Exton Benjamin, Hassard Francis, Medina-Vaya Angel, Grabowski Robert C
Faculty of Engineering and Applied Sciences, Cranfield University, Cranfield, United Kingdom.
Institute for Nanotechnology and Water Sustainability, University of South Africa, Johannesburg, South Africa.
Front Microbiol. 2024 Oct 23;15:1320487. doi: 10.3389/fmicb.2024.1320487. eCollection 2024.
Airport de-icing has been linked with the growth of undesirable river biofilms (URBs, formerly "sewage fungus"), a manifestation of organic pollution causing long-term ecological damage to watercourses. URBs are a polymicrobial community, with one key taxon standing out in literature: , a filamentous bacterium also found in sewage treatment and activated sludges. An industry often implicated in causing URBs is airport de-icing, with large biofilms often developing downstream of airport discharges in winter months. However, it is not yet clear which de-icers may cause URBs and how they influence growth. Therefore, specific objectives were to (i) determine which freeze-point depressants (FPDs) can be utilized by ; (ii) examine differences in the growth kinetics between FPDs; and (iii) compare pure-FPDs to commercial airport de-icers (CADs) as carbon sources, to determine impacts of additives. This study employed a turbidimetric micro-batch culture design to conduct microbial growth experiments, using and a minimal medium supplemented with airport de-icer as the carbon source. Equimolar carbon concentrations were used to compare the effects of common FPDs and CADs - each containing a specific FPD. Growth was assessed via optical density (OD) measurements, from which time-to-detection, maximum rate of change, and maximum optical density were derived and kinetics inferred. was found to grow effectively on all FPDs tested, although the microbial yield was heavily dependent on the carbon concentration for all FPDs and CADs. Sodium acetate generated the quickest growth, with the lowest TTD (lag-time) for all but the lowest concentrations tested. Propylene glycol produced the greatest maxOD (total growth), whereas ethylene glycol had a higher limiting concentration for maxROC (growth rate). The mixture of compounds and additives in commercial products did not significantly impact the growth of . This research provides evidence from controlled laboratory experiments that airport de-icers support the growth of . The differences in growth kinetics observed for the FPDs and CADs could inform improved mitigation or treatment to reduce the incidence and ecological impacts of URBs.
机场除冰与不良河流生物膜(URB,原称“污水真菌”)的生长有关,这是有机污染的一种表现,会对水道造成长期生态破坏。URB是一个多微生物群落,文献中有一个关键分类群尤为突出: ,一种在污水处理和活性污泥中也能发现的丝状细菌。常被认为会导致URB的一个行业是机场除冰,冬季时,大型生物膜常常在机场排水口下游形成。然而,目前尚不清楚哪些除冰剂可能导致URB以及它们如何影响其生长。因此,具体目标是:(i)确定 可以利用哪些冰点降低剂(FPD);(ii)研究不同FPD之间生长动力学的差异;(iii)将纯FPD与商业机场除冰剂(CAD)作为碳源进行比较,以确定添加剂的影响。本研究采用比浊法微批次培养设计进行微生物生长实验,使用 以及添加机场除冰剂作为碳源的基本培养基。采用等摩尔碳浓度来比较常见FPD和CAD的效果——每种都含有一种特定的FPD。通过测量光密度(OD)评估生长情况,由此得出检测时间、最大变化率和最大光密度,并推断出生长动力学。结果发现, 在所有测试的FPD上都能有效生长,不过所有FPD和CAD的微生物产量都严重依赖于碳浓度。乙酸钠产生的生长最快,除了测试的最低浓度外,所有浓度下的检测时间(滞后时间)都最短。丙二醇产生的最大光密度(总生长量)最大,而乙二醇对最大变化率(生长速率)的限制浓度更高。商业产品中化合物和添加剂的混合物对 的生长没有显著影响。这项研究通过对照实验室实验提供了证据表明机场除冰剂能支持 的生长。观察到的FPD和CAD生长动力学差异可为改进缓解措施或处理方法提供参考,以减少URB的发生率和生态影响。