>-<xref ref-type="bibr" rid="B5">5</xref>]. The method of measurement of this parameter or indicator consists of creating an inventory of GHG emissions, based on a Life Cycle Analysis, for each of the materials, resources and services required by the object of study during all its useful life or for an established period of time [<xref ref-type="bibr" rid="B6">6</xref>,<xref ref-type="bibr" rid="B7">7</xref>].</p>
			</sec>
			<sec>
				<title><italic>3.2</italic>. <bold>
 <italic>Calculating Carbon Footprint</italic>
</bold></title>
				<p>Before starting calculations for the Carbon Footprint, all anthropogenic GHG emissions within the organization must be estimated (CO<sub>2</sub>, CH<sub>4</sub>, N<sub>2</sub>O, HFC, PFC and SF<sub>6</sub>), and then, this information is converted into equivalent CO<sub>2</sub> emissions (KgCO<sub>2</sub> eq) using the global warming potential factor [<xref ref-type="bibr" rid="B8">8</xref>,<xref ref-type="bibr" rid="B9">9</xref>]. <xref ref-type="table" rid="t1">Table 1</xref> shows the conversion factors of the different GHG to Kg of CO<sub>2</sub> equivalents.</p>
				<p>
					<table-wrap id="t1">
						<label>Table 1</label>
						<caption>
							<title>Global warming potential factors of different GHG to Kg of CO2 equivalents.</title>
						</caption>
						<graphic xlink:href="0012-7353-dyna-85-207-36-gt1.jpg"/>
						<table-wrap-foot>
							<fn id="TFN1">
								<p><bold>Source:</bold> [<xref ref-type="bibr" rid="B10">10</xref>,<xref ref-type="bibr" rid="B11">11</xref>]</p>
							</fn>
						</table-wrap-foot>
					</table-wrap>
				</p>
				<p>The information reported in <xref ref-type="table" rid="t1">Table 1</xref>, together with the Emission Factors (<xref ref-type="table" rid="t2">Table 2</xref>) and <xref ref-type="disp-formula" rid="e1">Eq. (1)</xref>, are used to calculate the Total Carbon Footprint in Kg CO<sub>2</sub>eq.</p>
				<p>
					<disp-formula id="e1">
						<graphic xlink:href="0012-7353-dyna-85-207-36-e1.jpg"/>
					</disp-formula>
				</p>
				<p>Where TCF is the Total Carbon Footprint in Kg CO<sub>2</sub>eq, GWP<sub>i</sub> is the Global Warming Potential or the conversion factor, for the GHG i to Kg CO<sub>2</sub>eq, FE<sub>i</sub> is the GHG i Emission Factor of the Activity or Resource j and A<sub>j</sub> is the factor of the total consumption of the resource or service studied.</p>
			</sec>
			<sec>
				<title><italic>3.3.</italic> 
 <bold>
 <italic>Scope of the study</italic>
</bold></title>
				<p>To calculate the Carbon Footprint, first, the direct and indirect emissions are quantified, assuring that they are within the operational limits and the scope of the study [<xref ref-type="bibr" rid="B8">8</xref>,<xref ref-type="bibr" rid="B12">12</xref>]. These are described below and are illustrated graphically in <xref ref-type="fig" rid="f7">Fig. 7</xref>.</p>
				<p>
					<fig id="f7">
						<label>Figure 7</label>
						<caption>
							<title>Graphical representation of the study dimensions used to determine GHG emissions.</title>
						</caption>
						<graphic xlink:href="0012-7353-dyna-85-207-36-gf7.png"/>
						<attrib><bold>Source:</bold> [<xref ref-type="bibr" rid="B12">12</xref>]</attrib>
					</fig>
				</p>
				<p>Due to the characteristics of the resources consumed, waste generation and services rendered, this study focuses solely on indirect emissions, which correspond to <bold>Dimension 2 (Water and Electric Power)</bold> and <bold>Dimension 3 (Sanitation Service)</bold>, since the resources and services considered are provided by organizations in which the ITM has no intervention and/or operational control [<xref ref-type="bibr" rid="B4">4</xref>,<xref ref-type="bibr" rid="B8">8</xref>,<xref ref-type="bibr" rid="B12">12</xref>]. However, the ITM has used the <bold>recycling of waste and the composting of organic or biodegradable waste</bold> as mitigation measures for the emission of GHGs [<xref ref-type="bibr" rid="B11">11</xref>,<xref ref-type="bibr" rid="B13">13</xref>-<xref ref-type="bibr" rid="B15">15</xref>], which are taken from <bold>Dimension 1</bold>, since the ITM has operational control of these two activities and also, has so within the limits of the operation of the university institution. Additionally, these activities reduce the environmental impacts related to the emission of GHG through the use of collection trucks, from the place of collection to the landfill.</p>
			</sec>
			<sec>
				<title><italic>3.4. Emission factors by type of resource, services contracted with third parties and GHG emission mitigation activities</italic></title>
				<p>
					<xref ref-type="table" rid="t2">Table 2</xref> shows the GHG generation emission factors for the different resources and activities related to the development of the environmental programs analyzed in the present study.</p>
				<p>
					<table-wrap id="t2">
						<label>Table 2</label>
						<caption>
							<title>GHG emission factors for the energy and natural resources used by the ITM, and others related to the generation of solid waste.</title>
						</caption>
