Activated carbon (AC) is used for filtering organic and radioactive particles, in liquid and ventilation systems, respectively. Spent ACs (SACs) are stored till decaying to clearance level before disposal, but some SACs are found to contain C-14, a radioactive isotopes 5,730 years halflife, at a concentration greater than clearance level concentration, 1 Bq/g. However, without waste acceptance criteria (WAC) regarding SACs, SACs are not delivered for disposal at current situation. Therefore, this paper aims to perform a preliminary disposal safety examination to provide fundamental data to establish WAC regarding SACs SACs are inorganic ash composed mostly of carbon (~88%) with few other elements (S, H, O, etc.). Some of these SACs produced from NPPs are found to contain C-14 at concentration up to very-low level waste (VLLW) criteria, and few up to low-level waste (LLW) criteria. As SACs are in form of bead or pellets, dispersion may become a concern, thus requiring conditioning to be indispersible, and considering VLL soils can be disposed by packaging into soft-bags, VLL SACs can also be disposed in the same way, provided SACs are dried to meet free water requirement. But, further analysis is required to evaluate radioactive inventory before disposal. Disposability of SACs is examined based on domestic WAC’s requirement on physical and chemical characteristics. Firstly, particulate regulation would be satisfied, as commonly used ACs in filters are in size greater than 0.3 mm, which is greater than regulated particle size of 0.2 mm and below. Secondly, chelating content regulation would be satisfied, as SACs do not contain chelating chemicals. Also, cellulose, which is known to produce chelating agent (ISA), would be degraded and removed as ACs are produced by pyrolysis at 1,000°C, while thermal degradation of cellulose occurs around 350~600°C. Thirdly, ignitability regulation would be satisfied because as per 40 CFR 261.21, ignitable material is defined with ignition point below 60°C, but SACs has ignition point above 350°C. Lastly, gas generation regulation would be satisfied, as SACs being inorganic, they would be targeted for biological degradation, which is one of the main mechanism of gas generation. Therefore, SACs would be suitable to be disposed at domestic repositories, provided they are securely packaged. Further analysis would be required before disposal to determine detailed radioactive inventories and chemical contents, which also would be used to produce fundamental data to establish WAC.

The aim and originality of our current study are to use the original biomass (activated carbon) obtained by functionalizing waste banana peels (commonly found in Turkey) with acid in NaBH4 methanolysis and to examine its contribution to the hydrogen generation rate (HGR). Our study consisted of three stages. In the first stage, the optimum conditions were determined by examining the catalyst under parameters such as different acid types, different carbonization temperatures, and different carbonization times. Thus, based on the maximum HGR value, the optimum conditions were determined as H3PO4, 600 °C, and 40 min. In the second step, the effects of parameters such as acid concentration, NaBH4 concentration, catalyst amount, and temperature on HGR were investigated. As a result of methanolysis experiments (condition: catalyst amount: 100 mg, acid amount: 30%, NaBH4 concentration: 2.5%, temperature: 30 °C, carbonization temperature: 400 °C, and carbonization time: 40 min.), the maximum HGR value, the reaction completion time and activation energy were found as 65,625 mLmin− 1gcat−1, 0.233 min, and 4.56 kJ/mol, respectively. It was observed that the obtained activation energy was lower than that of some catalysts available in the literature. In addition, the structural and morphological examination of the banana peel (catalyst) with high HGR and low activation energy revealed that the acid functionalization process was successfully carried out.

