• Journal of Food Hygiene and Safety
• /
• v.21 no.4
• /
• pp.263-268
• /
• 2006

The purpose of this study was to monitor and compare the contamination levels of total aerobic bacteria, coliform groups and Escherichia coli from fruit-vegetable salad (FS), aquatic hard-boiled food (AF) and salt-fermented fishery product with spices (SP). The samples of ready-to-eat food were 25 FS, 11 AF and 7 SP. The contamination levels of total aerobic bacteria in FS, AF and SP were $4.56\sim7.45\;log_{10}$ CFU/g (FS), $2.43\sim7.03\;log_{10}$ CFU/g (AF), respectively. The contamination levels of coliform groups were $4.51\sim6.71\;log_{10}$ CFU/g (SP). $4.00\sim6.66\;log_{10}$ CFU/g (FS), $1.70\sim5.20\;log_{10}$ CFU/g (AF), respectively. The contamination levels of E. coli were $2.50\sim4.42\;log_{10}$ CFU/g (SP), $0\sim3.58\;log_{10}$ CFU/g (FS), $1.11\sim4.68\;log_{10}$ CFU/g (AF), respectively. The difference of completed packaging salad and instant packaging salad are not different about contamination levels. In conclusion, the results of this study indicated that the hygienic levesl of salads, hard-boiled foods and salted fishes were very poor. So our government need to improve the control plan for food safety from manufacturing process to market.

• Resources Recycling
• /
• v.32 no.1
• /
• pp.50-59
• /
• 2023

The amount of dust generated during the dissolution of scrap in an electric arc furnace is approximately 1.5% of the scrap metal input, and it is primarily collected in a bag filter. Electric arc furnace dust primarily consists of zinc and ion. The processing of zinc starts with its conversion into pellet form by the addition of a carbon-based reducing agent(coke, anthracite) and limestone (C/S control). These pellets then undergo reduction, volatilization, and re-oxidation in rotary kiln or RHF reactor to recover crude zinc oxide (60%w/w). Next, iron is discharged from the electric arc furnace dust as a solid called Fe clinker (secondary by-product of the Fe-base). Several methods are then used to treat the Fe clinker, which vary depending on the country, including landfilling and recycling (e.g., subbase course material, aggregate for concrete, Fe-source for cement manufacturing). However, landfilling has several drawbacks, including environmental pollution due to leaching, high landfill costs, and wastage of iron resources. To improve Fe recovery in the clinker, we pulverized it into optimal -sized particles and employed specific gravity and magnetic force selection methods to isolate this metal. A carbon-based reducing agent and a binding material were added to the separated coarse powder (>10㎛) to prepare briquette clinker. A small amount (1-3%w/w) of the briquette clinker was charged with the scrap in an electric arc furnace to evaluate its feasibility as an additives (carbonaceous material, heat-generating material, and Fe source).