						<graphic xlink:href="0012-7353-dyna-85-207-36-gt2.jpg"/>
						<table-wrap-foot>
							<fn id="TFN2">
								<label><sup>a</sup></label>
								<p> Composting operations are considered carbon neutral (KgCO<sub>2</sub>/Ton=0) <italic>[</italic><xref ref-type="bibr" rid="B11"><italic>11</italic></xref><italic>]</italic></p>
							</fn>
							<fn id="TFN3">
								<label><sup>b</sup></label>
								<p> Landfill without methane recovery (CH<sub>4</sub>)</p>
							</fn>
							<fn id="TFN4">
								<label><sup>c</sup></label>
								<p>Post-consumption waste from the First Life do not have any environmental burden when they are recycled and used as raw materials in the Second Life <italic>[</italic><xref ref-type="bibr" rid="B14"><italic>14</italic></xref><italic>]</italic></p>
							</fn>
							<fn id="TFN5">
								<p><bold>Source:</bold> the authors</p>
							</fn>
						</table-wrap-foot>
					</table-wrap>
				</p>
			</sec>
			<sec>
				<title><italic>3.5. Quality of data, considerations and assumptions about missing information</italic></title>
				<sec>
					<title><bold>
 <italic>3.5.1.</italic> Electricity and drinking water</bold></title>
					<p>As there is no information available for the months September to December 2017, they will be calculated based on the percentages of increase or decrease in consumption of these resources for these same months in 2015 and 2016, as the ITM’s consumption dynamics repeat year after year.</p>
				</sec>
				<sec>
					<title>3.5.2. <bold>Solid waste</bold></title>
					<p>Given that there is no information on solid waste for December 2015, the information from January 2016 will be used, since the ITM’s waste generation dynamics for these two months are similar.</p>
					<p>For the missing solid waste generation information from 2017, it will be calculated in the same way as the calculation of the electricity and water consumption of the missing months from the current year.</p>
				</sec>
				<sec>
					<title>3.5.3. <bold>Factores de emisión, constantes y datos secundarios Emission factors, constants and secondary data</bold></title>
					<p>This study uses information provided by the entities related to the evaluated material, product or service. If information from primary sources is not available, information reported in the literature will be used, as long as it is suitable for the Colombian context.</p>
				</sec>
			</sec>
		</sec>
		<sec sec-type="results">
			<title>4. <bold>Carbon Footprint results</bold></title>
			<sec>
				<title><italic>4.1. Electricity</italic></title>
				<p>In <xref ref-type="fig" rid="f8">Fig. 8</xref>, the Carbon Footprint (TonCO<sub>2</sub> eq) associated with the consumption of electricity is shown, month to month, for the years studied.</p>
				<p>
					<fig id="f8">
						<label>Figure 8</label>
						<caption>
							<title>Carbon Footprint for Electricity (TonCO<sub>2</sub>eq) of the ITM Robledo campus.</title>
						</caption>
						<graphic xlink:href="0012-7353-dyna-85-207-36-gf8.jpg"/>
						<attrib><bold>Source:</bold> the authors</attrib>
					</fig>
				</p>
			</sec>
			<sec>
				<title><italic>4.2.</italic> 
 <bold>
 <italic>Organic waste</italic>
</bold></title>
				<p>The organic waste is the entire biodegradable portion separated from the total waste generated in the ITM Robledo. Additionally, as mentioned above, this biodegradable portion is disposed of and treated entirely through composting processes at the ITM. Therefore, they do not generate GHG by being transported to landfill and also because they are subjected to anaerobic biological degradation at the final disposal composting site, and so this treatment is considered a mitigating agent in the emission of GHG.</p>
				<p>Below, <xref ref-type="table" rid="t4">Table 4</xref> shows the CF along with the emissions not created because there is no need to transport to landfill since the final destination is the composting equipment.</p>
			</sec>
			<sec>
				<title><italic>4.3.</italic> 
 <bold>
 <italic>Drinking water</italic>
</bold></title>
				<p>In <xref ref-type="fig" rid="f9">Fig. 9</xref>, the Carbon Footprint (TonCO<sub>2</sub> eq) associated with the consumption of drinking water is shown, month-to-month, for the years studied.</p>
				<p>
					<fig id="f9">
						<label>Figure 9</label>
						<caption>
							<title>Carbon Footprint for Drinking Water (TonCO2eq) of the ITM Robledo campus.</title>
						</caption>
						<graphic xlink:href="0012-7353-dyna-85-207-36-gf9.jpg"/>
						<attrib><bold>Source:</bold> the authors</attrib>
					</fig>
				</p>
			</sec>
			<sec>
				<title><italic>4.4.</italic> 
 <bold>
 <italic>Solid waste</italic>
</bold></title>
				<sec>
					<title>4.4.1. <bold>Ordinary solid waste</bold></title>
					<p>Ordinary waste is any material disposed of at the different solid waste collection points, which cannot be harnessed or revalued in any way and therefore are taken to landfill for final disposal. This study considers environmental impact as the GHG emissions from the collection trucks combusting </p>
