Faculty of Civil and Environmental Engineering, Bialystok University of Technology, 45A Wiejska St., Bialystok 15-351, Poland.
Environ Res. 2017 May;155:344-352. doi: 10.1016/j.envres.2017.02.019. Epub 2017 Mar 20.
Sewage sludge was taken from a dairy WWTP belonging to Mlekovita Cooperative in Wysokie Mazowieckie. There were excess sludge, flotation sludge and a mixture of excess and flotation sludge from pre-treatment of dairy sewage. The initial content of 16 PAHs in excess sludge before fermentation was approximately 689µg·kg in dry mass, whereas in post-flotation sludge (which constituted around 30% of raw sludge) it was approximately 95µg·kg in dry mass. A mixture of excess and flotation sludge had the content of 497,7µg·kg in dry mass. Through comparison of particular hydrocarbons content in raw sewage sludge to the total PAHs content, it was shown that tricyclic compounds, which constituted 46,3% of the PAHs sum (excess sludge), and tetracyclic compounds, which constituted 60,0% of the PAHs sum (flotation sludge), were the dominating fractions. In the sludge subjected to fermentation in reactors with mixed sludge and surplus activated sludge, the general trend of the course of changes in concentrations of PAHs was similar. Both in the sludge inoculated with EM and in that not inoculated with EM, a significant increase in the total PAHs contents was observed in the first fermentation phase (acidic fermentation) after 7 days of the process. Addition of EM into the sludge did not prevent the PAHs release, and therefore higher concentrations of PAHs sum were recorded during the hydrolysis stage than in sludge before fermentation. A decrease in the sum of PAHs was observed after 2 weeks of fermentation in relation to the quantity observed after 1 week of fermentation (except from post-flotation sludge). In the following weeks, there was further decrease in the concentration of the 16 PAHs sum in all sludge types. However, in sludge without EM inoculation, it was lower than in sludge with EM inoculation. The loss of the majority of tested hydrocarbons was reported in the final phase of fermentation.
污泥取自 Mlekovita 合作社的 Wysokie Mazowieckie 奶制品废水处理厂。这些污泥分别来自于剩余污泥、浮选污泥和预处理乳制品污水的剩余污泥与浮选污泥的混合物。发酵前剩余污泥中 16 种多环芳烃的初始含量约为 689µg·kg 干重,而在浮选后污泥(占原污泥的 30%左右)中,其含量约为 95µg·kg 干重。剩余污泥与浮选污泥的混合物中,16 种多环芳烃的含量为 497.7µg·kg 干重。通过比较原污水污泥中特定碳氢化合物的含量与总多环芳烃的含量,结果表明三环化合物(占多环芳烃总量的 46.3%)和四环化合物(占多环芳烃总量的 60.0%)是主要的多环芳烃。在混合污泥和剩余活性污泥的发酵罐中进行发酵时,多环芳烃浓度变化过程的总体趋势相似。在接种和未接种 EM 的污泥中,在 7 天的过程后,第一个发酵阶段(酸性发酵)中都观察到多环芳烃总含量的显著增加。向污泥中添加 EM 并不能防止多环芳烃的释放,因此,水解阶段记录的多环芳烃总量高于发酵前的污泥。与发酵 1 周后相比,发酵 2 周后,所有污泥类型的多环芳烃总量都有所下降(浮选后污泥除外)。在接下来的几周内,所有污泥类型的 16 种多环芳烃总量浓度都进一步下降。然而,在未接种 EM 的污泥中,其浓度比接种 EM 的污泥低。在发酵的最后阶段,报告了大多数测试碳氢化合物的损失。