Bohutskyi Pavlo, Liu Kexin, Nasr Laila Khaled, Byers Natalie, Rosenberg Julian N, Oyler George A, Betenbaugh Michael J, Bouwer Edward J
Department of Geography & Environmental Engineering, Johns Hopkins University, 3400 North Charles Street, Baltimore, MD, 21218-2686, USA,
Appl Microbiol Biotechnol. 2015 Jul;99(14):6139-54. doi: 10.1007/s00253-015-6603-4. Epub 2015 May 7.
Eighteen microalgae, including two local isolates, were evaluated for their ability to grow and remove nutrients from unsterilized primary or secondary wastewater effluents as well as wastewater supplemented with nutrient-rich anaerobic digester centrate (ADC). Most of the tested species except several phylogenetically clustered Chlorella sorokiniana including local isolates and Scenedesmus strains were unable to grow efficiently. This may reflect the presence of certain genetic traits important for robust growth in the unsterilized wastewater. The maximum algal-specific growth rates and biomass density obtained in these bacterial-contaminated cultures were in the range of 0.8-1 day(-1) and 250-350 mg L(-1), respectively. ADC supplementation was especially helpful to biologically treated secondary effluent with its lower initial macronutrient and micronutrient content. As a result of algal growth, total nitrogen and orthophosphate levels were reduced by as much as 90 and 70 %, respectively. Biological assimilation was estimated to be the main mechanism of nitrogen removal in primary and secondary effluents with ammonia volatilization and bacterial nitrification-denitrification contributing for cultures supplemented with ADC. Assimilation by algae served as the principal mechanism of orthophosphate remediation in secondary wastewater cultures, while chemical precipitation appeared also to be important for orthophosphate removal in primary wastewater. Overall, cultivation of microalgae in primary and primary + 5 % ADC may be more favorable from an economical and sustainability perspective due to elimination of the costly and energy-intensive biological treatment step. These findings demonstrate that unsterilized wastewater and ADC can serve as critical nutrient sources for biomass generation and that robust microalgae can be potent players in wastewater phytoremediation.
对18种微藻(包括两种本地分离株)进行了评估,以测定它们在未灭菌的一级或二级废水流出物以及添加了富含营养物的厌氧消化池浓缩液(ADC)的废水中生长和去除营养物的能力。除了几种系统发育聚类的索氏小球藻(包括本地分离株)和栅藻菌株外,大多数测试物种都无法高效生长。这可能反映出在未灭菌废水中存在对强劲生长很重要的某些遗传特征。在这些受细菌污染的培养物中获得的最大藻类比生长速率和生物量密度分别在0.8-1天⁻¹和250-350毫克/升的范围内。添加ADC对初始大量营养素和微量营养素含量较低的生物处理二级流出物特别有帮助。由于藻类生长,总氮和正磷酸盐水平分别降低了多达90%和70%。据估计,生物同化是一级和二级流出物中氮去除的主要机制,氨挥发和细菌硝化-反硝化作用对添加了ADC的培养物有贡献。藻类同化是二级废水培养中正磷酸盐修复的主要机制,而化学沉淀似乎对一级废水中正磷酸盐的去除也很重要。总体而言,从经济和可持续性角度来看,在一级废水和一级+5%ADC中培养微藻可能更有利,因为省去了成本高且能源密集的生物处理步骤。这些发现表明,未灭菌废水和ADC可作为生物质生产的关键营养源,并且健壮的微藻可以成为废水植物修复中的有力参与者。