12 research outputs found

    The carbon footprint associated with water management policy options in the Las Vegas Valley, Nevada

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    A system dynamics model was developed to estimate the carbon dioxide (CO2) emissions associated with conveyance of water from the water source to the distribution laterals of the Las Vegas Valley. In addition, the impact of several water management policies, including water conservation, reuse, and population growth rate change was evaluated. The results show that, at present, nearly 0.53 million metric tons of CO2 emissions per year are released due to energy use for water conveyance in distribution laterals of the Valley from Lake Mead, located 32.2 km (20 miles) southeast of the Las Vegas at an elevation of nearly 366 m (1200 ft) below the Valley. The results show that the reduction in per capita water demand to 753 lpcd by 2035 can lower the CO2 emissions by approximately 16.5%. The increase in reuse of treated wastewater effluent within the valley to 77 million cubic meters by 2020 results in the decrease of CO2 emissions by 3.6%. Similarly, change in population growth rate by Β±0.5% can result in CO2 emissions reduction of nearly 12.8% by 2035 when compared to the current status

    Modeling structural change in spatial system dynamics: A Daisyworld example

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    System dynamics (SD) is an effective approach for helping reveal the temporal behavior of complex systems. Although there have been recent developments in expanding SD to include systems' spatial dependencies, most applications have been restricted to the simulation of diffusion processes; this is especially true for models on structural change (e.g. LULC modeling). To address this shortcoming, a Python program is proposed to tightly couple SD software to a Geographic Information System (GIS). The approach provides the required capacities for handling bidirectional and synchronized interactions of operations between SD and GIS. In order to illustrate the concept and the techniques proposed for simulating structural changes, a fictitious environment called Daisyworld has been recreated in a spatial system dynamics (SSD) environment. The comparison of spatial and non-spatial simulations emphasizes the importance of considering spatio-temporal feedbacks. Finally, practical applications of structural change models in agriculture and disaster management are proposed

    System Dynamical Simulation of Risk Perception for Enterprise Decision-Maker in Communication of Chemical Incident Risks

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    PresentationSystem Dynamical Simulation of Risk Perception for Enterprise Decision-Maker in Communication of Chemical Incident Risk

    An integrated dynamical modeling perspective for infrastructure resilience

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    International audienceThis paper considers a dynamical way to connect resilience outcomes and processes by nesting process-based approaches inside a controlled dynamical system under resource constraints. To illustrate this, we use a dynamical model of electric power generation to show the complementary aspects of outcome, resources, and process-based approaches for analyzing infrastructure resilience. The results of this stylized model show that adaptation is the most influential process and that for monitoring to be efficient it must account for associated costs. Beyond these specific results, we suggest that nesting outcome- and process-based approaches within a dynamical controlled framework can be very useful and complementary for infrastructure managers and designers tasked with effectively allocating resources for enhancing system resilience

    Simulation Modeling for Sustainability: A Review of the Literature

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    This article is a review of work published in various journals and conference proceedings on the topics of Simulation Modelling for Sustainability between January 2000 and May 2015. A total of 192 papers are reviewed. The article intends to serve three goals. First, it will be useful to researchers who wish to know what kinds of questions have been raised and how they have been addressed in the areas of simulation modelling for sustainability. Second, the article will be a useful resource for searching research topics. Third, it will serve as a comprehensive bibliography of the papers published during the period. The literature is analysed for application areas, simulation methods and dimensions of the triple bottom line model of sustainable development

    Framework for assessing and improving the performance of recursive digital filters for baseflow estimation with application to the Lyne and Hollick filter

