• Title/Summary/Keyword: 토양 재활용

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Prediction of PAHs Concentration using Statistical Analysis for Soil Recycling (토양 재활용을 위한 통계적 분석의 PAHs 농도 예측)

  • Kim, Jongo;Lee, Manseung
    • Resources Recycling
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    • v.26 no.4
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    • pp.56-61
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    • 2017
  • This study investigated the feasibility of a statistical approach for soil recycling through the prediction of BaP, DahA and total PAH (${\Sigma}PAH$) concentrations from BaA concentration. As results of regression, excellent linear correlations ($R^2$ > 0.90) were observed between BaA and BaP (or DahA) concentrations. When a developed prediction equation was applied to other investigations as a validation study, good prediction results were obtained. The predictive model showed very good correlation between the measured and calculated BaP. From this equation, BaA was an apparently important hydrocarbon for the prediction of PAHs. This model might provide a potentially useful tool for the calculation of average BaP, DahA and ${\Sigma}PAH$ without additional tests.

No-tillage Agriculture of Korean-Type on Recycled Ridge I. Changes in Physical Properties : Soil Crack, Penetration Resistance, Drainage, and Capacity to Retain Water at Plastic Film Greenhouse Soil by Different Tillage System (두둑을 재활용한 한국형 무경운 농업 I. 경운방법에 따른 시설재배 토양의 물리적 특성: 균열, 관입저항, 배수, 보수력 변화)

  • Yang, Seung-Koo;Jung, Woo-Jin
    • Korean Journal of Organic Agriculture
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    • v.24 no.4
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    • pp.699-717
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    • 2016
  • This study was carried out to investigate the effect of no-tillage on sequential cropping supported from recycling of first crop ridge on the growth of pepper plant and physical properties of soil under green house condition. 1. Degree of crack on soil by tillage and no-tillage Soil cracks found in ridge and not found in row. At five months of tillage, crack number and crack length in length ridge were 3 and 37~51 cm in tillage. Maximum width and maximum depth in length ridge were 30 mm and 15.3cm in tillage. Crack number and crack length in width ridge were 7.5 and 7~28 cm in tillage. Maximum width and maximum depth in width ridge were 29 mm and 15.3 cm in tillage. At a year of no-tillage, crack number and crack length in length ridge were 1.0 and 140~200 cm in tillage. Maximum width and maximum depth in length ridge were 18 mm and 30 cm in a year of no-tillage. Crack number and crack length in width ridge were 11 and 6~22 cm in a year of no-tillage. Maximum width and maximum depth in width ridge were 22 mm and 18.5 cm in a year of no-tillage. Soil crack was not found at 2 years of no-tillage in sandy Jungdong series (jd) soil. Soil crack was found at 7 years of no-tillage in clayish Jisan series (ji) soil. 2. Penetration resistance on soil Penetration resistance was increased significantly at no-tillage in Jungdong series (jd). Depth of cultivation layer was extended at no-tillage soil compared with tillage soil. Penetration resistance of plow pan was decreased at 1 year of no-tillage compared with than tillage soil. Penetration resistance was linearly increased with increasing soil depth at tillage in Jisan series (ji). Penetration resistance on top soil was remarkably increased and then maintained continuously at no-tillage soil. 3. Drainage and moisture content of soil Moisture content of ridge in top soil was not significant difference at both tillage and no-tillage. Moisture content of ridge in 20 cm soil was 14% at no-tillage soil and 25% at tillage soil. 4. Change of capacity to retain water in soil Capacity to retain water in top soil was not significant difference at 1 bar both tillage and no-tillage. Capacity to retain water in soil was slightly higher tendency in 1 year and 2 years of no-tillage soil than tillage soil. Capacity to retain water in soil was increased at 15 bar both tillage and no-tillage. Capacity to retain water in subsoil was slightly higher tendency at 1 bar and 3 bar in 2 years of no-tillage than tillage soil and a year of no-tillage soil.

