Forced triboelectrification of fine powders in particle wall collisions

Triboelectric separation as an inexpensive and environmentally friendly technique could contribute to material-specific sorting. However, the application as a widespread method is limited due to the complexity of the process. In particle wall collisions, various parameters like collision energy and angle, work function of the contact partners, humidity, surface roughness, etc. influence the particle charging in a hardly predictable way. This study investigates the possibilities of forced triboelectric particle charging by applying an electrical potential to the metal contact partner (copper/steel pipe). The variations included different pipe lengths (0.5 m–3 m), particle materials, and particle sizes for limestone. A distinction is made between the net charge of the particles and the positive, negative, and neutral mass fractions. The work functions of the investigated materials vary from about 3.2 eV to >8.5 eV for glass, limestone, artificial slag, and lithium aluminate particles. With the applied high-voltage potential, the particle net charge can be shifted linearly. For limestone, it is shown that the neutral fraction is highest at the Point of Zero Net Charge (PZNC). This observation may identify an approach for the material selective separation of one target component from a multi-material mixture

Results of the Cooperative Uniform Soybean Nurseries

United States Department of Agriculture Bureau of Plant Industry, Cooperating with Bureau of Agricultural Chemistry and Engineering, and the State Agricultural Experiment Stations Of The North Central Region

The Role of RNA Editing in Cancer Development and Metabolic Disorders

Numerous human diseases arise from alterations of genetic information, most notably DNA mutations. Thought to be merely the intermediate between DNA and protein, changes in RNA sequence were an afterthought until the discovery of RNA editing 30 years ago. RNA editing alters RNA sequence without altering the sequence or integrity of genomic DNA. The most common RNA editing events are A-to-I changes mediated by adenosine deaminase acting on RNA (ADAR), and C-to-U editing mediated by apolipoprotein B mRNA editing enzyme, catalytic polypeptide 1 (APOBEC1). Both A-to-I and C-to-U editing were first identified in the context of embryonic development and physiological homeostasis. The role of RNA editing in human disease has only recently started to be understood. In this review, the impact of RNA editing on the development of cancer and metabolic disorders will be examined. Distinctive functions of each RNA editase that regulate either A-to-I or C-to-U editing will be highlighted in addition to pointing out important regulatory mechanisms governing these processes. The potential of developing novel therapeutic approaches through intervention of RNA editing will be explored. As the role of RNA editing in human disease is elucidated, the clinical utility of RNA editing targeted therapies will be needed. This review aims to serve as a bridge of information between past findings and future directions of RNA editing in the context of cancer and metabolic disease

Protecting the Health of First Nation Personnel at Contaminated Sites: A Case Study of Mid-Canada Radar Line Site 050 in Northern Canada

Recently, First Nation (FN) organizations have entered into agreements with federal and provincial government representatives to remediate radar-line sites in Ontario. These agreements stipulated that FN people would take part in the site delineation and remediation process to gain job experience and economic benefits. One important aspect of the process was protecting FN personnel from contaminant exposure and thus, from potential negative health outcomes associated with the cleanup work itself. In this paper, we describe the safety precautions used by FN workers preparing Mid-Canada Radar Line (MCRL) Site 050 for Phase 2 of the delineation process and the health monitoring protocol that was tested. We measured concentrations of total polychlorinated biphenyls (PCBs as Aroclor 1260), 14 individual PCB congeners, p,p’-DDT, p,p’-DDE, nine other organochlorine pesticides, and lead in the blood of Fort Albany FN workers before they started work at Site 050 and approximately a week before they completed their three-month work period in the contaminated zone. No significant differences were found in the paired samples. These results indicate that the safety precautions taken were adequate for the work and the site in question. The monitoring protocol discussed here may be used as a template and modified to meet the specific needs of other projects. The results of this study are important because other Aboriginal groups have entered or will be entering into agreements with government organizations for the remediation of other MCRL sites in Ontario and across Canada.Les stations de ligne radar désaffectées situées tant dans l’Arctique que dans le Subarctique canadiens seraient des sources ponctuelles de contamination. Des organismes des Premières nations ont participé dernièrement, avec des représentants des gouvernements fédéral et provinciaux, à des accords visant l’assainissement des stations de ligne radar en Ontario. Ces accords stipulaient que des membres des Premières nations prendraient part à la délimitation des sites et au processus d’assainissement afin d’acquérir de l’expérience de travail et de profiter des retombées économiques. Un volet important de ce processus visait à protéger le personnel autochtone de l’exposition aux contaminants et donc, d’effets potentiels négatifs pour la santé associés aux opérations de nettoyage mêmes. Dans cet article, on décrit les mesures de sécurité utilisées par les travailleurs autochtones oeuvrant sur le site 050 de la ligne radar Mid-Canada durant la phase 2 du processus de délimitation, ainsi que le protocole de contrôle de la santé mis alors à l’essai. On a mesuré les concentrations de l’accumulation de diphényles polychlorés (PCB comme l’Arochlore 1260), de 14 congénères de PCB, de p,p’-DDT, de p,p’-DDE, de neuf autres pesticides organochlorés ainsi que de plomb dans le sang des travailleurs autochtones de Fort Albany avant qu’ils commencent à travailler au site 050 et une semaine environ avant qu’ils terminent leur période de travail de trois mois dans la zone contaminée. On n’a pas trouvé de différences significatives entre les échantillons appariés. Ces résultats révèlent que les mesures de sécurité prises étaient adéquates pour le travail et le site en question. Le protocole de contrôle discuté ici pourrait servir de modèle et être adapté pour répondre aux critères spécifiques d’autres projets. Les résultats de cette étude sont importants car d’autres groupes autochtones participent actuellement ou vont participer à des accords avec des agences gouvernementales visant l’assainissement d’autres sites de la ligne radar Mid-Canada en Ontario et à travers le Canada