As Kori-1 permanently shut down in Korea, it is expected that a large amount of radioactive waste will be generated during decommissioning of nuclear power plants. Radioactive concrete waste is contaminated up to depth of 100 mm with radionuclides such as 137Cs and 60Co. The radioactive waste should be accurately classified to reduce the cost of disposing of radioactive waste. Therefore, the specific radioactivity of waste must be precisely evaluated by gamma-ray measurements emitted from the radionuclides. In general, the effectiveness of the radioactivity measurement and process is confirmed using certified reference material (CRM) composed of water or agar. However, the decommissioning waste differs from this CRM in apparent density and chemical elements, so the specific radioactivity is underestimated or overestimated. Therefore, reference material composed of the same apparent density and chemical elements as the sample is required to improve the quality of radioactivity measurement. The purpose of this study is to develop a concrete reference material for the nuclear decommissioning waste. The concrete reference material composed of SiO2, CaO, and Al2O3 were manufactured in compliance with ISO Guide 35. 10 bottles were randomly selected for homogeneity test, and 2 samples for analysis were taken from each bottle. The specific radioactivity was measured using an HPGe detector with an efficiency of 30%. The results of the homogeneity test of 137Cs and 60Co satisfied the requirements of ISO Guide 35. Coincidence summing and selfabsorption effects were corrected using the Monte Carlo efficiency transfer code and Monte Carlo NParticle transport code. The reference values of 137Cs and 60Co in the concrete reference material were evaluated in the range of 1,000–1,100 Bq·kg−1 and extended uncertainty was around 7%.

Plastic waste is becoming a problem in various countries because of the difficulty of natural decomposition. One type is PET plastic(Polyethylene Terephthalate), which is often used as a bottle for soft drink packaging, and LDPE(Low Density Polyethylene), which is also widely used as a food or beverage packaging material. The use of these two types of plastic continuously, without good recycling, will have a negative impact on the environment. Building material waste is also becoming a serious environmental problem. This study aims to provide a solution to the problem of the above plastic waste and building material waste by making them into a mixture to be used as bricks. Research is carried out by mixing both materials, namely plastic heated at a temperature of 180-220oC and building material waste that had been crushed and sized to 30-40 mesh with homogeneous stirring. The ratios of PET and LDPE plastic to building material waste are 9 : 1, 8 : 2, 7 : 3, 6 : 4 and 5 : 5. After heating and printing, density, water absorption and compressive strength tests are carried out. Addition of PET and LDPE plastic can increase compressive strength, and reduce water absorption, porosity and density. A maximum compressive strength of 10.5 MPa is obtained at the ratio of 6 : 4.

본 연구는 사용 후 핵연료의 금속전환 공정에서 발생되는 폐용융염을 고형화하는 방법으로 실리카 함유 무기물을 이용하여 폐용융염을 열적, 수화학적 안정한 화합물로 전환하는 방법을 제안하였다. 실리카 함유 무기물(SAP)은 일반적인 sol-gel process로 합성되었으며, 및 로 구성된다. 제조된 SAP을 에서 폐용융염과 반응시켜 각 금속염화물에 대한 반응특성 및 열안정성을 조사하고, PCT 침출시험법을 이용하여 수화학적 안정성을 평가하였다. LiCl은 와 로, CsCl는 CS-aluminosilicate와 로, 는 로, 는 로 전환되었다. 9시간 동안 반응시킨 후, 금속염화물의 전환율은 였으며, 까지 열감량은 1wt%이하로 TGA(Thermo Gravimetric Analysis)로 확인하였다. Cs 및 Sr의 침출속도는 로 매우 높은 내침출특성을 나타내었다. 이상의 결과로부터, SAP으로 명명된 안정화제(stabilizer)는 금속염화물로 구성된 폐용융염에 대해 매우 효과적인 것으로 판단된다. SAP을 이용한 폐용융염의 고화처리방법은 후속적인 안정성의 검증과정을 통하여 폐용융염의 최종처분부피를 최소화할 수 있는 대안적인 고화방법으로 고려될 수 있을 것으로 기대 된다.

To prevent environmental pollution caused by leakage of leachate from waste landfill, vinyl acetate-ethylene (VAE) resin is applied to liner and cover materials to improve their performance. Styrene, styrene butadiene rubber, and VAE are widely used as polymer resins that have excellent water resistance and durability. Further, VAE resin is known to have additional advantages such as adhesion to nonpolar materials and resistance to saponification as a copolymer. In this study, the effect of VAE content on the properties of liner and cover materials was studied. The water and air content ratios, bending and compressive strengths, water absorption ratio, and coefficient of permeability of these materials were measured. The liner and cover materials with 4 wt% VAE showed good properties.