					<p>Vehicular Natural Gas during the transport of material from the ITM Robledo to landfill. In <xref ref-type="table" rid="t3">Table 3</xref>, the emissions of the different GHGs and the Carbon Footprint (KgCO<sub>2</sub> eq) are shown.</p>
					<p>
						<table-wrap id="t3">
							<label>Table 3</label>
							<caption>
								<title>Carbon Footprint (KgCO2 eq) and GHG emission, for the transport of ordinary waste from the ITM Robledo to the landfill.</title>
							</caption>
							<graphic xlink:href="0012-7353-dyna-85-207-36-gt3.jpg"/>
							<table-wrap-foot>
								<fn id="TFN6">
									<p><bold>Source:</bold> the authors</p>
								</fn>
							</table-wrap-foot>
						</table-wrap>
					</p>
					<p>Because it is not disposed of in landfill and due to its biological degradation inside the final disposal tanks, organic waste does not generate GHGs. Therefore, as shown in <xref ref-type="table" rid="t5">Table 5</xref>, GHGs that are no longer emitted by this waste are subject to a harnessing process through composting.</p>
					<p>
						<table-wrap id="t4">
							<label>Table 4</label>
							<caption>
								<title>Carbon Footprint (KgCO<sub>2</sub> eq) and GHG emission, for the transport of organic waste from the ITM Robledo to landfill.</title>
							</caption>
							<graphic xlink:href="0012-7353-dyna-85-207-36-gt4.jpg"/>
							<table-wrap-foot>
								<fn id="TFN7">
									<p><bold>Source:</bold> the authors</p>
								</fn>
							</table-wrap-foot>
						</table-wrap>
					</p>
					<p>
						<table-wrap id="t5">
							<label>Table 5</label>
							<caption>
								<title>Carbon footprint (TonCO<sub>2</sub> eq) and mitigated GHG emissions, due to the non-disposal of organic waste in landfill, without methane recovery.</title>
							</caption>
							<graphic xlink:href="0012-7353-dyna-85-207-36-gt5.jpg"/>
							<table-wrap-foot>
								<fn id="TFN8">
									<p><bold>Source:</bold> the authors</p>
								</fn>
							</table-wrap-foot>
						</table-wrap>
					</p>
					<p>
						<xref ref-type="table" rid="t6">Table 6</xref> illustrates GHGs resulting from an organic waste composting process similar to that carried out at the ITM</p>
					<p>
						<table-wrap id="t6">
							<label>Table 6</label>
							<caption>
								<title>Carbon Footprint (TonCO<sub>2</sub> eq) and GHG emissions from the organic waste composting treatment at the ITM Robledo. <bold>Source:</bold> the authors</title>
							</caption>
							<graphic xlink:href="0012-7353-dyna-85-207-36-gt6.jpg"/>
							<table-wrap-foot>
								<fn id="TFN9">
									<p><bold>Source:</bold> the authors</p>
								</fn>
							</table-wrap-foot>
						</table-wrap>
					</p>
				</sec>
				<sec>
					<title>4.1.2. Recycling material</title>
					<p>The recycling material is the entire portion of waste that contains materials that can be reused by other people or organizations as raw materials for goods manufacturing processes, such as plastic, paper, and cardboard among others. These are separated from the total waste generated in the ITM Robledo. This type of material does not generate GHG from its transportation to landfill, since it acquires new value and so is considered a mitigating factor in GHG emissions.</p>
					<p>
						<xref ref-type="table" rid="t7">Table 7</xref> shows the CF along with the emissions not expelled due to the fact that there is no need for transportation to landfill, given that this portion of the waste is revalued and returned once again to the production cycle and thus avoids the consumption of virgin resources and energy, to manufacture the same material anew.</p>
					<p>
						<table-wrap id="t7">
							<label>Table 7</label>
							<caption>
								<title>Carbon Footprint (KgCO2 eq) and GHG emission, for the transport of ordinary waste from ITM Robledo to landfill.</title>
							</caption>
							<graphic xlink:href="0012-7353-dyna-85-207-36-gt7.jpg"/>
							<table-wrap-foot>
								<fn id="TFN10">
									<p><bold>Source:</bold> the authors.</p>
								</fn>
							</table-wrap-foot>
						</table-wrap>
					</p>
				</sec>
			</sec>
		</sec>
		<sec>
			<title>5. <bold>Total Carbon Footprint (Ton CO2eq.)</bold></title>
			<p>
				<xref ref-type="fig" rid="f10">Figs. 10</xref> and <xref ref-type="fig" rid="f11">11</xref> shows the consolidated total HC (Ton CO<sub>2</sub>eq.) per year, for the consumption of electricity and drinking water respectively.</p>
			<p>
				<fig id="f10">
					<label>Figure 10</label>
					<caption>
						<title>Carbon Footprint for Electricity (Ton CO2eq), for each year.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf10.jpg"/>
					<attrib><italic><bold>Source:</bold> the authors</italic></attrib>
				</fig>
			</p>
			<p>
				<fig id="f11">
					<label>Figure 11</label>
					<caption>
						<title>Carbon Footprint for Drinking Water (Ton CO2eq), for each year.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf11.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<xref ref-type="fig" rid="f12">Fig. 12</xref> shows in graph form the Total CF (Ton CO<sub>2</sub>eq.) associated with the transport of ordinary waste and the impact of composting organic waste and recycling activities on this indicator. </p>
