• 한국지반공학회논문집
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• 제22권12호
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• pp.33-43
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• 2006

직항타공법에서 사용되는 해머 쿠션의 재질 차이가 항타시 주변 지반의 진동과 발생 소음 및 에너지 전달효율에 미치는 영향을 실내 모형시험을 통해 평가하였다. 항타 과정을 모사할 수 있는 모델 말뚝과 항타시스템 및 스트레인 게이지와 홉킨슨 바(Hopkinson bar)를 이용한 에너지 전달효율 측정장치를 제작, 구성하였다. 해머 쿠션 재질로는 상용의 해머 쿠션재인 Micarta 이외, 현장에서 다수 사용하는 Plywood, Polyurethane, Rubber(SBR), Silicone rubber 등의 5가지 재료를 선정하여 항타시험을 실시하였다 항타시험결과 쿠션 재료별 에너지 전달효율은 (1)Micarta, (2)Polyurethane, (3)Plywood, (4)Rubber(SBR), (5)Silicone rubber의 순이었다. 또한 에너지 전달효율이 높은 쿠션재료가 음압레벨의 평균치 또한 높은 비례관계를 보였다. 항타 종료후 말뚝 정재하시험을 실시하여 말뚝의 지지력과 축하중전이 특성을 비교, 분석한 결과 Micarta와 Polyurethane이 다른 쿠션재료에 비해 높은 지지력 값을 보였다.

• 국제학술발표논문집
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• The 6th International Conference on Construction Engineering and Project Management
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• pp.54-55
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• 2015

Increase of impervious areas due to expansion of housing area, commercial and business building of urban is resulting in property change of stormwater runoff. Also, rapid urbanization and heavy rain due to climate change lead to urban flood and debris flow damage. In 2010 and 2011, Seoul had experienced shocking flooding damages by heavy rain. All these have led to increased interest in applying LID and decentralized rainwater management as a means of urban hydrologic cycle restoration and Natural Disaster Prevention such as flooding and so on. Urban development is a cause of expansion of impervious area. It reduces infiltration of rain water and may increase runoff volume from storms. Low Impact Development (LID) methods is to mimic the predevelopment site hydrology by using site design techniques that store, infiltrate, evaporate, detain runoff, and reduction flooding. Use of these techniques helps to reduce off-site runoff and ensure adequate groundwater recharge. The contents of this paper include a hydrologic analysis on a site and an evaluation of flooding reduction effect of LID practice facilities planned on the site. The region of this Case study is LID Rainwater Management Demonstration District in A-new town and P-new town, Korea. LID Practice facilities were designed on the area of rainwater management demonstration district in new town. We performed analysis of reduction effect about flood discharge. SWMM5 has been developed as a model to analyze the hydrologic impacts of LID facilities. For this study, we used weather data for around 38 years from January 1973 to August 2014 collected from the new town City Observatory near the district. Using the weather data, we performed continuous simulation of urban runoff in order to analyze impacts on the Stream from the development of the district and the installation of LID facilities. This is a new approach to stormwater management system which is different from existing end-of-pipe type management system. We suggest that LID should be discussed as a efficient method of urban disasters and climate change control in future land use, sewer and stormwater management planning.

• 환경영향평가
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• 제4권3호
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• pp.41-48
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• 1995

