In this work, α-Fe2O3 nanocrystals are synthesized by co-precipitation method and used as adsorbent to remove Cr6+, Cd2+, and Pb2+ from wastewater at room temperature. The prepared sample is evaluated by XRD, BET surface area, and FESEM for structural and morphological characteristics. XRD patterns confirm the formation of a pure hematite structure of average particle size of ~ 40 nm, which is further supported by the FESEM images of the nanocrystals. The nanocrystals are found to have BET specific surface area of ~ 39.18 m2 g−1. Adsorption experiments are carried out for the different values of pH of the solutions, contact time, and initial concentration of metal ions. High efficiency Cr6+, Cd2+, and Pb2+ removal occur at pH 3, 7, and 5.5, respectively. Equilibrium study reveals that the heavy metal ion adsorption of the α-Fe2O3 nanocrystals followed Langmuir and Freundlich isotherm models. The Cr6+, Cd2+, and Pb2+ adsorption equilibrium data are best fitted to the Langmuir model. The maximum adsorption capacities of α-Fe2O3 nanocrystals related to Cr6+, Cd2+, and Pb2+ are found to be 15.15, 11.63, and 20 mg g−1, respectively. These results clearly suggest that the synthesized α-Fe2O3 nanocrystals can be considered as potential nano-adsorbents for future environmental and health related applications.

포인세티아(Euphorbia pulcherrima Willd. Ex Klotzch) ‘Flame’ 은 국립원예특작과학원에서 2015년에 육성한 품종이다. ‘Flame’ 은 단일감응기간이 짧은 적색 포엽의 깊은 열편을 가진 ‘Eckalba’ 와 밝은 적색의 포엽을 가진 국내 육성 품종 ‘Candle Light’를 2013년에 교배하여 획득한 실생 계통을 선발 육성하였다. 2014 년부터 2015년까지 생육 및 개화 특성, 균일성에 대하여 1, 2차 특성검정을 실시하였으며, 2015년에 3차 특성검정을 실시하여 최종선발한 후 직무육성품종심의회에 상정하여 ‘Flame’으로 명명하였다. ‘Flame’ 품종의 포엽은 밝은 적색을 띠며 열편이 깊다. 초장과 초폭은 중간이나 적심하지 않아도 많은 분지가 발생하여 풍성한 수형을 이룬다. 단일처리후 약 7.5주가 경과하면 완전히 착색되어 출하가 가능하다. 이 품종은 2018년 1월 24일에 국립 종자원에 품종등록(등록번호 6921호)되었다.

본 실험은 장미의 삽목시 증산억제제와 생장억제제를 활용 하여 미스트나 밀폐시설 없이 삽목발근 효율을 증가시킬 목적으로 수행하였다. 절화장미 ‘M-Red’ 줄기 삽목 후 증산억제제 ‘Wilt Pruf’ 및 ‘Cloud Cover’ 1, 2, 4, 8%와 생장억제제 paclobutrazole 10, 20, 40, 80mg･L-1, diniconazole 100, 200, 400, 800mg･L-1를 각각 엽면살포 하였다. 증산억제제의 효과 는 종류에 따라 달랐는데, Wilt Pruf는 생존율, 신초 발생율, 발근율을 모두 향상시켰으나 신초수, 뿌리수, 뿌리길이에는 영향을 미치지 않았다. Cloud Cover는 생존율과 발근율을 향상시키는 효과가 없었으나 신초 발생율이 처리농도와 비례하여 높아져 4, 8% 처리시 가장 높게 나타났다. 생장억제제 처리효과도 종류에 따라 달라 paclobutrazol은 생존율과 발근율 향상에 영향을 미치지 않았으나 신초 발생율을 높였으며 1% 처리시에 신초발생이 가장 높았다가 농도가 높아지면서 낮아졌다. Diniconazole은 100, 200mg･L-1 처리시 생존율과 발근율을 향상시켰으나 800mg･L-1의 고농도에서는 생존율과 발근율 모두 낮게 나타났다.

Cryopreservation is used for blastocyst preservation of most mammalian embryos and is an important technique for breeding. We aimed to compare the efficiency of the cryopreservation method using the standard Cryotop device and the ReproCarrier device, a domestic product manufactured in Korea. The efficacy of the two devices was analyzed based on the survival rate, intracellular levels of reactive oxygen species (ROS), and apoptosis of the vitrified bovine blastocysts. The survival rates of the vitrified-warmed blastocysts were similar between the ReproCarrier group (58.4 ± 17.7%) and Cryotop group (59.9 ± 14.1%). Intracellular ROS levels and apoptotic index were determined by DCFDA staining and TUNEL assay. Changes in intracellular ROS levels, number of total nuclei, and cellular apoptosis of vitrified blastocysts after cryopreservation were not significantly different between the two groups. These results indicate that the ReproCarrier device method is as effective as the standard Cryotop method for vitrification of bovine blastocysts in vitro.

After the permanent shutdown of K1 in 2017, decommissioning processes have attracted great attention. According to the current decommissioning roadmap, the dismantling of the activated components of K1 may start in 2026, following the removal of its spent fuel. Since the reactor vessel (RV) and reactor vessel internal (RVI) of K1 contain massive components and are relatively highly activated, their decommissioning process should be conducted carefully in terms of radiological and industrial safety. For achieving maximum efficiency of nuclear waste management processes for K1, we present activation analysis of the segmentation process and waste classification of the RV and RVI components of K1. For RVI, the active fuel regions and some parts of the upper and lower active regions are classified as intermediate-level waste (ILW), while other components are classified as low-level waste (LLW). Due to the RVI’s complex structure and high activation, we suggest various underwater segmentation techniques which are expected to reduce radiation exposure and generate approximately nine ILW and nineteen very low level waste (VLLW)/LLW packages. For RV, the active fuel region and other components are classified as LLW, VLLW, and clearance waste (CW). In this case, we suggest in-situ remote segmentation in air, which is expected to generate approximately forty-two VLLW/LLW packages.