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    Baseflow is often regarded as the streamflow component derived predominantly from groundwater discharge. The estimation of baseflow is important for water supply, water allocation, investigation of contamination impacts, low flow hydrology and flood hydrology. Baseflow is commonly estimated using graphical methods, recursive digital filters (RDFs), tracer based methods, and conceptual models. Of all of these methods, RDFs are the most commonly used, due to their relatively easy and efficient implementation. This paper presents a generic framework for assessing and improving the performance of RDFs for baseflow estimation for catchments with different characteristics and subject to different hydrological conditions. As part of the framework, a fully integrated surface water/groundwater (SW/GW) model is used to obtain estimates of streamflow and baseflow for catchments with different properties, such as soil types and rainfall patterns. An RDF is then applied to the simulated streamflow to assess how well the baseflow obtained using the filter matches the baseflow obtained using the fully integrated SW/GW model. In order to improve the performance of the filter, the user-defined parameter(s) controlling filter operation can be adjusted in order to obtain the best match between the baseflow obtained using the filter and that obtained using the fully integrated SW/GW model (i.e. through calibration). The proposed framework is tested by applying it to a common SW/GW benchmarking problem, the tilted V-catchment, for a range of soil properties. HydroGeoSphere (HGS) is used to develop the fully integrated SW/GW model and the Lyne and Hollick (LH) filter is used as the RDF. The performance of the LH filter is assessed using the commonly used value of the filter parameter of 0.925, as well as calibrated filter parameter values. The results obtained show that the performance of the LH filter is affected significantly by the saturated hydraulic conductivity (Ks) of the soil and that calibrated LH filter parameter can result in significant improvements in filter performance. Β© 2012 Elsevier Ltd.L. Li, H.R. Maier, M.F. Lambert, C.T. Simmons, D. Partingto

    A Methodology for Assessing Dynamic Resilience of Coastal Cities to Climate Change Influenced Hydrometeorological Disasters

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    Confronted with rapid urbanization, intensified tourism, population densification, increased migration, and climate change impacts, coastal cities are facing more challenges now than ever before. Traditional disaster management approaches are no longer sufficient to address the increased pressures facing urban areas. A paradigm shift from disaster risk reduction to disaster resilience building strategies is required to provide holistic, integrated, and sustainable disaster management looking forward. To address some of the shortcomings in current disaster resilience assessment research, a mathematical and computational framework was developed to help quantify, compare, and visualize dynamic disaster resilience. The proposed methodological framework for disaster resilience combines physical, economic, engineering, health, and social spatio-temporal impacts and capacities of urban systems in order to provide a more holistic representation of disaster resilience. To capture the dynamic spatio-temporal characteristics of resilience and gauge the effectiveness of potential climate change adaptation options, a disaster resilience simulator tool (DRST) was developed to employ the mathematical framework. The DRST is applied to a case study in Metro Vancouver, British Columbia, Canada. The simulation model focuses on the impacts of climate change-influenced riverine flooding and sea level rise for three future climates based on the results of the CGCM3 global climate model and two (2) future emissions scenarios. The output of the analyses includes a dynamic set of resilience maps and graphs to demonstrate changes in disaster resilience in both space and time. The DRST demonstrates the value of a quantitative resilience assessment approach to disaster management. Simulation results suggest that various adaptation options such as access to emergency funding, provision of mobile hospital services, and managed retreat can all help to increase disaster resilience. Results also suggest that, at a regional scale, Metro Vancouver is relatively resilient to climate change influenced-hydrometeorological hazards, however it is not distributed proportionately across the region. Although a pioneering effort by nature, the methodological and computational framework behind the DRST could ultimately provide decision support to disaster management professionals, policy makers, and urban planners