Since the Framework Act on Resource Circulation was enacted in 2018, the government should establish a National Resource Circulation Master Plan every 10 years, which defines mid- to long-term policy goals and directions on the efficient use of resources, prevention of waste generation and recycling of waste. In addition, we must set mid- to longterm and stepwise targets for the final disposal rate, recycling rate (based on sorted recyclable materials and recycled products), and energy recovery rate of wastes, and relevant measures should be taken to achieve these targets. However, the current industrial waste (IW) statistics have limitations in setting these targets because the final disposal rate and recycling rate are calculated as the ratio of the recycling facility input to the IW generation. In this study, the material flow from the collection stage to the final disposal of industrial waste was analyzed based on the generation of 2016, and the actual recycling amount, actual incineration amount, final disposal amount and their rates were calculated. The effect on the recycling, incineration and final disposal rates was examined by changing the treatment method of nonhazardous wastes from the factory and construction and demolition wastes, which were put in landfills in 2016. In addition, the variation of the waste treatment charge was investigated according to the change of treatment methods. The results of this study are expected to be effectively used to establish the National Resource Circulation Master Plan and industrial waste management policy in the future in South Korea.

폐기물은 발생원을 기준으로 생활폐기물, 사업장폐기물 및 건설폐기물로 구분된다. 폐기물 처리는 재활용을 우선적으로 정책이 이루어지고 있다. 그러나 폐기물을 재활용하기 위해서는 기술적인 한계성과 경제성 등이 해결되어야 하며 이러한 이슈가 극복되지 않으면 재활용에는 한계가 따른다. 국내에서 도입된 네가티브 재활용 제도가 다양한 기술을 재활용로서 적용될 수 있도록 하였으며, 그 중 폐기물 에너지화 기술로써만 인식되어온 폐기물 가스화 기술은 에너지회수 기술 뿐 만 아니라 원료를 대체할 수 있는 재활용 기술로도 적용될 수 있게 되었다. 폐기물의 재활용은 물질재활용 기술로서 3R기술 위주로 재활용되어 왔으나 화학전환 기술에 의한 재활용을 위해서는 가스화 기술이 많은 기여를 할 것으로 기대된다. 또한 폐기물의 에너지 회수기술은 소각에 의한 에너지회수 또는 고형연료를 생산하여 연소보일러에 의한 에너지회수 방법이 주로 이용되어 왔으며 이러한 기술은 열에너지를 회수하는 기술에 국한되어 있다. 그러나 폐기물 가스화 기술은 열에너지와 화학에너지의 생산이 가능하므로 다양한 에너지로의 회수 기술과 고효율 에너지 이용기술의 적용이 가능한 기술이다. 따라서 본 연구에서는 폐기물 가스화를 통한 에너지회수 기술과 화학전환 기술로서 원료대체를 통한 재활용 기술로서의 특성을 고찰하였다. 폐기물 가스화 기술은 가연성물질이 함유된 폐기물의 대부분을 대상으로 적용이 가능하지만 합성가스를 이용하는 기술에 따라서 합성가스의 생산품질을 만족하기 위해서는 폐기물의 적정 발열량이 확보되어야 된다. 폐기물의 종류에 따라 기준은 달리 적용되겠지만 저위발열량 기준으로 3,200 kcal/kg이상인 경우 안정적인 합성가스를 생산할 수 있다고 판단되며, 폐기물종류 및 이용기술에 따라서는 3,000 kcal/kg이상인 경우 합성가스 생산품질을 유지할 수 있다. 폐기물 가스화를 통해 생산된 합성가스를 에너지회수 기술로서는 스팀터빈, 가스터빈, 가스엔진, 연료전지 등의 기술을 적용할 수 있고, LNG, 경우, 석탄, LPG 등 화석연료를 대체하는 가스연료로 적용할 수도 있다. 또한 합성가스의 주요성분인 일산화탄소와 수소는 고순도 수소 및 고순도 일산화탄소 자체로도 원료대체가 가능하며, 화학촉매 또는 미생물촉매 전환 공정을 통해 다양한 화학원료로 대체하는 재활용기술로서의 적용이 가능한 특성을 가지고 있다.

