2013
DOI: 10.1007/s11367-013-0635-8
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Evaluation of water services system through LCA. A case study for Iasi City, Romania

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Cited by 60 publications
(27 citation statements)
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“…Here, the selection of alternatives in each example (PV, eGrid, concrete, and paper pulp) is determined by single impact category. A survey of recent publications from the International Journal of Life Cycle Assessment reporting normalized impacts from CML supports the finding that marine aquatic ecotoxicity is the most influential category in evaluations of water services (Barjoveanu et al 2014), diapers (Mirabella et al 2013), exterior household walls (Monteiro and Freire 2012), packing tape (Navajas et al 2014), thermal insulation (Struhala et al 2014), and an entire inventory data library (White and Carty 2010). These results were also reproduced by Sim et al (2007) in a food sourcing application where authors excluded marine aquatic ecotoxicity from normalized results due to masking of other aspects.…”
Section: Resultsmentioning
confidence: 57%
“…Here, the selection of alternatives in each example (PV, eGrid, concrete, and paper pulp) is determined by single impact category. A survey of recent publications from the International Journal of Life Cycle Assessment reporting normalized impacts from CML supports the finding that marine aquatic ecotoxicity is the most influential category in evaluations of water services (Barjoveanu et al 2014), diapers (Mirabella et al 2013), exterior household walls (Monteiro and Freire 2012), packing tape (Navajas et al 2014), thermal insulation (Struhala et al 2014), and an entire inventory data library (White and Carty 2010). These results were also reproduced by Sim et al (2007) in a food sourcing application where authors excluded marine aquatic ecotoxicity from normalized results due to masking of other aspects.…”
Section: Resultsmentioning
confidence: 57%
“…As the main driver of the carbon footprint increase in the urban water cycle is related to energy efficiency, this variability may depend on several aspects of the energy consumption (such as high level of leakages, the need for significant water treatment, and inefficient plants and pumping stations); in addition, the energy mix adopted at the national level (including sources such as coal, nuclear fission, natural gas, or renewable sources) may produce a different environmental impact of supplied energy. For example, in Barjoveanu et al [11], the results have pointed out that the higher impacts are mainly due to the energetic effort needed for water supply abstraction and the fairly high water losses in the distribution system; for Jeong et al [16], the electricity consumption is mainly due to water transport and treatment. In this case study, rather than water treatment, the greater energy consumption is to be attributed to the pumping stations and to the significant water volumes that need to be pumped to compensate for water losses.…”
Section: Results From the Current Scenariomentioning
confidence: 99%
“…The system boundaries are defined in accordance with the PCR-UN CPC code 6921 [11] of the International EPD System (Environmental Product Declaration) and are represented in the Figure 1. In the present study, the system boundaries include the following processes:…”
Section: Inventory Analysismentioning
confidence: 99%
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“…Life cycle assessment (LCA) is known as an effective method for evaluating various environmental impacts and has been widely applied to WWTPs [9][10][11][12][13][14]. Although a number of LCA methodologies have been developed recently [15][16][17], none have addressed the ecotoxicity of NH 3 -N. Corominas et al [18] reported that decision-making in controlling wastewater nutrient removal systems was assessed using a combination of mechanistic process models using life cycle impact assessment models.…”
Section: Introductionmentioning
confidence: 99%