    Modeling Socio-Hydrological Systems for Wastewater Reused Watersheds

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    ν•™μœ„λ…Όλ¬Έ (박사)-- μ„œμšΈλŒ€ν•™κ΅ λŒ€ν•™μ› : μƒνƒœμ‘°κ²½Β·μ§€μ—­μ‹œμŠ€ν…œκ³΅ν•™λΆ€(μ§€μ—­μ‹œμŠ€ν…œκ³΅ν•™μ „κ³΅), 2014. 8. λ°•μŠΉμš°.λ³Έ μ—°κ΅¬μ—μ„œλŠ” μœ μ—­ 수문·수질 해석을 톡해 ν•˜μˆ˜μž¬μ΄μš©μ— λ”°λ₯Έ κ΄€κ°œμš©μˆ˜μ—μ˜ 영ν–₯을 λΆ„μ„ν•˜κ³ , 농업생산성과 ν™˜κ²½μ„±μ„ κ³ λ €ν•œ 재이용수 κ΄€κ°œ λ…Όμ˜ 적정 μ§ˆμ†Œμ‹œλΉ„λ°©λ²•μ„ μ œμ•ˆν•˜κ³ μž ν•˜μ˜€λ‹€. λ˜ν•œ, μ‹œμŠ€ν…œ λ‹€μ΄λ‚΄λ―ΉμŠ€λ₯Ό μ΄μš©ν•œ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨λΈλ§κ³Ό κ³Όμ • μ‚¬νšŒμˆ˜λ¬Έν•™μ˜ 인식틀을 톡해 ν•˜μˆ˜μž¬μ΄μš©μ— λ”°λ₯Έ μ†Œκ·œλͺ¨ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œμ˜ 변화과정을 λͺ¨μ˜ 및 λΆ„μ„ν•˜μ˜€λ‹€. SWAT λͺ¨ν˜•μ„ μ΄μš©ν•œ κ°„μ ‘μž¬μ΄μš©μ— λ”°λ₯Έ μœ μ—­μ˜ 수문·수질 μ‘λ‹΅λ°˜μ‘μ„ μ‹€μΈ‘ 수문 및 수질자료λ₯Ό 톡해 보정 및 κ²€μ •ν•œ κ²°κ³Ό, κ΅¬μΆ•ν•œ λͺ¨ν˜•μ΄ λŒ€μƒμœ μ—­μ—μ„œμ˜ κ°„μ ‘μž¬μ΄μš© 영ν–₯을 잘 해석할 수 μžˆλŠ” κ²ƒμœΌλ‘œ ν‰κ°€λ˜μ—ˆλ‹€. κ²€μ •λœ λͺ¨ν˜•μ„ μ΄μš©ν•˜μ—¬ ν•˜μˆ˜μ²˜λ¦¬μž₯의 μœ λ¬΄μ— λ”°λ₯Έ κ΄€κ°œμš©μˆ˜ μ·¨μˆ˜μ§€μ μ—μ„œμ˜ ν•˜μ²œμœ ν™© 및 κ΄€κ°œμˆ˜μ§ˆμ˜ν–₯을 λΆ„μ„ν•˜μ˜€λ‹€. ν•˜μ²œμœ ν™©μ€ ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜λ₯Ό λ°˜μ˜ν•˜μ—¬ μ¦κ°€ν•˜μ˜€μœΌλ©°, κ°ˆμˆ˜λŸ‰μœΌλ‘œ 갈수둝 ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜μ˜ 영ν–₯이 큰 κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ—ˆλ‹€. λ˜ν•œ, ν—ˆμš© κ°€λŠ₯ν•œ μ΄μ§ˆμ†Œ 농도와 λ†μ—…μš©μˆ˜ μˆ˜μ§ˆκΈ°μ€€μ˜ μ΄ˆκ³Όν™•λ₯ μ΄ 각각 60%와 40% 이상 μ¦κ°€ν•˜λŠ” κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ–΄ ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜μ˜ κ΄€κ°œμš©μˆ˜ μˆ˜μ§ˆμ—μ˜ 영ν–₯이 μƒλ‹Ήνžˆ 큰 κ²ƒμœΌλ‘œ ν‰κ°€λ˜μ—ˆλ‹€. DSSAT λͺ¨ν˜•μ„ μ΄μš©ν•œ ν•˜μˆ˜μž¬μ΄μš©μ— λ”°λ₯Έ μ§ˆμ†Œμ‹œλΉ„λ°©λ²• λͺ¨μ˜μ²΄κ³„λ₯Ό κ΅¬μΆ•ν•˜μ˜€μœΌλ©°, κ΅¬μΆ•ν•œ λͺ¨ν˜•μ€ 보정 및 κ²€μ •κΈ°κ°„ λ™μ•ˆ μ‹€μΈ‘ λ…Όλ²Ό μˆ˜ν™•λŸ‰μ„ 잘 λͺ¨μ˜ν•˜λŠ” κ²ƒμœΌλ‘œ λ‚˜νƒ€λ‚¬λ‹€. 