			<p>
				<fig id="f12">
					<label>Figure 12</label>
					<caption>
						<title>CF (Ton CO2eq) for the TRANSPORTATION of ordinary solid waste and the mitigation activities of composting and recycling.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf12.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<xref ref-type="fig" rid="f13">Fig. 13</xref> illustrates the results obtained for the mitigation of GHGs that would be generated if all the organic waste was not degraded under anaerobic conditions in landfill, since now it is being used to produce a bio-fertilizer through composting. In addition, GHGs emitted during the compost production process are included.</p>
			<p>
				<fig id="f13">
					<label>Figure 13</label>
					<caption>
						<title>CF (Ton CO2eq) for the composting of solid organic waste and the mitigation activities from non-disposal in landfill.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf13.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<xref ref-type="fig" rid="f14">Fig. 14</xref> illustrates the ITM Robledo campus’ Carbon Footprint in Ton of CO2 eq, for the various activities and consumption of resources that are impacted by the different environmental programs and GHG mitigation practices implemented in the institution.</p>
			<p>
				<fig id="f14">
					<label>Figure 14</label>
					<caption>
						<title>Carbon Footprint in Ton of CO<sub>2</sub> eq of the ITM Robledo campus, for the different activities and consumption of resources.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf14.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>
				<xref ref-type="fig" rid="f15">Fig. 15</xref> illustrates the consolidated Carbon Footprint in Ton of CO<sub>2</sub> eq, for the years analyzed. This information demonstrates the effectiveness of the environmental programs implemented and lead by the EMS coordination team at the ITM.</p>
			<p>
				<fig id="f15">
					<label>Figure 15</label>
					<caption>
						<title>Total Carbon Footprint (Ton of CO<sub>2</sub> eq), for the ITM Robledo campus.</title>
					</caption>
					<graphic xlink:href="0012-7353-dyna-85-207-36-gf15.jpg"/>
					<attrib><bold>Source:</bold> the authors</attrib>
				</fig>
			</p>
			<p>From an analysis of <xref ref-type="fig" rid="f15">Fig. 15</xref>, the effectiveness of the environmental programs is clearly evident, since the sustainability indicator Carbon Footprint results in negative values for the years studied. This indicates a mitigation of GHG emissions, which brings the institution closer to the goal of being carbon neutral or &quot;<italic>zero emissions</italic>&quot;.</p>
		</sec>
		<sec sec-type="conclusions">
			<title>6. <bold>Conclusions</bold></title>
			<p>Electric Power and Drinking Water consumption do not show a clear trend due to decreases shown month by month between 2015 and 2016, yet for the same month between 2016 and 2017 consumption rebounds and increases. In the case of Water, an increase is evidenced year after year. This may be due to the fact that the environmental programs implemented depend on an organizational culture, so despite the efforts made by the ITM’s EMS in the dissemination of the programs and training on the ideal and sensible use of water and energy resources, it is evident that the ITM community is not totally aware of them. However, when analyzing the consolidated electricity consumption per year, a decrease of 7% between the years 2016 and 2017 is evidenced. Thus, there is a decrease in the Carbon Footprint indicator of 17.73 Ton of CO<sub>2</sub>eq for this resource. Therefore, programs for the efficient and sensible use of water and energy resources can be considered as alternatives for the mitigation of GHG emissions in any organization.</p>
			<p>By observing the analysis of the Total Carbon Footprint resulting from the GHG mitigation activities, which in this case are recycling and the composting of organic waste, it can be concluded that these two processes are high impact mitigation actions. This especially in the case of the composting of the biodegradable portion of waste generated in the ITM Robledo campus, since unnecessarily transportion of these two types of material to landfill is avoided and they are revalued, due to the fact that they are reintegrated into the production cycle; recycling as raw materials for different industries and organic waste as fertilizer, through composting. In addition, methane gas formation is avoided, it being normally produced if the organic portion is disposed of in a landfill without going through any harnessing and/or revaluation processes. For example, GHG emissions from composting are approximately 1.5% of the emissions generated when organic waste is disposed into landfill.</p>