In former times the protection of our environment didn't play an important role due to the fact that emissions and effluents were not considered as serious impacts. However, opinions and scientific measurements meanwhile confirmed that the impacts are more serious than expected. Thus measures to protect our earth has to be taken into consideration. A part of these measures in the Environmental Impact Assessment (EIA). One of the most important parts of the EIA is the collection of basic datas and the following evaluation. Experience out of the daily business of Gerling Consulting Group shows that the content of the EIA has to be revised and enlarged in certain fields. The historical development demonstrated that in areas in which the population and the industrial activities reached high concentration there is a high necessity to develop strict environmental laws and regulations. Maximum values of the concentration of hazardous materials were fixed concerning the emission into and water. Companies not following these regulations were punished. The total amount of environmental offences increased rapidly during the last decade, at least in Germany. During this development the public consciousness concerning environmental affairs increased as well in the industrialized countries. But it could clearly be seen that the development in the field of environmental protection went into the wrong direction. The technologies to protect the environment became more and more sophisticated and terms as: "state of the art" guided more and more to lower emissions, Filtertechnologies and wastewater treatment for example reached a high technical level-but all these sophisticated technologies has one and the same characteristic: they were end-of-the pipe solutions. A second effect was that this kind of environmental protection costs a lot of money. High investments are necessary to reduce the dust emission by another ppm! Could this be the correct way? In Germany the discussion started that the environmental laws reduce the attractivity to invest or to enlarge existing investments within the country. Other countries seem to be not so strict with controlling the environmental laws which means it's simply cheaper to produce in Portugal or Greece. Everybody however knows that this is not the correct way and does not solve the environmental problems. Meanwhile the general picture changes a little bit and we think it changes into the correct direction "End-of-the-pipe" solutions are still necessary but this word received a real negative touch and nobody wants to be brought into connection with this word received a real negative touch and nobody wants to be brought into connection with this word especially in connection with environmental management and safety. Modern actual environmental management starts in a different way. Thoughts about emissions start in the very beginning of the production, they start with the design of the product and modification of traditional modes of production. Basis of these ideas are detailed analyses of products and processes. Due to the above mentioned facts that the public environmental consciousness changed dramatically a continous environmental improvement of each single production plant has to be guarantied. This question is already an important question of the EIA. But it was never really checked in a wholistic approach. Environmental risks have to be taken into considerations during the execution of an EIA. This means that the environmental risks have to be reduced down to a capable risk-level. Environmental risks have to be considered within the phase of planning, during the operation of a plant and after shut down. The experience shows that most of the environmental relevant accidents were and caused by human fault. Even in highly protected plants the human risk-factor can not be excluded during evaluation of the risk-potential. Thus the approach of an EIA has to regard technical evaluations as well as organizational thoughts and the human factor. An environmental risk is a threat to the environment. An analysis of the risk concerning the organizational and human aspect however never was properly executed during an EIA. A possible solution could be to use an instrument as the actual EMAS (Environmental Management System) of the EC for more accurate evaluation of the impact to the environment during an EIA. Organizations or investors could demonstrate by an approved EMAS or even by showing their installment of EMAS that not only the technical level of the planned investment meets the requested standards but as well the actual or planned management is able to reduce the environmental impact down to a bearable level.

• 생물환경조절학회지
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• 제16권4호
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• pp.275-283
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• 2007

본 연구는 기존 비닐하우스 아연도 강관을 사용한 하우스 폭 3.6m와 5m 천창개폐형 대립계 포도 비가림하우스에 대한 구조적 안전성을 검토하고, 인장강도 $400N{\cdot}mm^{-2}$(SGH400 등) 이상의 파이프를 사용하는 조건에서 하우스 폭 5m인 천창개폐형 대립계 포도 비가림하우스에 대하여 구조적으로 안전한 최적 파이프 규격을 제시하고자 수행하였다. 주기둥 $3m{\times}$서까래 60cm인 천창개폐형 3.6m 비가림하우스의 경우, 적설심 35cm에서는 구조적으로 안전한 것으로 분석되었으나 측면 및 전후면 풍속 $35m{\cdot}s^{-1}$에서는 불안전한 것으로 나타났으며, 동일 주기둥과 서까래 간격을 갖는 천창개폐형 5m 비가림하우스의 경우에는 적설심 35와 풍속 $35m{\cdot}s^{-1}$에서 모두 불안전하여 구조보강이 필요한 것으로 분석되었다. 그리고 동일 주기둥과 서까래간격을 가지나 인장강도 $400N{\cdot}mm^{-2}$ 이상을 갖는 파이프를 사용하는 조건에서 천창개폐형 5m 비가림하우스의 최적 파이프 규격은 지붕높이 1.6m(아치형)와 지붕높이 1.8m(복숭아형)에 대하여 동일하게 두 경우로 규격화 할 수 있었다. 즉, 안전풍속 $35m{\cdot}s^{-1}$와 안전적설심 40cm에서 구조적으로 안전한 서까래 규격은 ${\Phi}31.8{\times}1.5t@600$이었으며, 안전풍속 $35m{\cdot}s^{-1}$와ss 안전적설심 35cm에서는 서까래 ${\Phi}25.4{\times}1.5t@600$인 것으로 분석되었다. 덕면으로부터 곡부보까지의 높이는 안전적설심보다는 안전풍속에 직접적인 영향을 미치는 것으로 분석되었으며, 처마를 높임에 따라 측면풍속에 대해서는 방풍벽파이프(측벽서까래)를, 전후면 풍속에 대해서는 마구리기둥의 규격을 강화하여야 하는 것으로 분석되었다.