적정 μ§ˆμ†Œμ‹œλΉ„λŸ‰μ„ κ΄€κ°œμˆ˜ μ΄μ§ˆμ†Œ 농도 μˆ˜μ€€λ³„λ‘œ λͺ¨μ˜ν•œ κ²°κ³Ό ν‘œμ€€μ‹œλΉ„λŸ‰ λŒ€λΉ„ 20~50% μ €κ°λœ μ§ˆμ†Œμ‹œλΉ„λŸ‰μ—μ„œλ„ λͺ©ν‘œ λ…Όλ²Ό μˆ˜ν™•λŸ‰μ„ 생산할 수 μžˆλŠ” κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ—ˆλ‹€. μ§ˆμ†Œμ‹œλΉ„λ°©λ²•μ— λŒ€ν•œ λ…Όλ²Ό μˆ˜ν™•λŸ‰μ˜ 민감도λ₯Ό λΆ„μ„ν•œ κ²°κ³Ό, 밑거름보닀 μƒˆλΌμΉ κ±°λ¦„κ³Ό 이삭거름에 더 λ―Όκ°ν•œ κ²ƒμœΌλ‘œ λ‚˜νƒ€λ‚¬μœΌλ©°, λΆ„μ‹œμœ¨μ„ μ‘°μ •ν•¨μœΌλ‘œμ¨ 10~20 kg ha-1 μ •λ„μ˜ 좔가적인 μ§ˆμ†Œμ‹œλΉ„λŸ‰ 저감이 κ°€λŠ₯ν•œ κ²ƒμœΌλ‘œ λͺ¨μ˜λ˜μ—ˆλ‹€. μˆ˜λ¬Έμ‹œμŠ€ν…œμ˜ 물리적 ν˜„μƒμ„ μˆ˜μ‹ν™”ν•œ 결정둠적 μ΄κ΄„ν˜• μˆ˜λ¬Έμ‹œμŠ€ν…œ λΆ€λͺ¨ν˜•κ³Ό 인ꡬ, ν† μ§€μ΄μš©, κ²½μ œμ„±, 그리고 기술 및 μ •μ±…μˆ˜μ€€ 등을 μˆ˜μ‹ν™”ν•œ μ‚¬νšŒμ‹œμŠ€ν…œ λΆ€λͺ¨ν˜•μ„ μ‹œμŠ€ν…œ λ‹€μ΄λ‚΄λ―ΉμŠ€λ₯Ό μ΄μš©ν•˜μ—¬ ν•˜λ‚˜μ˜ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨ν˜•μœΌλ‘œ κ΅¬μΆ•ν•˜μ˜€λ‹€. 민감도 뢄석과 κ·Ήν•œμ‘°κ±΄ μ‹œν—˜, 그리고 SWAT λͺ¨ν˜•μ˜ λͺ¨μ˜κ²°κ³Ό 및 μ‹€μΈ‘ μˆ˜λ¬Έμžλ£Œμ™€μ˜ 비ꡐλ₯Ό 톡해 κ΅¬μΆ•ν•œ λͺ¨ν˜•μ΄ ꡬ쑰 건전성과 거동 객관성을 가진 κ²ƒμœΌλ‘œ ν‰κ°€λ˜μ—ˆλ‹€. μΈκ΅¬μ¦κ°€λŠ” ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜λ₯Ό 톡해 ν•˜μ²œμœ λŸ‰κ³Ό μ§€ν•˜μˆ˜μœ„, 그리고 ν•˜μˆ˜μž¬μ΄μš©λŸ‰μ„ μ¦κ°€μ‹œν‚€λŠ” κ²ƒμœΌλ‘œ λͺ¨μ˜λ˜μ—ˆλ‹€. λ†κ²½μ§€μ˜ λ„μ‹œμš©μ§€λ‘œμ˜ ν† μ§€μ΄μš© λ³€ν™”λŠ” μΉ¨νˆ¬λŸ‰κ³Ό λ†μ—…μš©μˆ˜ μˆ˜μš”λŸ‰μ„ κ°μ†Œμ‹œν‚€κ³ , μ§€ν•˜μˆ˜ κ΄€κ°œλŸ‰μ˜ κ°μ†Œλ‘œ μ§€ν•˜μˆ˜μœ„λ₯Ό μƒμŠΉμ‹œν‚¬ 수 μžˆλŠ” κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ—ˆλ‹€. λͺ©ν‘œ μˆ˜λ¦¬λ‹΅λ₯ μ„ λ‹¬μ„±ν•˜κΈ° μœ„ν•΄ μ§€ν•˜μˆ˜ κ΄€κ°œ 비쀑을 높일 경우 지속가λŠ₯ν•˜μ§€ μ•Šμ€ μ§€ν•˜μˆ˜ 이용이 λ°œμƒν•  수 있으며, 재처리수 κ΄€κ°œλŸ‰μ„ 늘릴수둝 λͺ©ν‘œ μˆ˜λ¦¬λ‹΅λ₯ μ„ 보닀 빨리, 그리고 μ•ˆμ •μ μœΌλ‘œ 달성할 수 μžˆλŠ” κ²ƒμœΌλ‘œ λͺ¨μ˜λ˜μ—ˆλ‹€. 