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Stabilisation of municipal solid waste after autoclaving in a passively aerated bioreactor

机译:在被动曝气生物反应器中进行高压灭菌后,可稳定市政固体废物

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Autoclaving of unsorted municipal solid waste is one of the solutions in waste management that maximises the amount of waste for recycling. After autoclaving, however, a large part of the waste is composed of unstabilised biodegradable fractions (organic remaining fraction, ORF), which may comprise up to 30% of autoclaved waste and cannot be landfilled without further stabilisation. Thus, the aim of this study was to investigate the effectiveness of aerobic stabilisation in a passively aerated reactor of organic remaining fraction after full-scale autoclaving of unsorted municipal solid waste. The organic remaining fraction had a volatile solids content of ca. 70%, a 4-day respiration activity test (AT4) of ca. 26 g O-2 kg(-1) total solids and a 21-day gas formation test (GP21) of ca. 235 dm(3) kg(-1) total solids. Stabilisation was conducted in a 550 L reactor with passive aeration (Stage I) and a periodically turned windrow (Stage II). The feedstocks consisted entirely of organic remaining fraction, or of organic remaining fraction with 10% inoculum (ORF + I). Inoculum constituted product of stabilisation of organic remaining fraction. During stabilisation of organic remaining fraction and ORF + I, thermophilic conditions were achieved, and the decreases of volatile solids, AT4 and GP21 could be described by 1 order kinetic models. The rate constants of volatile solids removal (k(VS)) were 0.033 and 0.068 d(-1) for organic remaining fraction and ORF + I, respectively, and the thermophilic phase was shorter with ORF + I (25 days vs. 45 days). The decrease in GP21 corresponded to volatile solids decrease, but AT4 decreased sharply during the first 10 days of waste stabilisation in the reactor, indicating that the content of highly biodegradable organic matter decreased during this time.
机译:未分类的城市固体废物的高压灭菌是废物管理中的解决方案之一,该解决方案可最大程度地提高废物的回收利用率。但是,高压灭菌后,很大一部分废物是由不稳定的可生物降解部分(有机残留部分,ORF)组成,这些部分可能占高压灭菌废物的30%,如果不进一步稳定就不能填埋。因此,本研究的目的是在对未分类的城市固体废物进行全面高压灭菌后,研究有机剩余部分的被动曝气反应器中有氧稳定的有效性。剩余的有机部分的挥发性固体含量为约3。 70%,约4天的呼吸活动测试(AT4)。 26 g O-2 kg(-1)总固体和21天的气体形成测试(GP21)约为。固体总含量235 dm(3)kg(-1)。在具有被动曝气(阶段I)和定期翻堆的草堆(阶段II)的550 L反应器中进行稳定化。原料完全由有机剩余部分或含10%接种物(ORF + I)的有机剩余部分组成。接种物构成有机剩余部分稳定化的产物。在稳定有机剩余部分和ORF + I的过程中,达到了高温条件,挥发性固体,AT4和GP21的减少可以用一阶动力学模型描述。残留有机物和ORF + I的挥发性固体去除速率常数(k(VS))分别为0.033和0.068 d(-1),ORF + I的嗜热相较短(25天vs. 45天) )。 GP21的减少与挥发性固体的减少相对应,但是AT4在反应器中废物稳定的前10天急剧减少,这表明可生物降解的高度有机物的含量在这段时间内减少了。

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