• 한국산업보건학회지
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• 제15권2호
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• pp.124-134
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• 2005

To investigate the exposure effect of polynuclear aromatic hydrocarbons (PAHs), we measured airborne total PAHs as an external dose, urinary 1-hydroxypyrene (1-OHP) as an internal dose of PAHs exposure, and analyzed the relationship between urinary 1-OHP concentration and PAHs exposure. The study population contained 44 workers in steel-pipe coating and paint manufacture industries. The airborne PAHs was obtained during survey day, and urine were sampled at the end of shift. Personal information on age, body weight, height, eniployment duration, smoking habit, and alcohol consumption was obtained by a structured questionnaire. Airborne PAHs were analyzed by the gas chromatograph with mass selective detector. Urinary 1-OHP levels were analyzed by the high performance liquid chromatograph with ultraviolet wavelength detector. For statistical estimation, t-test, ${\chi}^2$-test, analysis of variance, correlation analysis, arid regression analysis were executed by SPSS/PC (Windows version 10). The mean of environmental total PAHs was $87.8{\pm}7.81{\mu}g/m^3$. The mean concentration ($526.5{\pm}2.85{\mu}g/m^3$) of workers in steel-pipe coating industries using coal tar enamel was the higher than that ($17.5{\pm}3.36{\mu}g/m^3$) of workers in paint manufacture industries using coal tar paint. The mean of urinary 1-OHP concentration ($51.63{\pm}3.144{\mu}\;mol/mol$ creatinine) of workers in steel-pipe coating industries was the higher than that ($2.33{\pm}4.709{\mu}\;mol/mol$ creatinine) of workers in paint manufacture industries. The mean of urinary 1-OHP concentration of smokers was the higher than that of non-smokers. There was significant correlation between the urinary concentration of 1-OHP and the environmental concentration of PAHs (r=O.S48, p<0.001), pyrene(r=0.859, p<0.001), and urinary cotinine (r=0.324, p<0.05). The regression equation between the urinary concentration of 1-OHP in ${\mu}g/g$ creatinine($C_{1-OHP}$) and airborne concentration of PAHs (or pyrene) in ${\mu}g/m^3$ ($C_{PAHs}$ or Cpyrene) is: Log ($C_{1-OHP}$)=-0.650+0.889×Log($C_{PAHs}$), where $R^2=0.694$ and n=38 for p<0.001.Log ($C_{1-OHP}$)=1.087+0.707${\times}$Log(Cpyrene), where $R^2=0.713$ and n=38 for p<0.001. From the results of stepwise multiple regression analysis about 1-OHP, significant independents were total PAHs and urinary cotinine (adjusted $R^2=0.743$, p<0.001). In this study, there were significant correlation between the urinary concentration of 1-OHP and the airborne concentration of PAHs. The urinary 1-OHP was effective index as a biomarker of airborne PAHs in workplace. But it was influenced by non-occupational PAHs source, smoking.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 1997년도 추계 국제학술심포지움 논문집
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• pp.3-31
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• 1997

Water has always played a significant role in the lives of people. In urbanised Rome, with its million people. sophisticated supply systems developed and then fled with the empire. only to be rediscovered later But it was the industrial Revolution commencing in the eighteenth century that ushered in major paradigm shifts In use and altitudes towards water. Rapid and concentrated urbanisation brought problems of expanded demands for drinking supplies, waste management and disease. The strategy of using water from local streams, springs and village wells collapsed under the onslaughts of rising urban demands and pollution due to poor waste disposal practices. Expanding travel (railways. and steamships) aided the spread of disease. In England. public health crises peaks, related to water-borne typhoid and the three major cholera outbreaks occurred in the late eighteenth and early nineteenth century respectively. Technological, engineering and institutional responses were successful in solving the public health problem. it is generally accepted that the putting of water into pipe networks both for a clean drinking supply, as well as using it as a transport medium for removal of human and other wastes, played a significant role in towering death rates due to waterborne diseases such as cholera and typhoid towards the end of the nineteenth century. Today, similar principles apply. A recent World Bank report Indicates that there can be upto 76％ reduction in illness when major water and sanitation improvements occur in developing countries. Water management, technology and thinking in Australia were relatively stable in the twentieth century up to the mid to late 1970s. Groundwater sources were investigated and developed for towns and agriculture. Dams were built, and pipe networks extended both for supply and waste water management. The management paradigms in Australia were essentially extensions of European strategies with the minor adaptions due to climate and hydrogeology. During the 1970s and 1980s in Australia, it was realised increasingly that a knowledge of groundwater and hydrogeological processes were critical to pollution prevention, the development of sound waste management and the problems of salinity. Many millions of dollars have been both saved and generated as a consequence. This is especially in relation to domestic waste management and the disposal of aluminium refinery waste in New South Wales. Major institutional changes in public sector water management are occurring in Australia. Upheveals and change have now reached ail states in Australia with various approaches being followed. Market thinking, corporatisation, privatisation, internationalisation, downsizing and environmental pressures are all playing their role in this paradigm shift. One casualty of this turmoil is the progressive erosion of the public sector skillbase and this may become a serious issue should a public health crisis occur such as a water borne disease. Such crises have arisen over recent times. A complete rethink of the urban water cycle is going on right now in Australia both at the State and Federal level. We are on the threshold of significant change in how we use and manage water, both as a supply and a waste transporter in Urban environments especially. Substantial replacement of the pipe system will be needed in 25 to 30 years time and this will cost billions of dollars. The competition for water between imgation needs and environmental requirements in Australia and overseas will continue to be an issue in rural areas. This will be especially heightened by the rising demand for irrigation produced food as the world's population grows. Rapid urbanisation and industrialisation in the emerging S.E Asian countries are currently producing considerable demands for water management skills and Infrastructure development. This trend e expected to grow. There are also severe water shortages in the Middle East to such an extent that wars may be fought over water issues. Environmental public health crises and shortages will help drive the trends.

