최근의 국제사회는 경제성장에 따른 기상이변의 방지를 위한 국가 간 기후변화협력 체결(1992년)을 시작으로 환경 오염물질 배출 저감을 요구하고 있다(Moon et al, 2014). 따라서 최근에는 전 세계적으로 지구온난화와 기후변화의 원인이 되는 온실가스의 발생을 줄 이고자 노력하고 있으며, 건설 산업은 이러한 온실가스 배출량의 주요 원인으로 인식되고 있다(Kong et al., 2016) 교량 건설사업이 환 경에 미치는 정도를 전과정평가(Life Cycle Assessment, LCA)방법을 활용하여 재료 및 공법의 지속가능성에 대한 객관적, 정량적 평가 체계를 구축하고자한다. 본 연구에서는 선행적으로 국내외 환경성적표지제도(Environment Product Declaration, EPD), 탄소발자국(Carbon footprint) 등을 분석함으로써, LCA 관련 제도에 대한 전반적인 동향을 파악하였다. 그다음, 국제적으로 통용되고 있는 제품 범주 규칙 (PCR)과 환경제품선언(EPD) 사례를 분석하여 LCA 관련 분석 범위를 확인했으며, 전과정영향평가(LCIA) 방법론과 국내외 LCI DB(Ecoinvent, Athena Pavement LCA, LCA PAVE 등)을 분석함으로써 국내외 환경 영향인자 관련 기술자료를 확보하였다. 또한, 건설 자재, 시공, 유지 관리 관련 설계 명세서, 표준품셈, 단가 산출표를 분석함으로써, 자재 투입량, 장비 연료 소모량에 대한 기초 DB를 도출하였다. 기존 프로그램을 토대로 고속도로 온실가스 산정 프로그램을 개발하여 건설자재, 수송, 시공, 유지 관리 단계에서의 탄소 배출량 산정 사례 분석을 수행했다. 교량 분야는 STEEL BOX교를 선정했다. 이에대하여 건설자재. 시공, 수송, 유지관리에 탄소배출량 을 산정하였다. 산정된 결과를 바탕으로 LCA분석의 기틀을 마련하였으며, 이를 통하여 추후 추가적인 기초 DB를 추가하여 교량 분야 전과정평가 LCA를 분석하기 위한 플랫폼을 제작할 예정이다.

산업화에 따른 이산화탄소 등 온실가스 발생량의 증가는 지구 온난화 현상을 가속화 하였다. 이러한 현상은 지난 수 세기동안 지속 되어왔으며 최근 우리 인간 삶에 지대한 영향을 미치고 있다. 이러한 위험에 따라 주요 선진국들은 에너지 감축 및 온실가스 배출량 제한에 대하여 매우 적극적인 입장을 취하고 있다. 유럽연합(EU)은 온실가스 배출 절감을 위해 시행 중인 ‘탄소배출권 거래제(Emission Traiding System)’ 개혁안에 대하여 합의하여 2050년까지 인위적 생성되는 탄소 배출량을 자연적으로 흡수되는 양과 동일하게 하는 ‘탄 소중립’을 목표로 제시하였다. 국내에선 환경영향평가의 대상이 되는 계획 및 개발사업에 도로건설이 포함되는 ‘탄소중립기본법 시행 령’이 지난 3월 의결되어 시행되었다. 이렇듯, 국내외에선 이러한 탄소저감 제도 구축에 노력을 기울이고 있다. 국내에선 도로건설이 환경영향평가의 대상으로 설정되었으나 2011년 국토교통부에서 배포한 시설물별 탄소배출량 산정 가이드라인 외의 구체적인 생애주기 분석 방법이 부재한 상황이다. 따라서 본 연구에서 국제 표준 ISO 14040의 전과정평가 LCA(Life Cycle Assessment) 방법과 2011년 국 토교통부의 시설물별 탄소배출량 산정 가이드라인을 따라 국내 LCI DB(Life Cycle Inventory Data Base)를 활용한 도로 분야의 전과정 탄소 배출량을 산정하였다. 이후 장비 연료 소모량과 자재 사용에 대한 국내외 LCI DB를 추가하여 도로 건설 전 과정에 대한 LCA 분석 플랫폼을 제작할 예정이다.

PURPOSES : In this study, emissions from asphalt mixture production and construction processes are calculated and used to estimate the emission from each asphalt pavement layer. The calculated emissions for the processes are used as fundamental data to estimate the total emission from the entire life cycle of pavement engineering in South Korea. METHODS : A design proposal and the Korean standard, which provide quantitative information for activities, were used to estimate the amount of construction materials and energy consumption. Subsequently, the LCI DB from NAPA and the LCIA DB from EPA were utilized in conjunction with the estimated quantity to assess the effect of the emissions to determine their environmental impact categories. RESULTS : Calculation results show that 5.84 million ton of CO2eq is discharged from production and construction processes, whereas 3.24 million ton of CO2eq is discharged from operation processes in the pavement engineering sector. The total GHG emission, i.e., 9.08 million ton of CO2eq, is approximately 1.25% of the national GHG emission in 2018. The asphalt mixture production process results in the highest GHG emission in the life cycle of asphalt pavements. CONCLUSIONS : An LCI DB that accounts for the industrial characteristics of South Korea must be established to provide more reliable emission data to be used for national GHG reduction plans, including those for the pavement engineering sector.

