Adsorption of dibenzothiophene (DBT) and 4,6-dimethyldibenzothiophene (4,6-DMDBT) from solutions in hexane and hexadecane respectively as well as in acetonitrile for both thiophenic compounds was investigated with sorbents of three activated carbons and their oxidized counterparts. The raw sorbents were of different surface acidity. Oxygen surface groups created after oxidation increased the adsorption of thiophenic compounds via polar interactions.Cesium and cobalt radioactive isotopes (134Cs and 60Co) are dangerous to human health due to their long half-life about 2.1 and 5.3 year, respectively. Developing a new composite used as an efficient sorbent for these is an urgent requirement for radioactive waste management. Herein, preparation of different materials such as aluminum silicate (AS), cultured of Chlorella vulgaris (NCV) alga, and aluminum silicate/Chlorella vulgaris (AS/NCV) composite 31 were prepared by wet chemical technique and used to remove the 134Cs and 60Co radionuclides. Different analytical techniques were used to characterize the prepared sorbents as SEM, TEM, XRD, BET, TGA/DTA, FTIR particle size analyzer, and pore size distribution. The factors affecting the sorption process as pH, temperature, contact time, and weight of adsorbent were studied. The sorption process was found to follow a pseudo-second-order mechanism. The monolayer capacity for 134Cs radionuclide onto the aluminum silicate, non-living Chlorella vulgaris biomass, and aluminum silicate/Chlorella vulgaris composites are 66.67, 83.54, and 90.11 mg/g, respectively, and for 60Co radionuclide are 59.31, 91.99, and 99.24 mg/g, respectively. The values of thermodynamic parameters indicate that the sorption process is endothermic and spontaneous.Antimicrobial resistance (AMR) is a growing threat that causes over 700,000 deaths per year worldwide. The goal of the current multicenter, cross-sectional study was to identify the knowledge and practice gaps in antimicrobial stewardship among Egypt's undergraduate medical students. Nine-hundred and sixty-three participants (375 male) from 25 medical schools responded to our self-administered questionnaire. Overall, the majority of students (96%) exhibited fair/satisfactory knowledge and attitude scores towards AMR. However, the most common misconceptions were that skipping one or two antimicrobial doses does not contribute to AMR (43%) and that antimicrobials are the drug of choice for the treatment of sore throat (38.8%). About 36% of the students thought that bacteria cause common cold and influenza. In terms of practices, about 62% of the students reported taking antibiotics when they have cough or sore throat and saving the remaining antibiotic for the next time. About 48% of the students reported that when they start feeling better, they stop the antibiotic course, and 41% stated that they often/sometimes discard the remaining leftover or share the leftover antibiotics with their friends. Interestingly, males had more frequently poorer levels of knowledge than females (p = 0.02). Moreover, students in the clinical science years (p less then 0.001), living in urban areas (p = 0.02) or Cairo (p less then 0.01) reported better practices than their counterparts. Educational programs about antimicrobial stewardship and the role of healthcare professionals in preventing AMR should be introduced early in medical curricula. Further, active educational techniques as clinical scenarios that simulate clinical settings and interactive learning workshops would be more efficient teaching methods.Both the epidemiological and animal experimental studies have reported the association between PM2.5 and respiratory, cardiovascular, and metabolic diseases. However, the study linking PM2.5 and hepatic injury is few, and the relative mechanism has not been fully elucidated. Thirty-two 6-week-old male C57BL/6 mice were exposed to filtered air (FA) or concentrated PM2.5 for 12 weeks using Shanghai Meteorological and Environmental Animal Exposure System ("Shanghai-METAS"), respectively. At week 11, the mice began to be treated with intraperitoneal injection of normal 0.9% saline or AMPK activator (AICAR). The mRNA levels of IL-6 and TNF-α, and protein expressions of AMPK, GLUT4, NF-κB, p38MAPK, ERK, and JNK in the liver and UCP-1 in brown adipose tissue (BAT) were measured. Meanwhile, histopathological examination both in the liver and BAT was performed to evaluate the histopathological changes. PM2.5 exposure induced steatosis, hepatocyte ballooning, lobular and portal inflammation in the liver, and the brown adipocyte swelling in BAT. The results found that PM mice displayed higher IL-6, TNF-α, NF-κB, and JNK expression and lower AMPK, GLUT4, and UCP-1 when compared with FA mice. The AICAR injection upregulated the expressions of GLUT4 in the liver of PM-AIC mice when compared with the PM mice. However, there were no significant effects of AICAR on histopathological condition. The current study showed that ambient PM2.5 exposure might induce the hepatic injury along with the lipid metabolism disorder in BAT. AMPK activation can ameliorate most of the harmful effects and might become the potential target for treating PM2.5-induced hepatic injury.Sulfadiazine (SDZ) residues have been detected in manured soils as well as their adjacent water resources, but its behavior is still poorly understood in acidic tropical soils. https://www.selleckchem.com/products/kaempferide.html This research aimed to evaluate sorption, leaching, and biodegradation of 14C-SDZ in four acidic soils from Brazil, using OECD guidelines. Except for the sand soil (Kd = 2.6 L kg-1), SDZ sorption tended to be higher (Kd > 8.4 L kg-1) and more hysteretic (ΔH >> 1) in acidic soils. When freshly applied, SDZ leaching was low ( 78% of AR up to 7 days). For certain acidic soils, the abrupt breakdown of the SDZ suggests that degradation should be initially chemical and then followed by enzymatically driven reactions. The fast formation of NERs was attributed mostly to chemical bounding to soil humic substances (Type II-NER), but SDZ sequestration cannot be ruled out (Type I-NER). NERs represent a long-term environmental reservoir of SDZ that may cause deleterious effects on non-target organisms as well as promote antibiotic resistance to soil microbes.