			<p>The success of the GHG mitigation within the ITM Robledo campus, through the implementation of recycling and composting, is due to the fact that this campus has more direct control, since success depends on the training of all cafeteria and general office staff to correctly separate waste and clear guidelines for the coordination of the EMS-ITM, in terms of sanctions, follow-up activities and continuous improvement of the practices implemented. For this reason, these types of alternatives should be implemented in other organizations, given their effectiveness in mitigating GHGs, the low investment required for their implementation and the environmental awareness that is generated in the whole organizational community.</p>
		</sec>
	</body>
	<back>
		<ref-list>
			<title>References</title>
			<ref id="B1">
				<label>[1]</label>
				<mixed-citation>[1] Liu, H., Wang, X., Yang, J., Zhou, X. and Liu, Y., The ecological footprint evaluation of low carbon campuses based on life cycle assessment: A case study of Tianjin, China. J. Clean. Prod., 144, pp. 266-278, 2017. DOI: 10.1016/j.jclepro.2017.01.017</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Liu</surname>
							<given-names>H.</given-names>
						</name>
						<name>
							<surname>Wang</surname>
							<given-names>X.</given-names>
						</name>
						<name>
							<surname>Yang</surname>
							<given-names>J.</given-names>
						</name>
						<name>
							<surname>Zhou</surname>
							<given-names>X.</given-names>
						</name>
						<name>
							<surname>Liu</surname>
							<given-names>Y</given-names>
						</name>
					</person-group>
					<article-title>The ecological footprint evaluation of low carbon campuses based on life cycle assessment: A case study of Tianjin, China</article-title>
					<source>J. Clean. Prod</source>
					<volume>144</volume>
					<fpage>266</fpage>
					<lpage>278</lpage>
					<year>2017</year>
					<pub-id pub-id-type="doi">10.1016/j.jclepro.2017.01.017</pub-id>
				</element-citation>
			</ref>
			<ref id="B2">
				<label>[2]</label>
				<mixed-citation>[2] Savely, S.M., Carson, A.I. and Delclos, G.L., An environmental management system implementation model for US colleges and universities. J. Clean. Prod., 15, pp. 660-670, 2007. DOI: 10.1016/j.jclepro.2006.01.013</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Savely</surname>
							<given-names>S.M.</given-names>
						</name>
						<name>
							<surname>Carson</surname>
							<given-names>A.I.</given-names>
						</name>
						<name>
							<surname>Delclos</surname>
							<given-names>G.L</given-names>
						</name>
					</person-group>
					<article-title>An environmental management system implementation model for US colleges and universities</article-title>
					<source>J. Clean. Prod</source>
					<volume>15</volume>
					<fpage>660</fpage>
					<lpage>670</lpage>
					<year>2007</year>
					<pub-id pub-id-type="doi">10.1016/j.jclepro.2006.01.013</pub-id>
				</element-citation>
			</ref>
			<ref id="B3">
				<label>[3]</label>
				<mixed-citation>[3] Robinson, O.J., Tewkesbury, A., Kemp, S. and Williams, I.D., Towards a universal carbon footprint standard: A case study of carbon management at universities. J. Clean. Prod., 2017. DOI: 10.1016/j.jclepro.2017.02.147</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Robinson</surname>
							<given-names>O.J.</given-names>
						</name>
						<name>
							<surname>Tewkesbury</surname>
							<given-names>A.</given-names>
						</name>
						<name>
							<surname>Kemp</surname>
							<given-names>S.</given-names>
						</name>
						<name>
							<surname>Williams</surname>
							<given-names>I.D</given-names>
						</name>
					</person-group>
					<article-title>Towards a universal carbon footprint standard: A case study of carbon management at universities</article-title>
					<source>J. Clean. Prod</source>
					<year>2017</year>
					<pub-id pub-id-type="doi">10.1016/j.jclepro.2017.02.147</pub-id>
				</element-citation>
			</ref>
			<ref id="B4">
				<label>[4]</label>
				<mixed-citation>[4] Pandey, D., Agrawal, M. and Pandey, J.S., Carbon footprint: Current methods of estimation. Environ. Monit. Assess., 178(1-4), pp. 135-160, 2011. DOI: 10.1007/s10661-010-1678-y</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Pandey</surname>
							<given-names>D.</given-names>
						</name>
						<name>
							<surname>Agrawal</surname>
							<given-names>M.</given-names>
						</name>
						<name>
							<surname>Pandey</surname>
							<given-names>J.S</given-names>
						</name>
					</person-group>
					<article-title>Carbon footprint: Current methods of estimation</article-title>
					<source>Environ. Monit. Assess</source>
					<volume>178</volume>
					<issue>1-4</issue>
					<fpage>135</fpage>
					<lpage>160</lpage>
					<year>2011</year>
					<pub-id pub-id-type="doi">10.1007/s10661-010-1678-y</pub-id>
				</element-citation>
			</ref>
			<ref id="B5">
				<label>[5]</label>
				<mixed-citation>[5] Gómez, N., Angeles, M. and Monsalve, F., Carbon footprint of a university in a multiregional model: the case of the University of Castilla-La Mancha. J. Clean. Prod., 138, pp. 119-130, 2016. DOI: 10.1016/j.jclepro.2016.06.009 </mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Gómez</surname>
