风洞试验中空气中微塑料的垂直浓度梯度和迁移

E. M. Esders, Christoph Georgi, Wolfgang Babel, Andreas Held, Christoph Karl Thomas
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引用次数: 0

摘要

摘要微塑料是环境(包括大气)中无处不在的人为材料。尽管微塑料是一种潜在的污染物,但很少有研究关注微塑料的大气传输机制及其扩散。我们在风洞这种具有中性稳定性的可控环境中研究了空中微塑料的垂直迁移,以确定微塑料在大气中长距离迁移的必要条件。超声波分散器从直径为 0.51 微米的聚苯乙烯微球微塑料(MPs)悬浮液中产生气载水滴。水滴被注入气流,蒸发并释放出空气中的单个微塑料。分散器可实现风洞中 MPs 浓度的时变性和用户控制。MPs 分别在离地面 27、57 和 255 毫米处注入。一台 GRIMM R11 光学粒子计数器(OPC)和三台 Alphasense OPC 测量了时间平均的 MP 浓度曲线(距离地面 27、57 和 157 毫米)。这些数据与热线探头测量到的湍流气流特征相结合,利用通量-梯度相似理论估算垂直颗粒通量。GRIMM R11 OPC 通过垂直移动其采样管来测量垂直浓度剖面。三台 Alphasense OPC 同时测量了三个不同高度的粒子浓度。结果表明,最大浓度不是在注入高度测量到的,而是由于重力沉降而转移到表面的。中压微粒作为较大水滴的一部分,会经历较高的重力沉降。对于 27 毫米的最低注入高度,沉降导致风洞中的 MP 浓度较低,因为 MP 会因沉降而损失。风速的增加会减少 MP 的沉降损失,但沉降在最大摩擦速度 0.14 m s-1 之前一直存在。在 255 毫米的最高注入量和层流条件下,沉降导致净 MP 排放,这对高注入量时净 MP 沉积的预期提出了挑战。湍流逆转了 MP 浓度曲线,产生了净 MP 沉积,沉积速度为 3.7 ± 1.9 cm s-1。认识到微塑料与矿物颗粒具有相同的沉积速度,有助于了解它们的环境行为。该结果支持使用现有模型来评估微塑料在累积模式下的迁移。相似的沉积速度表明,在大气中迁移的微塑料可以在与矿物颗粒相同的地方被发现。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Vertical concentrations gradients and transport of airborne microplastics in wind tunnel experiments
Abstract. Microplastics are an ubiquitous anthropogenic material in the environment, including the atmosphere. Little work has focused on the atmospheric transport mechanisms of microplastic nor its dispersion, despite it being a potential pollutant. We study the vertical transport of airborne microplastics in a wind tunnel, a controllable environment with neutral stability, to identify the necessary conditions for the long-range atmospheric transport of microplastics. An ultrasonic disperser generated airborne water droplets from a suspension of polystyrene microsphere microplastics (MPs) with a diameter of 0.51 µm. The water droplets were injected into the airflow, evaporating and releasing single airborne MPs. The disperser allowed for time-invariant and user-controlled concentrations of MPs in the wind tunnel. MPs were injected at 27, 57, and 255 mm above the ground. A single GRIMM R11 optical particle counter (OPC) and three Alphasense OPCs measured time-averaged MP concentration profiles (27, 57, and 157 mm above the ground). These were combined with turbulent airflow characteristics measured by a hotwire probe to estimate vertical particle fluxes using the flux-gradient similarity theory. The GRIMM R11 OPC measured vertical concentration profiles by moving its sampling tube vertically. The three Alphasense OPCs measured particle concentrations simultaneously at three distinct heights. Results show that maximum concentrations are not measured at the injection height but are rather shifted to the surface by gravitational settling. The MPs experience higher gravitational settling while they are part of the larger water droplets. For the lowest injection at 27 mm, the settling leads to smaller MP concentrations in the wind tunnel, as MPs are lost to deposition. Increasing the wind speed decreases the loss of MPs by settling, but settling is present until our maximum friction velocity of 0.14 m s−1. For the highest injection at 255 mm and laminar flow, the settling resulted in a net MP emission, challenging the expectation of a net MP deposition for high injection. Turbulent flows reverse the MP concentration profile giving a net MP deposition with deposition velocities of 3.7 ± 1.9 cm s−1. Recognizing that microplastics share deposition velocities with mineral particles bridges the gap in understanding their environmental behavior. The result supports the use of existing models to evaluate the transport of microplastics in the accumulation mode. The similar deposition velocities suggest that microplastics transported in the atmosphere can be found in the same places as mineral particles.
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