재처리수 κ΄€κ°œμ‹œμ„€μ— λŒ€ν•œ κ²½μ œμ„± 뢄석결과, μ‹œμ„€ 규λͺ¨κ°€ μž‘μ„μˆ˜λ‘ λ‹¨μœ„μžλ³ΈλΉ„μ˜ 영ν–₯이 μ¦κ°€ν•˜μ˜€μœΌλ©°, 재처리수 κ΄€κ°œμ˜ κ²½μ œμ„±μ— λ‹¨μœ„μžλ³ΈλΉ„κ°€ λ‹¨μœ„μš΄μ˜λΉ„λ³΄λ‹€ 더 큰 영ν–₯을 λ―ΈμΉ˜λŠ” κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ—ˆλ‹€. λ˜ν•œ, ν•˜μ²œμœ μ§€μœ λŸ‰μ„ ν†΅ν•œ ν•˜μ²œμˆ˜ 취수 μ œν•œμ€ ν•˜μ²œμœ λŸ‰μ˜ λ³΄μ „λΏλ§Œ μ•„λ‹ˆλΌ 보상적 μ§€ν•˜μˆ˜ κ΄€κ°œ 및 κΈ°μ €μœ μΆœμ— λ”°λ₯Έ μƒλŒ€μ  ν•˜μ²œμœ λŸ‰μ˜ κ°μ†Œμ™€ μ‚¬νšŒμ  κΈ°νšŒλΉ„μš© λ˜ν•œ μ•ΌκΈ°ν•  수 μžˆλŠ” κ²ƒμœΌλ‘œ λΆ„μ„λ˜μ—ˆλ‹€. ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜μ˜ κ΄€κ°œμš©μˆ˜μ—μ˜ 영ν–₯κ³Ό λŒ€μ•ˆμ  μ§ˆμ†Œμ‹œλΉ„ λ°©λ²•μœΌλ‘œλΆ€ν„° 지속가λŠ₯ν•œ λŒ€μ²΄μˆ˜μžμ›μœΌλ‘œμ„œμ˜ ν•˜μˆ˜μ²˜λ¦¬μˆ˜μ˜ λ†μ—…μš©μˆ˜μž¬μ΄μš©μ„ μœ„ν•œ 합리적인 κ΄€λ¦¬λ°©μ•ˆμ„ λ§ˆλ ¨ν•  수 μžˆμ„ κ²ƒμœΌλ‘œ κΈ°λŒ€λœλ‹€. λ˜ν•œ, μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨λΈλ§μ€ μˆ˜μžμ› 정책결정에 μ€‘μš”ν•œ λ„κ΅¬λ‘œ ν™œμš©ν•  수 있으며, μ†Œκ·œλͺ¨ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œμ˜ 인과관계에 λŒ€ν•œ 보닀 μƒμ„Έν•œ 톡찰을 톡해 κ³Όμ • μ‚¬νšŒμˆ˜λ¬Έν•™μ˜ λ°©λ²•λ‘ μœΌλ‘œ μ‚¬μš©ν•  수 μžˆμ„ κ²ƒμœΌλ‘œ κΈ°λŒ€λœλ‹€.λͺ© μ°¨ 초 둝 β…° λͺ© μ°¨ β…² List of Tables β…Ά List of Figures β…Ή 제 1 μž₯ μ„œ λ‘  1 1.1. 연ꡬ배경 및 λͺ©μ  1 1.2. 논문ꡬ성 5 제 2 μž₯ 연ꡬ사 7 2.1. ν•˜μˆ˜μ²˜λ¦¬μˆ˜μ˜ λ†μ—…μš©μˆ˜μž¬μ΄μš© 7 2.2. 수문λͺ¨ν˜•κ³Ό ν•˜μˆ˜μž¬μ΄μš© μœ μ—­ 수문·수질 λͺ¨μ˜ 9 2.3. μž‘λ¬Όμƒμœ‘λͺ¨ν˜•κ³Ό μ μ •μ‹œλΉ„λŸ‰ λͺ¨μ˜ 11 2.4. μ‚¬νšŒμˆ˜λ¬Έν•™κ³Ό μ‹œμŠ€ν…œ λ‹€μ΄λ‚΄λ―ΉμŠ€ 12 제 3 μž₯ SWAT λͺ¨ν˜•μ„ μ΄μš©ν•œ μœ μ—­ 수문·수질 해석 16 3.1. SWAT λͺ¨ν˜• 16 3.2. λŒ€μƒμœ μ—­ 및 μž…λ ₯자료 17 3.2.1. λŒ€μƒμœ μ—­ 17 3.2.2. 