PURPOSES : This study aimed to provide a method for linking VE/LCC/LCA and BIM and to develop a system for BIM-based VE/LCC/ LCA evaluation. METHODS : Based on literature reviews and case studies, we propose bridge hierarchies for sharing and integrating VE/LCC/LCA and BIM information and standard unit price and equipment workloads for LCC and LCA analysis. We further developed a BIM library to visualize various ideas and alternatives. RESULTS : The results of the proposed system demonstrate that the VE can be systemized and the original draft and alternatives can be visually provided via the BIM library. In addition, the LCC cost can be calculated by the automatic volume calculation of the bridge BIM library and the LCA can be calculated using the materials and equipment (these are BIM attribute information). CONCLUSIONS : The developed method can be more reliable and productive of VE, LCC, and LCA work owing to the partial automation and visualization of the developed system.

The concern on the greenhouse gas emissions is increasing globally. Especially, the greenhouse gas emission from fisheries is an important issue due to Cancun Agreements Mexico in 1992 and the Kyoto protocol in 2005. Furthermore, the Korean government has a plan to reduce the GHG emissions as 5.2% compared to the BAU in fisheries until 2020. However, the investigation on the GHG emissions from Korean fisheries has not been executed much. Therefore, the quantitative analysis of GHG emissions from Korean fishery industry is needed as the first step to find a relevant way to reduce GHG emissions from fisheries. The purpose of this research is to investigate which degree of GHG emitted from the major coastal fisheries such as coastal gillnet fishery, coastal dual purpose fishery, coastal pots fishery and coastal small scale stow net fishery. Here, we calculated the GHG emission from the fisheries using the LCA (Life Cycle Assessment) method. The system boundary and input parameters for each process level are defined for LCA analysis. The fuel use coefficients of the fisheries are also calculated according to the fuel type. The GHG emissions from sea activities by the fisheries will be dealt with. Furthermore, the GHG emissions for the unit weight of fishes are also calculated with consideration to the different consuming areas. The results will be helpful to understand the circumstances of GHG emissions from Korean fisheries.

The negative factors of fishery in environmental aspect of view are Greenhouse gas emission problems by high usage of fossil fuel, destruction of underwater ecosystem by bottom trawls, reduction of resources by fishing and damage of ecosystem diversity. Especially, the Greenhouse gas emission from fisheries is an important issue due to Cancún meeting, Mexico in 1992 and Kyoto protocol in 2005. However, the investigation on the GHG emissions from Korean fisheries did not much carry out. Therefore, the quantitative analysis of GHG emissions from Korean fishery industry is needed as a first step to find a relevant way to reduce GHG emissions from fisheries. The purpose of this research is to investigate which degree of GHG emitted from fishery. Here, we calculated the GHG emission from Korean bottom pair trawl fishery using the LCA (Life Cycle Assessment) method. The system boundary and input parameters for each process level are defined for LCA analysis. The fuel use coefficient of the fishery is also calculated. The GHG emissions from the representative fishes caught by bottom pair trawl will be dealt with. Furthermore, the GHG emissions for the edible weight of fishes are calculated with consideration to the different consuming areas and slaughtering process also. The results will be helpful to understand the circumstances of GHG emissions from Korean fisheries.

The global warming related to GHG (greenhouse gases) emissions from industries is a major issue globally. Furthermore, GHG emissions from the fishery industries also represent an important issue, as indicated by "The Code of Conduct for Responsible Fisheries" at the Cancun, Mexico, meeting in 1992 and by the Kyoto protocol in 2005. Korea pronounced itself to be a voluntary exclusion management country at the 16th IPCC at Cancun, Mexico, in 2010. However, few analyses of GHG emissions from Korean fisheries have been performed. Therefore, a quantitative analysis of GHG emissions from the major Korean fisheries is needed before guidelines for reducing GHG emissions from the fishing industry can be established. The aim of this study was to assess the present GHG emissions from the Korean Purse seine fishery using the LCA (life cycle assessment) method. The system boundary and allocation method were defined for the LCA analysis. The fuel consumption factor of the purse seine fishery was also calculated. The GHG emissions for the edible fish were evaluated by determining the weights of whole fish and gutted fish. Finally, the GHG emissions required to produce 1kg of whole fish and 1kg of edible fish were deduced. The results will help determine the GHG emissions from the fishery. They will also be helpful to stakeholders and the government in understanding the circumstances involved in GHG emissions from the fishing industry.