• 한국수자원학회논문집
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• 제53권9호
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• pp.661-670
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• 2020

최근 지진재해의 규모가 점차 증대됨에 따라 세계적으로 개별 시설물에 대한 내진성능평가와 관련한 연구가 다수 진행되고 있다. 상수도 시스템은 타 기반 시설에 비해 설치범위가 광범위하고 그 구성요소가 다양해 고려할 것이 많아 지진에 대한 안정성을 정확하고 효과적으로 확보하기 힘든 실정이다. 따라서 지진을 대비한 상수도 시스템의 내진성능 평가 방안을 연구하고 개발할 필요가 있다. 지진에 의한 상수도 시스템의 내진성능을 평가하기 위해 지반운동예측식(Ground Motion Prediction Equation, GMPE)이 활용된다. GMPE는 지진 규모 등과 같은 독립변수 와 PGV (Peak Ground Velocity), PGA (Peak Ground Acceleration)와 같은 지반운동 등을 고려하여 산정하게 된다. 우리나라에서 발생된 높은 강도의 지진 데이터는 현재까지 많이 축적되지 않아 특정 지진에 국한된 데이터를 활용하여 GMPE를 결정하는 등의 연구가 진행되었다. 본 연구에서는 우리나라에서 계측된 지진 데이터를 활용하여 국내 지진 모의에 적합한 GMPE를 선정하고자 하였으며, 이를 위해 기존 국내 지진을 기반으로 산정된 GMPE식을 분석하고 그 결과를 제시하였다. 본 연구를 통해 결정된 적정 GMPE는 상수도관망의 수리학적 내진성능 평가에 직접적으로 활용 가능하다. 즉, 파손확률 모형과의 연계를 통한 지진시 관로 파손률의 정량화가 가능하며, 파손 및 누수에 의한 단수지역 파악 등과 같은 피해범위 산정시 보다 객관적이며 합리적인 결과 도출이 가능하다. 최종적으로 이와 같은 내진 성능 정량화 결과는 지진재해가 발생하였을 경우 그 피해를 최소화할 수 있는 최적 복구방안 마련과 선제적 관망 내진설계의 기준 자료로 활용될 수 있다.

• 생물환경조절학회지
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• 제24권4호
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• pp.333-340
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• 2015

간척지 내 토양은 염분농도 및 함수비가 일반지역에 비해 상당히 높기 때문에 간척지에 매입된 온실의 부재는 높은 부식 환경에 노출된다. 염해의 환경에서는 파이프 골조로 이루어진 온실의 기초 및 기초와 이어진 파이프에 부식을 촉진시키기 때문에 이에 대한 보수/보강기술개발 및 효율적인 유지 관리가 필요하다. 본 연구에서는 염해의 위험성이 높은 간척지에 적합한 온실의 유지관리, 보수/보강에 대한 기준을 마련하기 위한 기초자료로서 토양염분환경에서 온실부재의 부식속도를 측정하였다. 각 온실파이프는 염분농도가 0%, 0.1%, 0.3% 및 0.5%인 토양 및 수중환경에 관찰기간동안(480일) 노출시켜 부식속도를 측정하였으며, 그 결과 육안으로도 염분 농도에 따른 부식정도의 차이가 뚜렷하게 관찰되었으며, 시험편의 표면이 검은색의 부식현상과 함께 비교적 고르게 부식되는 균일부식의 형태를 나타내었다. 논토양의 경우 염분농도 0, 0.1, 0.3, 0.5%에서 각각 0.008, 0.027, 0.036, $0.043mm{\cdot}yr^{-1}$로 염분농도가 증가할수록 부식속도가 뚜렷하게 증가하는 경향을 나타내었고 밭토양의 경우, 염분농도 0, 0.1, 0.3, 0.5%에서 각각 0.0002, 0.039, 0.040, $0.039mm{\cdot}yr^{-1}$의 부식속도를 나타내었다. 상대적으로 세립질이 많은 논토양에서 부식속도가 더 높은 것으로 나타났으며, 이는 입경이 작고 고르게 분포하는 토양에서 부식속도가 높은 일반적인 특성이 그대로 반영된 것으로 판단되었다. 간척지의 경우 토양의 입자의 세립정도는 일반 내륙지역의 농경지 토양보다 높을 것으로 예상되기 때문에 파이프 부식에 대한 철저한 대비가 있어야 할 것으로 판단되었다.