							<given-names>N.</given-names>
						</name>
						<name>
							<surname>Angeles</surname>
							<given-names>M.</given-names>
						</name>
						<name>
							<surname>Monsalve</surname>
							<given-names>F</given-names>
						</name>
					</person-group>
					<article-title>Carbon footprint of a university in a multiregional model: the case of the University of Castilla-La Mancha</article-title>
					<source>J. Clean. Prod</source>
					<volume>138</volume>
					<fpage>119</fpage>
					<lpage>130</lpage>
					<year>2016</year>
					<pub-id pub-id-type="doi">10.1016/j.jclepro.2016.06.009</pub-id>
				</element-citation>
			</ref>
			<ref id="B6">
				<label>[6]</label>
				<mixed-citation>[6] ICONTEC, GTC-ISO-TR 14049: gestión ambiental. evaluación del ciclo de vida. ejemplos de aplicación de la ISO 14041 para la definición del objetivo y el alcance y para el análisis del inventario. Bogotá, 2015. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<collab>ICONTEC</collab>
					</person-group>
					<source>GTC-ISO-TR 14049: gestión ambiental. evaluación del ciclo de vida. ejemplos de aplicación de la ISO 14041 para la definición del objetivo y el alcance y para el análisis del inventario</source>
					<publisher-loc>Bogotá</publisher-loc>
					<year>2015</year>
				</element-citation>
			</ref>
			<ref id="B7">
				<label>[7]</label>
				<mixed-citation>[7] ICONTEC, NTC-ISO 14044. gestión ambiental. análisis de ciclo de vida. Requisitos y directrices. Requisitos del ciclo de vida. 2007. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<collab>ICONTEC</collab>
					</person-group>
					<source>NTC-ISO 14044. gestión ambiental. análisis de ciclo de vida. Requisitos y directrices. Requisitos del ciclo de vida</source>
					<year>2007</year>
				</element-citation>
			</ref>
			<ref id="B8">
				<label>[8]</label>
				<mixed-citation>[8] ICONTEC, NTC-ISO 14064-1: gases de efecto invernadero. parte 1: especificación con orientación, a nivel de las organizaciones, para la cuantificación y el informe de las emisiones y remociones de gases de efecto invernadero. Norma Técnica Colomb., 2006, 23 P. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<collab>ICONTEC</collab>
					</person-group>
					<source>NTC-ISO 14064-1: gases de efecto invernadero. parte 1: especificación con orientación, a nivel de las organizaciones, para la cuantificación y el informe de las emisiones y remociones de gases de efecto invernadero</source>
					<publisher-name>Norma Técnica Colomb</publisher-name>
					<year>2006</year>
					<fpage>23</fpage>
					<lpage>23</lpage>
				</element-citation>
			</ref>
			<ref id="B9">
				<label>[9]</label>
				<mixed-citation>[9] Ertug-Ercin, A. and Hoekstra, Y., Carbon and Water Footprints. Concepts, Methodol. Policy Responses, United Nations Educational, Scientific and Cultural Organization, pp. 1-24, 2012. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<name>
							<surname>Ertug-Ercin</surname>
							<given-names>A.</given-names>
						</name>
						<name>
							<surname>Hoekstra</surname>
							<given-names>Y</given-names>
						</name>
					</person-group>
					<source>Carbon and Water Footprints. Concepts, Methodol. Policy Responses</source>
					<publisher-name>United Nations Educational, Scientific and Cultural Organization</publisher-name>
					<fpage>1</fpage>
					<lpage>24</lpage>
					<year>2012</year>
				</element-citation>
			</ref>
			<ref id="B10">
				<label>[10]</label>
				<mixed-citation>[10] Myhre, G. et al., Anthropogenic and natural radiative forcing. In: Climate change 2013: The physical science basis. Contribution of working group i to the fifth assessment report of the Intergovernmental Panel on Climate Change, pp. 659-740, 2013. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<name>
							<surname>Myhre</surname>
							<given-names>G.</given-names>
						</name>
						<etal/>
					</person-group>
					<chapter-title>Anthropogenic and natural radiative forcing</chapter-title>
					<source>Climate change 2013: The physical science basis. Contribution of working group i to the fifth assessment report of the Intergovernmental Panel on Climate Change</source>
					<fpage>659</fpage>
					<lpage>740</lpage>
					<year>2013</year>
				</element-citation>
			</ref>
			<ref id="B11">
				<label>[11]</label>
				<mixed-citation>[11] Sánchez, A. et al., Greenhouse gas emissions from organic waste composting. Environ. Chem. Lett., 13(3), pp. 223-238, 2015. DOI: 10.1007/s10311-015-0507-5</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Sánchez</surname>
							<given-names>A.</given-names>
						</name>
						<etal/>
					</person-group>
					<article-title>Greenhouse gas emissions from organic waste composting</article-title>
					<source>Environ. Chem. Lett</source>
					<volume>13</volume>
					<issue>3</issue>
					<fpage>223</fpage>
					<lpage>238</lpage>
					<year>2015</year>
					<pub-id pub-id-type="doi">10.1007/s10311-015-0507-5</pub-id>
				</element-citation>
			</ref>
			<ref id="B12">
