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Wood Drying Condensate Treatment Using a Bio – Trickling Filter with Bark Chips as a Support Medium

机译:使用生物点滴滤池和树皮屑作为支撑介质的木材干燥冷凝水处理

摘要

The kiln drying of wood produces huge amounts of vapour. The vapour is released to the environment when the process purges some of the saturated hot air. The main environmental issue regarding the use of kiln drying process are the release of the water vapour which contains organic contaminants. Some of them are hazardous to human health. In addition, there are some wood particles which may released with the water vapour purging process.In this research, the vapour is condensed and analysed for its organic contaminants and their biodegradability. The result showed that the dominant contaminants present in the condensate were ethanol and methanol with the concentration of approximately 65 mg/L and 25 mg/L respectively. The average COD concentration of the condensate was 159 ± 40 mg/L. The analysis also showed that the contaminants were biodegradable. In order to treat the wastewater, a trickling filter process using bark chips as a support medium was used to treat an artificial wastewater. The artificial wastewater contained the dominant contaminant present in the wood drying condensate. In the experiment, different sizes of bark chips were used. In addition, the loading rate of the treatment system was varied by changing the flow rate and contaminant concentration.The 30 cm long trickling filter using bark chips varying between of 2.8 – 4 mm diameter as the support medium gave a maximum removal of 36.4 % with removal capacity of 8.34 kg COD/m³bed•day at a flow rate of 2.8 cm/min and average inlet COD load of 20.4 kg COD/m3bed•day. The trickling filter with bark chips varying between 5.6 – 8 mm diameter as the support medium was operated using variations in contaminant concentration and flow rate. The operation using different inlet concentration gave the highest removal rate of 13.5 kg COD/m3bed•day at average initial load of 84.9 kg COD/m³bed•day, flow rate of 2.8 cm/min and theoretical initial concentration of 680 mg/L. The trickling filter operated with flow rate variation showed the highest removal rate of 10 kg COD/m³bed•day at an average inlet load of 53.3 kg COD/m³bed•day and flow rate of 7.1 cm/min.The removal rate of the contaminants in treatment was limited. There is a number of possible explanations. First is the active surface area, which indicating the area where the contact between the biofilm surface and feed happened. The active surface area increased as the flow rate increased. Second is the residence time of the feed in the bed. The residence time of the feed varied with the flow rate. It decreased as the flow rate increased. Third is the influence of the contaminants in the feed. The presence of methanol and methanol in the feed inhibited each other’s degradation.The dimention of a full-scale biotrickling filter to be used in actual kiln was also estimated. The estimation was made based on the maximum removal rate and optimum flow rate obtained in the experiments. The result of the estimation showed to obtain significant removal, the required bed would have to be 2.35 m in diameter and 160 in height.
机译:木材的窑干燥产生大量的蒸气。当该工艺吹扫一些饱和的热空气时,蒸气会释放到环境中。使用窑炉干燥过程的主要环境问题是释放出含有有机污染物的水蒸气。其中一些对人体健康有害。此外,在水蒸气吹扫过程中可能会释放一些木材颗粒。在本研究中,对蒸气进行冷凝并分析其有机污染物及其生物降解性。结果表明,冷凝物中存在的主要污染物是乙醇和甲醇,其浓度分别约为65 mg / L和25 mg / L。冷凝液的平均COD浓度为159±40 mg / L。分析还表明,污染物是可生物降解的。为了处理废水,使用以树皮屑为支撑介质的滴滤法处理人造废水。人造废水包含木材干燥冷凝物中存在的主要污染物。在实验中,使用了不同大小的树皮碎片。此外,通过改变流速和污染物浓度来改变处理系统的负荷率。30厘米长的滴滤池使用树皮屑作为支撑介质,直径在2.8 – 4 mm之间变化,最大去除量为36.4%。在2.8 cm / min的流速下,脱除能力为8.34 kg COD /m³·day,平均进口COD负荷为20.4 kg COD / m3·day•day。作为支撑介质,带有树皮屑的滴滤过滤器的直径在5.6 – 8 mm之间变化,这是通过污染物浓度和流速的变化来进行的。使用不同入口浓度的操作在平均初始负荷为84.9 kg COD /m³床•天,流速为2.8 cm / min和理论初始浓度为680 mg / L时,去除率最高为13.5 kg COD / m3·床·天。在流量变化下运行的滴滤过滤器在103.3 kg COD /m³·day的平均入口负荷和7.1 cm / min的流速下显示出最高的10 kg COD /m³·d的去除率。治疗是有限的。有许多可能的解释。首先是有效表面积,它表示生物膜表面与饲料之间发生接触的区域。活性表面积随流速的增加而增加。其次是饲料在床上的停留时间。进料的停留时间随流速而变化。随着流量增加,它降低了。第三是饲料中污染物的影响。进料中甲醇和甲醇的存在会抑制彼此的降解。还估算了用于实际窑炉的全尺寸生物滴滤器的尺寸。根据实验中获得的最大去除率和最佳流速进行估算。估算结果表明,该床获得了显着的去除效果,所需床的直径必须为2.35 m,高度为160。

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    Kristiono Arie;

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  • 年度 2009
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