首页> 外文期刊>Transactions of The Institution of Chemical Engineers. Process Safety and Environmental Protection, Part B >Reaction mechanisms in solid-state anaerobic digestion I.The Reaction Front Hypothesis
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Reaction mechanisms in solid-state anaerobic digestion I.The Reaction Front Hypothesis

机译:固态厌氧消化I的反应机制I.反应前假设

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The proposed mechanism applies to the solid-state anaerobic digestion of a bed of organic wastes or other substrates. It is initiated by a seed body above a minimum viable size, around which a multi-zoned, mobile, reaction front develops. Acetate is formed in the leading zone, then diffuses back to a separate methanogenic zone, which is protected from acid inhibition by an intervening, passive buffer zone. This front gradually advances until the whole waste mass has been stabilized. The front cannot cross voids, so good inter-particle contact accelerates the process. The number of seed bodies determines the number of fronts and thus the rate of stabilization. Moreover, seeding patterns largely determine the mean distance the fronts must cover in order to complete the stabilization process, so they have a major effect on process kinetics. In packed-bed digesters densely seeded with previously digested waste, viable seed bodies are plentiful and closely spaced. Consequently, numerous fronts are formed and the mean distance they must cover is short, so the process is quick. However, in a typical landfill, inadequate seeding greatly extends the distances the few fronts must travel and thus greatly prolongs the stabilization process. This solid-phase mechanism would be dominant in well-seeded, rich, organic wastes. However, in lean wastes or in the absence of viable seed bodies, conventional, liquid-phase mechanisms would be dominant instead. In some circumstances, the two mechanisms might also co-exist. In others, neither might be effective, so the raw waste could be preserved indefinitely. This hypothesis is proposed for evaluation and testing. No such mechanism seems to have been considered in process modelling, in the design of experimental studies or in the operation of packed-bed waste digesters and bioreactor landfills. However, it could have a major impact in all these applications.
机译:所提出的机制适用于固态的有机废物床或其他基材的固态厌氧消化。它由上述最小可行尺寸的种子体引发,周围多次分区,移动,反应前部发展。乙酸盐形成在前导区中,然后延伸回到单独的甲状腺区,通过中间被动缓冲区免受酸抑制的影响。这正面逐渐进展,直到整个废物稳定。前线不能跨越空隙,因此良好的粒子间接接触加速了该过程。种子体的数量决定了前部的数量,从而确定了稳定率。此外,播种图案在很大程度上决定了前方必须覆盖的平均距离以完成稳定过程,因此它们对工艺动力学产生了重大影响。在包装床上的消化器中,用先前消化的废物浓密地播种,可行的种子体具有丰富而紧密间隔。因此,形成了许多前线,并且它们必须覆盖的平均距离短,因此该过程很快。然而,在典型的垃圾填埋场中,播种不足大大延伸了少数前方必须旅行的距离,因此大大延长了稳定过程。这种固相机制将在种子良好,丰富,有机废物中占主导地位。然而,在瘦废物或在没有活种子体的情况下,常规的液相机制将是占优势的。在某些情况下,两种机制也可能共存。在别人中,既不是有效的,所以原始废物可以无限期地保存。提出了该假设进行评估和测试。在实验研究的设计中或在包装床废物消化器和生物反应器垃圾填埋场的设计中,没有这样的机制似乎已被考虑在过程建模中。但是,它可能对所有这些应用产生重大影响。

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