				<label>[12]</label>
				<mixed-citation>[12] World Business Council for Sustainable Development (WBCSD) and World Resources Institute (WRI), Greenhouse gas protocol corporate value chain (Scope 3) accounting and reporting standard. World Resour. Inst. World Bus. Counc., pp. 1-152, 2011. </mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<collab>World Business Council for Sustainable Development (WBCSD)</collab>
						<collab>World Resources Institute (WRI)</collab>
					</person-group>
					<source>Greenhouse gas protocol corporate value chain (Scope 3) accounting and reporting standard. World Resour</source>
					<publisher-name>Inst. World Bus. Counc</publisher-name>
					<fpage>1</fpage>
					<lpage>152</lpage>
					<year>2011</year>
				</element-citation>
			</ref>
			<ref id="B13">
				<label>[13]</label>
				<mixed-citation>[13] Sánchez, A. et al., Greenhouse gas from organic waste composting: emissions and measurement. In: CO2 sequestration, biofuels and depollution, environmental chemistry for a sustainable world, 5, pp. 33-43, Switzerland: Springer International Publishing, 2015. DOI: 10.1007/978-3-319-11906-9</mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<name>
							<surname>Sánchez</surname>
							<given-names>A.</given-names>
						</name>
						<etal/>
					</person-group>
					<chapter-title>Greenhouse gas from organic waste composting: emissions and measurement</chapter-title>
					<source>CO2 sequestration, biofuels and depollution, environmental chemistry for a sustainable world</source>
					<volume>5</volume>
					<fpage>33</fpage>
					<lpage>43</lpage>
					<publisher-loc>Switzerland</publisher-loc>
					<publisher-name>Springer International Publishing</publisher-name>
					<year>2015</year>
					<pub-id pub-id-type="doi">10.1007/978-3-319-11906-9</pub-id>
				</element-citation>
			</ref>
			<ref id="B14">
				<label>[14]</label>
				<mixed-citation>[14] Shen, L., Worrell, E. and Patel, M.K., Open-loop recycling: A LCA case study of PET bottle-to-fibre recycling. Resour. Conserv. Recycl., 55(1), pp. 34-52, 2010. DOI: 10.1016/j.resconrec.2010.06.014</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Shen</surname>
							<given-names>L.</given-names>
						</name>
						<name>
							<surname>Worrell</surname>
							<given-names>E.</given-names>
						</name>
						<name>
							<surname>Patel</surname>
							<given-names>M.K</given-names>
						</name>
					</person-group>
					<article-title>Open-loop recycling: A LCA case study of PET bottle-to-fibre recycling</article-title>
					<source>Resour. Conserv. Recycl</source>
					<volume>55</volume>
					<issue>1</issue>
					<fpage>34</fpage>
					<lpage>52</lpage>
					<year>2010</year>
					<pub-id pub-id-type="doi">10.1016/j.resconrec.2010.06.014</pub-id>
				</element-citation>
			</ref>
			<ref id="B15">
				<label>[15]</label>
				<mixed-citation>[15] Turner, D.A., Williams, I.D. and Kemp, S., Greenhouse gas emission factors for recycling of source-segregated waste materials. Resour. Conserv. Recycl., 105, pp. 186-197, 2015. DOI: 10.1016/j.resconrec.2015.10.026</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Turner</surname>
							<given-names>D.A.</given-names>
						</name>
						<name>
							<surname>Williams</surname>
							<given-names>I.D.</given-names>
						</name>
						<name>
							<surname>Kemp</surname>
							<given-names>S</given-names>
						</name>
					</person-group>
					<article-title>Greenhouse gas emission factors for recycling of source-segregated waste materials</article-title>
					<source>Resour. Conserv. Recycl</source>
					<volume>105</volume>
					<fpage>186</fpage>
					<lpage>197</lpage>
					<year>2015</year>
					<pub-id pub-id-type="doi">10.1016/j.resconrec.2015.10.026</pub-id>
				</element-citation>
			</ref>
			<ref id="B16">
				<label>[16]</label>
				<mixed-citation>[16] UPME, La calculadora FECOC 2016 [En línea]. [fecha de referencia: 17 de Marzo de 2017]. Disponible en: <comment>Disponible en: <ext-link ext-link-type="uri" xlink:href="http://www.upme.gov.co/calculadora_emisiones/aplicacion/calculadora.html">http://www.upme.gov.co/calculadora_emisiones/aplicacion/calculadora.html</ext-link>
					</comment>. </mixed-citation>
				<element-citation publication-type="webpage">
					<person-group person-group-type="author">
						<collab>UPME</collab>
					</person-group>
					<source>La calculadora FECOC 2016</source>
					<comment>En línea</comment>
					<date-in-citation content-type="access-date" iso-8601-date="2017-00-00">17 de Marzo de 2017</date-in-citation>
					<comment>Disponible en: <ext-link ext-link-type="uri" xlink:href="http://www.upme.gov.co/calculadora_emisiones/aplicacion/calculadora.html">http://www.upme.gov.co/calculadora_emisiones/aplicacion/calculadora.html</ext-link>
					</comment>
				</element-citation>
			</ref>
			<ref id="B17">
				<label>[17]</label>
				<mixed-citation>[17] Kyung, D., Kim, D., Park, N. and Lee, W., Estimation of CO2 emission from water treatment plant - Model development and application. J. Environ. Manage., 131, pp. 74-81, 2013. DOI: 10.1016/j.jenvman.2013.09.019</mixed-citation>