본 연구는 통계청(2009-2010)의 국가 산업 표준을 기본으로 생애주기를 고려한다. 생애주기에 대한 변수는 경제활동인구와 사업체 동향을 분석하여 실시하며 이에 따른 자격은 산업과 직업에 관련하여 해당하는 자격의 매칭 테이블을 기준으로 그 자격의 가치를 평가하는 방법을 선택하였다. 산업에 대한 분석은 일반적으로 활용되고 있는 경영기법에 따라 그 절차를 수용하고 관련변수를 응용 또는 적용하도록 하였다.

It is crucial that the manufacturing companies should consider reducing environmental impacts of the products in the early design phases. Life Cycle Assessment method is one of the most widely used and important tools for assessing the overall environmental impacts of products across the entire lifecycle. Based on the Life Cycle Assessment method, we provide a systematic guideline for eco-product design. The proposed guideline is primarily aimed at product developers or engineers, as a insight to the integration of environmental thinking into the early design phase, and therefore into products. This guideline has several steps: select the target product, describe the product structure, quantify the environmental impacts, identify meaningful underlying environmental impacts, and develop an environmental strategy. The usefulness of proposed guideline is also demonstrated through the application to an actual vacuum cleaner.

A life cycle assessment(LCA) is increasing its applicability as a powerful tool for an environmental burdens analysis. In this study, some cases are compared in terms of analysis procedures and results obtained with LCAs for evaluating power generation technologies in Korea. For the comparison, 3 power generation technologies are selected because they produces almost 90% of 2003 total electricity generation in Korea. It is shown that the range of evaluation values amounts to maximally the order of about 105, which is rather large discrepancy than the level of 101 in comparison with foreign studies. The difference seems to be due to the simplicity of modeling used in each case study. It is proposed that this large discrepancy should be obviously clarified to improve their reliability in that electricity is a essentialness for all industries and the capacity of LCA of national-level electricity affects the results of LCA for the other sectors.

As environmental damage increase by a highly developed material civilization of today, many companies take a growing immensely interest in the influence of environment for beginning a new paradigm year by year. The previous assessments dose not run the gamut of industry but is confined within a certain facility or an area. Industrial processes and operations can not be accomplished independently but are connected with each others through suppliers and customer, and these ideas are fundamental notions of Life Cycle Assessment(LCA). This paper will introduce Life Cycle Assessment(LCA) in environment which is rising, and would like to build environmental management system using approach of Quality Function Deployment(QFD) and Safety Function Deployment(SFD) belonging to the assessment method.

Industrial processes and operations can not be accomplished independently but are connected with each others through suppliers and customer, and these ideas are fundamental notions of Life Cycle Assessment(LCA). This paper will introduce Life Cycle Assessment(LCA) in environment which is rising, and would like to build environmental management system using approach of Quality Function Deployment(QFD) and Safety Function Deployment(SFD) belonging to the assessment method.

In this paper, the life cycle assessment(LCA) methodology is applied to Personal Computer's basic materials in order to analyze the impact to the environment. LCA data collection is carried out taking into account on main materials of PC's parts and compo

As environmental damage increase by a highly developed material civilization of today, many companies take a growing immensely interest in the influence of environment for beginning a new paradigm year by year. The previous assessments dose not run the gamut of industry but is confined within a certain facility or an area. Industrial processes and operations can not be accomplished independently but are connected with each others through suppliers and customer, and these ideas are fundamental notions of Life Cycle Assessment(LCA). This paper will introduce Life Cycle Assessment(LCA) n environment which is rising, and would like to build environmental management system using approach of Quality Function Development(QFD) and Safety Function Development(SFD) belonging to the assessment method.

As environmental damage increase by a highly developed material civilization of today, many companies take a growing immensely interest in the influence of environment for beginning a new paradigm year by year. The previous assessments dose not run the gamut of industry but is confined within a certain facility or an area. Industrial processes and operations can not be accomplished independently but are connected with each others through suppliers and customer, and these ideas are fundamental notions of Life Cycle Assessment(LCA). This paper will introduce Life Cycle Assessment(LCA) in environment which is rising, and would like to build environmental management system using approach of Quality Function Development(QFD) and Safety Function Development(SFD) belonging to the assessment method.

In this paper, the life cycle assessment(LCA) methodology is applied to Personal Computer in materials processing stage in order to analyze the impact to the environment. LCA data collection is carried out taking into account on main materials of PC in materials processing stage. And the impact assessment is the environmental burdens on three factor in air emission(CO2, SOx, NOx), five factor in water emission(BOD, COD, SS, N, P), and three factor in transported substance(cl, NH4, SO4). According to the result, the loading in the materials processing stage of PC proved to be used total energy 6,285Mj and emitted CO2 259.8kg, SOx 3,571g, NOx 330g, COD 1,328g, P 246g, N 2,434g.