수문 및 수질자료 19 3.2.3. μž…λ ₯자료 22 3.3. λͺ¨ν˜•μ˜ 보정과 κ²€μ • 28 3.3.1. μœ μΆœλŸ‰ 32 3.3.2. μœ μ‚¬λŸ‰ 39 3.3.3. μ΄μ§ˆμ†Œ 42 3.4. κ΄€κ°œμš©μˆ˜ 영ν–₯ 뢄석 45 3.4.1. ν•˜μˆ˜μ²˜λ¦¬μž₯ λ°©λ₯˜μˆ˜ 46 3.4.2. ν•˜μ²œμœ λŸ‰ 49 3.4.3. κ΄€κ°œμˆ˜μ§ˆ 53 3.4.4. ν•˜μˆ˜μž¬μ΄μš©λŸ‰ 56 3.5. μš”μ•½ 및 κ²°λ‘  58 제 4 μž₯ DSSAT λͺ¨ν˜•μ„ μ΄μš©ν•œ λ…Όλ²Ό μˆ˜ν™•λŸ‰ λͺ¨μ˜ 60 4.1. DSSAT λͺ¨ν˜• 60 4.2. μ‹œν—˜ν¬μž₯ 및 μž…λ ₯자료 62 4.2.1. μ‹œν—˜ν¬μž₯ 62 4.2.2. μž…λ ₯자료 63 4.3. λͺ¨ν˜•μ˜ 보정과 κ²€μ • 68 4.3.1. λͺ¨ν˜•μ˜ 보정 68 4.3.2. λͺ¨ν˜•μ˜ κ²€μ • 71 4.4. 적정 μ§ˆμ†Œμ‹œλΉ„ 방법 λͺ¨μ˜ 74 4.4.1. μ§ˆμ†Œμ‹œλΉ„λŸ‰μ— λ”°λ₯Έ λ…Όλ²Ό μˆ˜ν™•λŸ‰ 75 4.4.2. μ§ˆμ†Œμ‹œλΉ„μ— λŒ€ν•œ λ…Όλ²Ό μˆ˜ν™•λŸ‰ 민감도 78 4.4.2. μ§ˆμ†Œμ‹œλΉ„ λΆ„μ‹œμœ¨μ— λ”°λ₯Έ λ…Όλ²Ό μˆ˜ν™•λŸ‰ 80 4.5. μš”μ•½ 및 κ²°λ‘  82 제 5 μž₯ μ‹œμŠ€ν…œ λ‹€μ΄λ‚΄λ―ΉμŠ€λ₯Ό μ΄μš©ν•œ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨λΈλ§ 84 5.1. μ‹œμŠ€ν…œ λ‹€μ΄λ‚΄λ―ΉμŠ€ 86 5.2. λŒ€μƒμœ μ—­ 및 μž…λ ₯자료 88 5.2.1. λŒ€μƒμœ μ—­ 88 5.2.2. μž…λ ₯자료 96 5.3. μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨λΈλ§ 111 5.3.1. λ¬Έμ œμ •μ˜ 111 5.3.2. 인과지도 113 5.3.3. μˆ˜λ¬Έμ‹œμŠ€ν…œ λΆ€λͺ¨ν˜• 116 5.3.4. μ‚¬νšŒμ‹œμŠ€ν…œ λΆ€λͺ¨ν˜• 127 5.3.5. μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨ν˜• 146 5.4. λͺ¨ν˜•μ˜ 평가 155 5.4.1. λͺ¨ν˜• 건전성 156 5.4.2. λͺ¨ν˜• 객관성 166 5.5. μš”μ•½ 및 κ²°λ‘  173 제 6 μž₯ ν•˜μˆ˜μž¬μ΄μš©μ— λ”°λ₯Έ μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ 해석 175 6.1. μ‹œλ‚˜λ¦¬μ˜€ 섀계 176 6.2. λ„μ‹œν™” 영ν–₯ 뢄석 177 6.2.1. 인ꡬ증가 177 6.2.2. ν† μ§€μ΄μš© λ³€ν™” 184 6.3. ν•˜μˆ˜μž¬μ΄μš© 영ν–₯ 뢄석 190 6.3.1. μˆ˜λ¬Έμ‹œμŠ€ν…œ 190 6.3.2. μ‚¬νšŒμ‹œμŠ€ν…œ 194 6.3.3. κ²½μ œμ„± 뢄석 202 6.4. ν•˜μ²œμœ μ§€μœ λŸ‰ 영ν–₯ 뢄석 205 6.4.1. κΈ°μ€€μœ λŸ‰μ˜ μ‚°μ • 205 6.4.2. μˆ˜λ¬Έμ‹œμŠ€ν…œ 206 6.4.3. μ‚¬νšŒμ‹œμŠ€ν…œ 209 6.5. μ‚¬νšŒ-μˆ˜λ¬Έμ‹œμŠ€ν…œ λͺ¨λΈλ§μ˜ ν•¨μ˜ 213 6.6. μš”μ•½ 및 κ²°λ‘  215 제 7 μž₯ μ’…ν•©κ²°λ‘  217 μ°Έκ³ λ¬Έν—Œ 221 Abstract 242Docto