				<element-citation publication-type="journal">
					<person-group person-group-type="author">
						<name>
							<surname>Kyung</surname>
							<given-names>D.</given-names>
						</name>
						<name>
							<surname>Kim</surname>
							<given-names>D.</given-names>
						</name>
						<name>
							<surname>Park</surname>
							<given-names>N.</given-names>
						</name>
						<name>
							<surname>Lee</surname>
							<given-names>W</given-names>
						</name>
					</person-group>
					<article-title>Estimation of CO2 emission from water treatment plant - Model development and application</article-title>
					<source>J. Environ. Manage</source>
					<volume>131</volume>
					<fpage>74</fpage>
					<lpage>81</lpage>
					<year>2013</year>
					<pub-id pub-id-type="doi">10.1016/j.jenvman.2013.09.019</pub-id>
				</element-citation>
			</ref>
			<ref id="B18">
				<label>[18]</label>
				<mixed-citation>[18] Sharp, S., Greenhouse gas emissions from landfill waste and compost - the carbon roadshow. Carbon Accounting &amp; Calculators. The University of Texas at Austin [Online]. 2016. [date of reference: 24th of October of 2017]. Available at: <comment>Available at: <ext-link ext-link-type="uri" xlink:href="https://sites.utexas.edu/carbonroadshow/2016/03/30/greenhouse-gas-emissions-from-landfill-waste-and-compost/">https://sites.utexas.edu/carbonroadshow/2016/03/30/greenhouse-gas-emissions-from-landfill-waste-and-compost/</ext-link>
					</comment>
				</mixed-citation>
				<element-citation publication-type="book">
					<person-group person-group-type="author">
						<name>
							<surname>Sharp</surname>
							<given-names>S</given-names>
						</name>
					</person-group>
					<source>Greenhouse gas emissions from landfill waste and compost - the carbon roadshow. Carbon Accounting &amp; Calculators</source>
					<publisher-name>The University of Texas at Austin</publisher-name>
					<year>2016</year>
					<date-in-citation content-type="access-date" iso-8601-date="2017-00-00">24th of October of 2017</date-in-citation>
					<comment>Available at: <ext-link ext-link-type="uri" xlink:href="https://sites.utexas.edu/carbonroadshow/2016/03/30/greenhouse-gas-emissions-from-landfill-waste-and-compost/">https://sites.utexas.edu/carbonroadshow/2016/03/30/greenhouse-gas-emissions-from-landfill-waste-and-compost/</ext-link>
					</comment>
				</element-citation>
			</ref>
		</ref-list>
		<fn-group>
			<fn fn-type="other" id="fn1">
				<label>1</label>
				<p> Adapted from: <ext-link ext-link-type="uri" xlink:href="http://www.itm.edu.co/dependencias/sistema-de-gestion-ambiental/programas-ambientales-del-sga/">http://www.itm.edu.co/dependencias/sistema-de-gestion-ambiental/programas-ambientales-del-sga/</ext-link>
				</p>
			</fn>
			<fn fn-type="other" id="fn2">
				<label>2</label>
				<p>
					<ext-link ext-link-type="uri" xlink:href="https://www.tgi.com.co/noticias/sala-de-prensa2/comunicados-de-prensa/con-prueba-de-camion-bogota-avanza-en-el-uso-de-combustibles-limpios-para-la-recoleccion-de-residuos">https://www.tgi.com.co/noticias/sala-de-prensa2/comunicados-de-prensa/con-prueba-de-camion-bogota-avanza-en-el-uso-de-combustibles-limpios-para-la-recoleccion-de-residuos</ext-link>
				</p>
			</fn>
		</fn-group>
		<fn-group>
			<fn fn-type="other" id="fn3">
				<label>How to cite:</label>
				<p> Aristizábal-Alzate, C.E. and González-Manosalva J.L., Effectiveness analysis of the ITM environmental programs: saving and efficient use of electric energy and water, and comprehensive solid waste management. A case study. DYNA, 85(207), pp. 36-43, Octubre - Diciembre, 2018.</p>
			</fn>
		</fn-group>
		<fn-group>
			<fn fn-type="other" id="fn4">
				<label>C.E. Aristizábal-Alzate,</label>
				<p> received the BSc. of Chemical Engineer in 2012 from the Universidad Nacional de Colombia, Medellín campus. Additionally, in 2016, he began studying for a MSc. Degree in Industrial Energy Management at the Metropolitan Technological Institute of Medellín (ITM). From 2012 until January 2016, he worked as an advisor for small enterprises in the chemical and agroindustrial sector. Furthermore, over the last year he has worked as a researcher, lecturer and contractor at the ITM environmental management system ORCID: 0000-0002-8970-6389 </p>
			</fn>
			<fn fn-type="other" id="fn5">
				<label>J.L. González-Manosalva,</label>
				<p> received a BSc. Eng in Civil Engineering and Bs. Eng Sanitary Engineering in 1996, a Sp degree in Environmental Management in 1998, and a MSc degree in Environment and Development in 2019. He has worked in environmental programs and projects with emphasis on environmental management and since 1998 for the Universidad Nacional de Colombia in the publication of scientific journals. He is currently coordinator of the Department of Environmental Sciences and Construction, Faculty of Exact and Applied Sciences at the Instituto Tecnológico Metropolitano, Medellín, Colombia. ORCID: 0000-0002-0625-3362</p>
			</fn>
		</fn-group>
	</back>
</article>