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The removal of N and P in aerobic and anoxic-aerobic digestion of waste activated sludge from biological nutrient removal systems

机译:从生物营养去除系统中的活性污泥的好氧和缺氧-好氧消化中去除氮和磷

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Biological nutrient removal (BNR) activated sludge (AS) systems produce a waste activated sludge (WAS) that is rich in nitrogen (N) and phosphorus (P). When this sludge is thickened to 3-6% total suspended solids (TSS) and digested (aerobic or anaerobic), a high proportion of N and P are released to the bulk liquid resulting in high concentrations of ammoniaitrate and orthophosphate up to several hundred mg/l (without denitrification or P precipitation). This research investigates P removal by P precipitation in anoxic-aerobic digestion of P-rich BNR system WAS. The experimental setup for this work was a lab-scale membrane UCT BNR system fed real settled sewage with added acetate, orthophosphate, and cations Mg and K to increase biological excess P removal. This WAS was fed to batch aerobic digesters at various TSS concentrations, and to two 20-day retention time continuous anoxic-aerobic digesters (AnAerDig) with aeration cycles of 3-h air on and 3-h air off, one fed concentrated WAS (20 g TSS/l) and the other fed diluted WAS (3 g TSS/l). Nitrogen removal has been discussed in the previous paper. This paper focuses on the P removal by P precipitation observed in the batch tests and continuous systems. The rate of polyphosphate release (b(GP)) during batch aerobic digestion at low TSS without P precipitation was found to be 2.5 times faster than the endogenous respiration rate (b(G)) of phosphorus accumulating organics (PAO), i.e. b(GP) = 0.1/d. This rate was then applied to the high-TSS aerobic batch tests and continuous anoxic-aerobic digesters to estimate the P precipitation at various TSS concentrations, with and without additional Mg or Ca dosing. Newberyite (MgHPO4 center dot 3H(2)O) and amorphous tricalcium phosphate (ACP or TCP, Ca-3(PO4)(2)center dot xH(2)O) are found to be the most common phosphate precipitates.
机译:生物营养物去除(BNR)活性污泥(AS)系统产生的废活性污泥(WAS)富含氮(N)和磷(P)。当污泥增稠到总悬浮固体(TSS)的3-6%并被消化(好氧或厌氧)时,大量的N和P释放到散装液体中,导致高浓度的氨/硝酸盐和正磷酸盐百mg / l(无反硝化或P沉淀)。本研究研究了富磷BNR系统WAS在缺氧-好氧消化中的P沉淀去除P。这项工作的实验装置是实验室规模的膜式UCT BNR系统,该系统向实际沉降的污水中加入乙酸盐,正磷酸盐以及阳离子Mg和K,以增加生物中过量P的去除。将该WAS喂入各种TSS浓度的分批需氧消化池中,并送入两个20天保留时间的连续缺氧需氧消化池(AnAerDig),其中曝气循环为3小时空气和3小时空气,其中一个为浓缩WAS( 20克TSS / l)和另一份稀释的WAS(3克TSS / l)。脱氮已经在先前的论文中进行了讨论。本文重点介绍了在分批测试和连续系统中观察到的通过P沉淀去除P的方法。发现在低TSS下无磷沉淀的分批需氧消化中多磷酸盐的释放速率(b(GP))比蓄磷有机物(PAO)的内源性呼吸速率(b(G))快2.5倍,即b(G) GP)= 0.1 / d。然后将此速率应用于高TSS好氧分批测试和连续缺氧-好氧消化池,以估算在添加和不添加镁或钙的情况下,各种TSS浓度下的P沉淀。发现Newberyite(MgHPO4中心点3H(2)O)和无定形磷酸三钙(ACP或TCP,Ca-3(PO4)(2)中心点xH(2)O)是最常见的磷酸盐沉淀。

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