矿物冰核能力对热的敏感性及其对生物冰核器热试验的影响

M. Daily, M. Tarn, T. Whale, B. Murray
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引用次数: 6

摘要

摘要冰核粒子(INPs)是一种大气气溶胶粒子,可以通过在过冷的云水滴中触发冰的形成,强烈地影响混合相云的辐射特性和降水的发生。为了更好地了解它们的分布和来源,需要在从环境中收集的样品中区分矿物和生物来源的INPs,但这是具有挑战性的。评估从环境中收集的样品(如气溶胶、雨水、土壤)中矿物和生物成因INPs的相对贡献的一种常用方法是确定加热前后的冰成核能力(INA),其中热量预计会使与生物冰成核相关的蛋白质变性。关键的假设是,生物起源的冰核位置因热而变性,而与矿物表面相关的冰核位置则不受影响;我们在这里验证这个假设。我们将与大气相关的矿物样品暴露在湿热(INP悬浮液加热到90°C以上)或干热(干燥样品加热到250°C)下,并使用液滴冷冻法评估其浸入模式INA的影响。k长石,被认为是主要的矿物基大气INP类型,不受湿加热的显著影响,而石英,斜长石和亚利桑那测试尘埃(ATD)在这种模式下加热时失去INA。我们认为,水相中INA的减少是由于热处理直接改变了矿物颗粒表面,而不是由于生物或有机污染。我们假设,由于矿物INA失活程度与其溶解速率之间的相关性,在所有情况下,活性位点的降解都是通过矿物表面的溶解来实现的。干加热在钾长石颗粒中产生轻微但可重复的失活,但与湿加热相比,通常不太可能使矿物失活。我们还对蛋白质和非蛋白质生物源INP替代材料进行了热测试,发现非蛋白质样品(纤维素和花粉)相对耐热。相比之下,蛋白质冰核样品对干湿热高度敏感,正如预期的那样,尽管加热后它们的活性仍然不可忽略。我们的结论是,尽管INP热测试有可能产生假阳性,即矿物INP失活可能被误解为生物INP的存在,但只要矿物INP是由钾长石控制的,它们仍然是一种有效的方法,用于定性检测环境样品中的蛋白质生物INP。
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The sensitivity of the ice-nucleating ability of minerals to heat and the implications for the heat test for biological ice nucleators
Abstract. Ice-nucleating particles (INPs) are atmospheric aerosol particles that can strongly influence the radiative properties and precipitation onset in mixed-phase clouds by triggering ice formation in supercooled cloud water droplets. The ability to distinguish between INPs of mineral and biological origin in samples collected from the environment is needed to better understand their distribution and sources, but this is challenging. A common method for assessing the relative contributions of mineral and biogenic INPs in samples collected from the environment (e.g., aerosol, rainwater, soil) is to determine the ice-nucleating ability (INA) before and after heating, where heat is expected to denature proteins associated with biological ice nucleants. The key assumption is that the ice nucleation sites of biological origin are denatured by heat, while those associated with mineral surfaces remain unaffected; we test this assumption here. We exposed atmospherically relevant mineral samples to wet heat (INP suspensions warmed to above 90 °C) or dry heat (dry samples heated to 250 °C) and assessed the effects on their immersion mode INA using a droplet freezing assay. K-feldspar, thought to be the dominant mineral-based atmospheric INP type where present, was not significantly affected by wet heating, while quartz, plagioclase feldspars and Arizona test Dust (ATD) lost INA when heated in this mode. We argue that these reductions in INA in the aqueous phase result from direct alteration of the mineral particle surfaces by heat treatment rather than from biological or organic contamination. We hypothesise that degradation of active sites by dissolution of mineral surfaces is the mechanism in all cases due to the correlation between mineral INA deactivation magnitudes and their dissolution rates. Dry heating produced minor but repeatable deactivations in K-feldspar particles but was generally less likely to deactivate minerals compared to wet heating. We also heat tested proteinaceous and non-proteinaceous biogenic INP proxy materials and found that non-proteinaceous samples (cellulose and pollen) were relatively heat resistant. In contrast, the proteinaceous ice-nucleating samples were highly sensitive to wet and dry heat, as expected, although their activity remained non-negligible after heating. We conclude that, while INP heat tests have the potential to produce false positives, i.e., deactivation of a mineral INA that could be misconstrued as the presence of biogenic INPs, they are still a valid method for qualitatively detecting proteinaceous biogenic INP in ambient samples, so long as the mineral-based INA is controlled by K-feldspar.
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