    Combined Strategic-Tactical Planning for Facility Rehabilitation Using System Dynamics and Optimization

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    Rehabilitation programs are essential for efficiently managing large networks of infrastructure assets and sustaining their safety and operability. While numerous studies in the literature have focused on various aspects of infrastructure rehabilitation, such as rehabilitation processes, deterioration modeling, life cycle cost analysis, project financing, etc., limited efforts have investigated the overall dynamics among these functions and the development of holistic models that can analyze the long-term effect of different strategic policies and their impact on tactical rehabilitation decisions. To support strategic level of decision-making and long-term policy analysis, this research utilized System Dynamics (SD) to study the dynamic interactions among the deterioration, rehabilitation, and budgeting feedback loops. Model performance and suggested policies were also checked against reference modes and verified using various model testing methods to ensure adequacy. The proposed System Dynamics model was then expanded to incorporate four main modules including policy, physical condition, life cycle cost, and sustainability, for the purpose of backlog accumulation analysis. School building facilities were used as the focused asset domain of this study. After identification of key variables based on literature analysis, previous researches on school building facilitates, and experts’ opinion, the dynamic interactions were studied using causal loop diagraming (CLD) methods. The developed CLD was then mapped into a stock-and-flow simulation model incorporating the four integrated modules with all the underlying mathematical relationships. Numerous experiments with different policy scenarios were conducted to investigate the impact of various policies related to rehabilitation, budget distribution, government investment, and private financing. The simulation results clearly indicated that some of the commonly used policies such as condition-based prioritization methods can lead to significant long-term problems in terms of backlog, and showed that equal distribution of budget can be more effective. Simulation results also indicated that the use of private financing for backlog elimination need to be carefully analyzed to determine a proper payback scheme without a negative effect on long-term backlog projections. The SD Model was also adopted to provide optimum policy solutions in terms of the level of budget allocated to rehabilitation of exiting school buildings and construction of new facilities to accommodate future enrolment. The proposed model used facility condition index (FCI) as an industry standard to investigate facility performance and also a utilized a facility risk index (FRI) to account for the risk of failure. The model was used to investigate and compare the effect of using enrolment-based budgeting policies versus an optimized policy solution on a network of 438 elementary school buildings. Results clearly showed that the enrolment-based approach, which has been used by education ministries for a long time, could be significantly improved with the used of policy optimization. The policy solutions form the strategic-level analysis were used to create detailed tactical rehabilitation plans. To support the tactical level of decision-making this research investigated the performance of mathematical mixed integer programming and genetic algorithm (GA) optimization models to handle the large-scale tactical problems. First, various model formulations including an integer, a one-shot binary, and a year-by-year binary formulation were examined for their performance on large-scale problems. A year-by-year formulation was then selected for the network-level analysis and was used with GA-based optimization. To improve the performance of the GA-based model, a segmentation approach was used that was able to eliminate performance degradation, yet exhibited long processing time. Subsequently, an integer programming model was developed on the GAMS/CPLEX optimization tool that resulted in the best solution quality and fast processing time for very large-scale problems (e.g., 50,000 building components). The promising result of the proposed mathematical model was mainly attributed to the formulation of the optimization model, advancements in the used optimization tools, and the separation between project and network level analysis. Combination of the strategic and tactical models developed in this research provides a comprehensive and systematic framework for a combined analysis of rehabilitation plans at both strategic and tactical levels of facility management
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