시멘트를 이용한 지반개량 및 시멘트계 건설폐기물의 재활용에 의한 환경오염

  • Min, Soo-Hong;Moon, Se-Heum
    • Proceedings of the Korean Geotechical Society Conference
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    • 2008.10a
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    • pp.267-267
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    • 2008
  • 시멘트를 이용한 지반개량 및 시멘트계 건설폐기물을 (예, 폐콘크리트, 및 시멘트 개량토 등) 성토재로 재활용하는 경우 지반 환경에 미칠 수 있는 영향으로는 (1) 시멘트에 함유된 6가 크롬($Cr^{6+}$) 및 (2) 강알칼리 물질의 용출이 있을 수 있다. 특히 $Cr^{6+}$의 경우 인체에 치명적인 발암성물질로 알려져 있어 이에 따른 주의가 필요하다. 최근 일본에서는 시멘트의 $Cr^{6+}$에 의한 지반오염이 우려됨에 따라 2000년 시멘트계 고화재를 지반에 사용하는 경우와 개량된 토양을 재이용하는 경우에는 토양환경기준을 만족하도록 규제하고 있다. $Cr^{6+}$외의 시멘트계 물질에 의한 환경오염으로는 강알칼리 물질의 유출이 있을 수 있다. 시멘트 개량토나 폐콘크리트 등의 건설폐기물을 성토재로 재활용하는 경우, 강우의 유입에 따라 구성물질인 수산화칼슘이 용해되어 높은 pH의 유출수가 발생한다. 강알칼리 유출수가 주변 하천 등으로 유입되는 경우 심각한 환경문제를 유발할 수 있으므로 이에 대한 기술적 검토가 필요하다. 본 발표에서는 시멘트계 물질에 의한 일본의 지반환경오염 사례 및 대책을 소개하였다.

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Study on the Support Policy for Recycling Food Wastes into Feed & Compost (음식물류 폐기물의 사료화 및 퇴비화 등 자원화 지원정책에 관한 연구)

  • Ahn Sang-Sun
    • Journal of Soil and Groundwater Environment
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    • v.10 no.3
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    • pp.52-63
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    • 2005
  • Korea has recently implemented two m메or policies on organic wastes, including food wastes. One is the Volume-Based waste Fee System (VBWFS). which went effect nationwide in January 1995, and the other is a ban on the landfill of organic wastes, such as food wastes. organic sludge, and animal manure, in accordance with the Waste Management Act. These two policies have brought about remarkable positive effects, including the reduction of organic wastes at source, and the development of technology for recycling food wastes into feed and compost. However, they have caused obstacles to carry out the policy on food wastes, in areas of legal and technological infrastructures for recycling. Therefore, this study intends to find problems of policies for recycling food wastes, and to suggest ways to resolve them.

No-Tillage Agriculture of Korean-Style on Recycled Ridge III. Changes in Pepper Growth and Biodiversity at Plastic Film Greenhouse Soil in Organic Cultivation of No-tillage Systems (두둑을 재활용한 한국형 무경운 농업 III. 시설 무경운 유기재배 고추의 생육 및 생물다양성의 변화)

  • Yang, Seung-Koo;Shin, Kil-Ho;Kim, Sun-Kook;Kim, Do-Ik;Han, Yeon-Soo;Jung, Woo-Jin
    • Korean Journal of Organic Agriculture
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    • v.25 no.1
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    • pp.71-84
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    • 2017
  • Hot pepper growth in no-tillage cultivation on recycled ridge was increased by 22% compared with tillage cultivation. At 3 years after no-tillage cultivation, hot pepper growth was increased by 12% compared with tillage cultivation. Dry weight of unripe hot pepper at 2 years of no-tillage cultivation was 348.4 kg/10a increasing 16% compared with tillage cultivation while dry weight of unripe hot pepper was decreased at 3 years of no-tillage cultivation. Bacteria flora at 2 years of no-tillage cultivation was significantly increased compared with tillage cultivation. Bacteria flora was not significantly different at 3 years of no-tillage cultivation. Actinomyces flora at 2 years of no-tillage cultivation was significantly increased compared with tillage cultivation. Actinomyces flora was decreased at 3 years of no-tillage cultivation. Fungi flora at 2 and 3 years of no-tillage cultivation was increased by 1.3 and 1.7 times respectively, compared with tillage cultivation. Generation amount of carbon dioxide at no-tillage cultivation soil was remarkably decreased by 41% compared with tillage cultivation. Population of animalcule in early stage of hot pepper soil was 2 species and 6 individuals on Collembola and Acari at tillage cultivation. Population of animalcule in hot pepper soil was 5 species and 11 individuals including Chilopode at one year of no-tillage cultivation. Population of animalcule in hot pepper soil was 3 species and 5 individuals including Coleoptera and Chilopode at 2 years of no-tillage cultivation. Population of animalcule was 4 species and 40 individuals including Hypogastrurigae and 8 species and 97 individuals including Earwig (Labidura japornica) at 46 days after transplanting on tillage cultivation. Population of animalcule was 9~10 species and 101~107 individuals on no-tillage cultivation. Nature status for environmental change as index organism was 19 points and 33 points, at tillage and no-tillage cultivation, respectively. These results indicate that no-tillage agriculture of korean-style on recycled ridge plays a very important roles on pepper growth, biodiversity of animalcule, and greenhouse gases at plastic film greenhouse soil in no-tillage systems.