• 대한용접접합학회:학술대회논문집
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• 대한용접접합학회 2009년 추계학술발표대회
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• pp.100-100
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• 2009

본 논문에서는 원자력발전소 1차 계통의 스테인리스강 저합금강 이종금속용접부 및 스테인리스강 동종용접부의 잔류응력을 평가하고 스테인리스강 용접부의 응력부식균열 민감성에 대해 고찰하였다. 노즐 안전단의 이종금속용접부 및 안전단 배관의 동종용접부 제작 및 소재가공에 의행 생성되는 잔류응력을 예측하기 위해 열 탄소성 유한요소법 수치해석을 수행하였으며, 용접공정과 함께 표면의 잔류응력에 기여하는 절삭 및 연삭가공과 소재의 담금질 공정을 열 탄소성적으로 모사하였다. 전산해석 결과, 스테인리스주강의 담금질 잔류응력은 무시할 수 없는 상당한 크기이므로 배관 용접잔류응력 평가 시 소재의 담금질 효과를 고려해야 할 것으로 판단된다. 이종금속 용접과 동종금속 용접공정이 보수용접 없이 정상적인 절차(내면에서 외면으로 적층)로 완성된다면, 냉각재 환경에 노출되는 용접부 내면의 잔류응력은 재료의 응력부식균열 민감성에 영향을 주지 않을 것으로 판단된다. 한편, 안전단 배관 동종용접부의 연삭가공에 의해 내면의 잔류응력이 크게 상승하는 것으로 예측되었으므로, 내면의 연삭가공 이후 표면잔류응력 완화처리(예, 버핑)가 필요하다.

• 원예과학기술지
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• 제17권6호
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• pp.737-741
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• 1999

본 조사는 생리장해 연구의 기초자료를 얻기 위하여 1998년에 경북 시설 과채류 주산지에서 재배실태와 생리장해에 대하여 농가 현장방문을 통하여 실시되었다. 재배시설의 형태는 단동 또는 연동의 철 파이프 PE하우스가 대부분이며, 딸기, 참외, 수박은 단동 PE하우스, 그리고 토마토와 오이는 연동하우스를 이용하였다. 전체 조사농가 중 단작의 비율은 56.8%, 그리고 윤작은 40.9%로 나타났다. 시설내의 관수는 점적만 하는 농가는 전체 농가의 38.6%이다. 연작연수는 전제적으로 5년 미만의 농가가 38.1%였으며, 10년 이상 된 농가도 20.5%에 달하였다. 재배품종은 작물별로 다양하나, 특히 오이와 수박에서 다양하였다. 딸기의 기형과는 3월에 발생이 많았고 수확종기에 소과가 나타났다. 영양결핍에 의한 황화증상은 5월 이후에 많았고, 월동기에 왜화와 생육초기에 런너발생 등이 관찰되었다. 토마토는 9~11월에 열과, 10월과 2~4월에 기형과, 7~9월에 배꼽썩음과 등이 심하였으며, 순멎이, 이상경, 영양결핍증 등도 관찰되었다. 오이는 곡과, 곤봉과, 어깨빠진과 등 기형과는 11~12월에 심하게 나타났으며, 5~7월에 낙하산엽 증상 등이 조사되었다. 참외의 기형과와 발효과는 3~5월에 심하였고 수박의 열과도 4~5월에 많았으며 변형과는 8월에 나타났다. 식물체에는 영양결핍인 황화증상이 다수의 농가에서 발견되었다. 생리장해에 대한 인식은 병해충에 대한 인식보다 강하지 못할 뿐 아니라 장해의 동정이나 방제법에 소홀한 점들이 많았다. 생리장해 발생원인으로는 토양환경 불량과 온도관리의 미흡이라고 응답하였으며 대책으로는 하우스 환경관리를 잘 해야 한다고 대부분의 농가가 응답하였다.