In order to promote the resource circulation and upcycling of waste refrigerators, it is necessary to analyze the material flow of recovered valuable resources and low-value residues after they are discharged. This study divided the flow of waste refrigerators into the five steps of discharge, collection, pretreatment, resource recovery, and sale/export/disposal and conducted material flow analysis (MFA) in each step. Waste refrigerators are treated via official (formal sectors, 65.6% of total amount) and unofficial (informal sectors, 34.4% of total amount) channels. Officially, waste refrigerators are collected through free collection by national and local governments, recovery by product producers and distributors, and waste collection·transportation·recycling companies and are recycled at public and private recycling centers. Unofficially, waste refrigerators are collected through junk shops and individual collectors. Waste refrigerators recycled in the formal sectors undergo pretreatment processes such as the disassembly, shredding, and separation and recovery of resources such as scrap irons, plastics, PCB (printed circuit board), cables, glasses, waste refrigerants, urethane, etc. Waste refrigerators recycled in informal sector treated through disassembly of the exterior, the shredding process by the excavators in illegal facilities and recovered waste refrigerants, plastics, glasses, scrap irons, copper, nickel silver, PCB, urethane, etc. MFA results show that in 2015, the amount of waste refrigerators collected from formal sectors reached 121,642 ton/year, the amount of recycling was 107,684 ton/year, and the amount of residues was 13,955 ton/year respectively. Thus, actual recycling rate per a waste refrigerator was estimated 88.15% in 2015. To promote the resource circulation and upcycling of waste refrigerators, it is necessary to find a way to improve the recycling of urethane, which accounts for 10.8% of the total weight of a refrigerator.

최근 환경오염을 방지하고 자원소비를 절감할 수 있는 ‘자원순환사회’로의 전환을 서둘러야 한다는 공감대가 빠르게 확산되고 있으며, ‘자원순환사회’란 폐기물의 소각, 매립을 최소화하고 재활용을 극대화함으로써 환경오염을 방지하고 자원과 에너지를 절약이 큰 이슈화 되고 있는 실정이다. 리튬 이차전지 생산과정 중 전구체 제조공침 기술에서 암모니아수를 사용하게 되며, 공정 중 발생하는 암모니수에 질소제거를 위한 스트리핑법을 이용하여 최종 황산암모늄 수용액이 부산물로 발생 하고 있다. 황산암모늄 폐수 처리시 T-N이 함유되어 고도처리를 해야 하므로 고가의 폐수처리 발생비용 발생 되고 있는 실정이다. 현재 구미산업공단 및 경북 산업단지 내의 매월 약 150톤의 폐황산암모늄이 발생되어 지고 있으며, 주로 고가의 폐수비용을 지불하며 고도처리 방식으로 처리되고 있다. 따라서. 황산암모늄 폐수 활용하여 폐수비용을 경감시키고 부가가치를 창출 할 수 있는 기술에 대하여 관심이 높아지고 있다. 구미산업공단 및 경북 산업단지내의 매월 약 150톤의 폐황산암모늄이 발생되어 지고 있으며, 주로 고가의 폐수비용을 지불하며 고도처리 방식으로 처리되고 있어 환경오염 및 비용이 문제가 점차 확대되고 있는 실정이다. 따라서 본 연구에서는 전지소재 공정에서 발생되는 폐수를 이용하여 황산암모늄 정제기술 및 최적 결정화방법을 개발하였다. 이를 활용하여 폐수 발생량을 줄일 수 있으며, 처리비용을 절감시키는 효과를 통하여 자원순환화 할 수 있을 것으로 사료된다.