토양세척공법을 적용한 유류오염토양 정화 사례

  • Sin Jeong-Yeop;Gong Jun;Kim Geon-U;Jeon Gi-Sik;Hwang Jong-Sik
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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    • 2006.04a
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    • pp.45-48
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    • 2006
  • 혼합유류(등,경유)로 오염된 대상부지의 토양특성을 파악하여 세척공법의 적용성을 판단하고, 적용성시험을 통하여 장치별 설계인자를 도출하였다. 시험결과 본 세척대상토양의 경우 계면활성제와 같은 첨가제를 주입하지 않고 물리적인 탈착공정만을 거쳐도 90%이상의 오염물질이 토양입자표면으로부터 탈착됨을 알 수 있었으며, 이를 반영하여 장치를 제작, 설치하였다. 세척대상 오염토량은 총 $12,225m^3$, 사업수행기간은 약 6개월, 세척장치에 주입된 세척토양의 평균오염농도는 약 3,152ppm 이었으며 세척 완료된 토양의 평균농도는 약 150ppm으로 약 97%의 제거효율을 보여 복원목표인 800ppm을 만족시킬 수 있었다. 그리고, 세척토양의 입도분포를 정확히 파악하고 분리시킬 토양입자 크기를 결정하여 현장 적용한 결과 세척공법으로부터 배출되는 응집슬러지를 최소화할 수 있었으며, 발생되는 세척폐수 또한 세척수 처리시스템을 거쳐 재활용 할 수 있도록 하였다. 이런 결과를 통하여 세척공법이 다른 Ex-situ 공법과 비교하였을 경우 현장의 적용성, 경제성, 복원기간 등을 감안하였을 경우 성공적인 세척공법의 적용사례라 할 수 있다.

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Chemical Remediation and Recirculation Technologies of Wastewater from Metal-Contaminated Soil Washing (금속오염(金屬汚染) 토양세척(土壤洗滌) 폐수(廢水)의 화학적(化學的) 처리(處理)와 재순환(再循環) 기술(技術))

  • Lim, Mi-Hee;Abn, Ji-Whan
    • Resources Recycling
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    • v.20 no.3
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    • pp.28-39
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    • 2011
  • This review investigated theoretical principals and practical application examples on recirculation system of soil washing-wastewater treatment-treated water recycling. As for technologies which have attempted to remediating metals-contaminated soil in and around country, there are reactive barriers, encapsulation, solidification/stabilization, soil washing, and phytoremediation. Among those, in particular, this review covers soil washing technology which physicochemically removes contaminants from soils. The major drawbacks of this technology are to generate a large amount of wastewater which contains contaminants complexed with ligands of washing solution and needs additional treatment process. To solve these problems, many chemical treatment methods have been developed as follows: precipitation/coprecipitation, membrane filtration, adsorption treatment, ion exchange, and electrokinetic treatment. In the last part of the review, recent research and field application cases on soil washing wastewater treatment and recycling were introduced. Based on these integrated technologies, it could be achieved to solve the problem of soil washing wastewater and to enhance cost effective process by reducing total water resources use in soil washing process.

저수지 퇴적물 재활용을 위한 처리장치에 관한 연구

  • 박진홍;조영민;오종민
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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    • 2002.04a
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    • pp.338-341
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    • 2002
  • This work is the basis research to apply Hydrocyclone for the separation and the thickening to the reservoir sediment. Chemical analysis result showed that organic contaminants were abundantly found in smaller sediment particles. As a result of the experiment device that higher reduced efficiency was obtained under the high velocity and low concentration with the small cyclones.

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Evaluating Possibility of Heavy Metal Accumulation by Fly Ash Application in Rice Paddy Soils (논토양에서 석탄회시용에 따른 중금속 축적가능성 평가)

  • Hong, Chang-Oh;Lee, Chang-Hoon;Lee, Hyup;Lee, Yong-Bok;Kim, Pil-Joo
    • Korean Journal of Environmental Agriculture
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    • v.25 no.4
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    • pp.331-338
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    • 2006
  • Coal combustion fly ash, which has a high available Si content and alkaline pH, was selected as a potential source of soil amendment in this study. Two field experiments were carried out to evaluate the possibility of heavy metal accumulation in silt loam (Pyeongtaeg series) and loamy sand (Nagdong series) of rice (Oryza sativa) paddy soils to which 0, 40, 80, and $120Mg\;ha^{-1}$ of fly ash were added. Rice yields increased significantly with fly ash application and the highest rice yields were achieved following the addition of around $90Mg\;ha^{-1}$ fly ash. Fly ash increased the soil pH but did not increase heavy metal uptakes of rice and heavy metal concentration in soils, due to very low concentration of heavy metals in the selected fly ash. Labile fraction of heavy metals (exchangeable + acidic fraction) was scarcely contained and most of them were stable and unavailable form (oxidizable and residual fraction). In conclusion fly ash could be a good supplement to an inorganic soil amendments without heavy metal contamination in paddy soils.