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微藻处理废水过程中的一氧化二氮排放:现状及对温室气体预算的影响。

Nitrous oxide emissions during microalgae-based wastewater treatment: current state of the art and implication for greenhouse gases budgeting.

机构信息

School of Food and Advanced Technology, Massey University, Private Bag 11222, Palmerston North, New Zealand E-mail:

出版信息

Water Sci Technol. 2020 Sep;82(6):1025-1030. doi: 10.2166/wst.2020.304.

DOI:10.2166/wst.2020.304
PMID:33055393
Abstract

Microalgae can synthesise the ozone depleting pollutant and greenhouse gas nitrous oxide (NO). Consequently, significant NO emissions have been recorded during real wastewater treatment in high rate algal ponds (HRAPs). While data scarcity and variability prevent meaningful assessment, the magnitude reported (0.13-0.57% of the influent nitrogen load) is within the range reported by the Intergovernmental Panel on Climate Change (IPCC) for direct NO emissions during centralised aerobic wastewater treatment (0.016-4.5% of the influent nitrogen load). Critically, the ability of microalgae to synthesise NO challenges the IPCC's broad view that bacterial denitrification and nitrification are the only major cause of NO emissions from wastewater plants and aquatic environments receiving nitrogen from wastewater effluents. Significant NO emissions have indeed been repeatedly detected from eutrophic water bodies and wastewater discharge contributes to eutrophication via the release of nitrogen and phosphorus. Considering the complex interplays between nitrogen and phosphorus supply, microalgal growth, and microalgal NO synthesis, further research must urgently seek to better quantify NO emissions from microalgae-based wastewater systems and eutrophic ecosystems receiving wastewater. This future research will ultimately improve the prediction of NO emissions from wastewater treatment in national inventories and may therefore affect the prioritisation of mitigation strategies.

摘要

微藻可以合成消耗臭氧的污染物和温室气体氧化亚氮(NO)。因此,在高负荷藻类塘(HRAP)中进行实际废水处理时,已经记录到了大量的 NO 排放。尽管数据的稀缺性和可变性使得有意义的评估变得困难,但报告的数值(进水氮负荷的 0.13-0.57%)在政府间气候变化专门委员会(IPCC)报告的集中好氧废水处理过程中的直接 NO 排放范围内(进水氮负荷的 0.016-4.5%)。关键的是,微藻合成 NO 的能力挑战了 IPCC 的广泛观点,即细菌反硝化和硝化作用是来自废水处理厂和接收废水氮的水生环境中 NO 排放的唯一主要原因。事实上,已经从富营养水体中多次检测到大量的 NO 排放,而废水排放通过释放氮和磷导致了富营养化。考虑到氮和磷供应、微藻生长和微藻 NO 合成之间的复杂相互作用,进一步的研究必须迫切寻求更好地量化基于微藻的废水处理系统和接收废水的富营养化生态系统中的 NO 排放。未来的研究将最终提高国家清单中对废水处理中 NO 排放的预测,因此可能会影响缓解策略的优先级。

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