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Production of class A biosolids with anoxic low dose alkaline treatment and odor management

机译:通过缺氧低剂量碱处理和气味控制生产A类生物固体

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The feasibility of full-scale anoxic disinfection of dewatered and digested sludge from Winnipeg, Manitoba with low lime doses and lagoon fly ash was investigated to determine if a class A product could be produced. Lime doses of 50 g, 100 g, and 200 g per kg of biosolids (dry) were used along with fly ash doses of 500 g, 1,000 g, and 1,500 g per kg of biosolids (dry). The mixed product was buried in eight-10 cubic metre trenches at the West End Water Pollution Control Center in Winnipeg. The trenches were backfilled With dirt and trapped to simulate anoxic conditions. Sampling cages were packed with the mixed product and pathogens non-indigenous to Winnipeg's biosolids. The cages were buried amongst the mixed biosolids in the trench. The non-indigenous pathogens spiked in the laboratory were the helminth Ascaris suum and the enteric virus reovirus. Samples were removed at days 12, 40, 69, 291, and 356 and were tested for the presence of fecal Coliform, Clostridium perfringens spores, Ascaris suum eggs, and reovirus. The pH, total solids, and free ammonia content of the mixed product were also determined for each sample. Odor was quantified for samples at both 291 and 356 days. Fecal Coliform bacteria and reovirus were completely inactivated for doses as low as 100 g lime per kg biosolids (dry) and 50 g lime + 500 g fly ash per kg biosolids (dry). Spores of the bacteria C. perfringens experienced a 4-log reduction when treated with 100 g lime per kg biosolids and a 5-log reduction when treated with doses as low as 50 g lime + 500 g fly ash per kg biosolids (dry) after 69 days. Ascaris eggs were completely inactivated in 5 gram packets for all treatments involving 100 g lime per kg biosolids (dry) after 69 days. Class A pathogen requirements were met for all treatments involving a lime dose of at least 100 g per kg biosolids. The odor potential from the produced biosolids is also assessed.
机译:研究了用低石灰剂量和泻湖粉煤灰对来自马尼托巴省温尼伯的脱水和消化污泥进行全面缺氧消毒的可行性,以确定是否可以生产A类产品。每千克生物固体使用50克,100克和200克石灰粉(干),每千克生物固体使用500克,1000克和1500克粉煤灰(干粉)。混合后的产品被埋在温尼伯西区水污染控制中心的8至10立方米的trench沟中。沟槽被灰尘回填并被捕获以模拟缺氧条件。采样笼中装有混合产品和非温尼伯生物固体病原体。笼子被埋在海沟中的混合生物固体中。在实验室中加标的非本地病原体是蠕虫A虫和肠道病毒呼肠孤病毒。在第12、40、69、291和356天取出样品,并测试粪便大肠菌,产气荚膜梭状芽孢杆菌孢子,猪scar虫卵和呼肠孤病毒的存在。还确定了每个样品的混合产品的pH,总固体和游离氨含量。在291天和356天都对样品的气味进行了定量。粪便大肠菌和呼肠孤病毒完全灭活,剂量低至每千克生物固体100克石灰(干)和每千克生物固体50克石灰+ 500克粉煤灰(干)。每公斤生物固体用100克石灰处理后,产气荚膜梭菌的孢子减少4个对数,而每公斤生物固体(干燥)的剂量低至50克石灰+ 500克粉煤灰时,其孢子减少5对数69天在69天后,对于所有涉及每公斤生物固体100克石灰(干燥)的处理,将5克包装的虫卵完全灭活。石灰剂量至少为每千克生物固体100克的所有处理均满足A类病原体的要求。还评估了产生的生物固体的潜在气味。

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