Liu Yu, Shi Xiaohong, Zhang Sheng, Lu Junping, Li Wenbao, Sun Biao, Zhao Shengnan, Yao Dingwen, Huotari Jussi
Water Conservancy and Civil Engineering College, Inner Mongolia Agricultural University, Hohhot, 010018, China; Autonomous Region Collaborative Innovation Center for Integrated Management of Water Resources and Water Environment in the Inner Mongolia Reaches of the Yellow River, Hohhot, 010018, China.
Water Conservancy and Civil Engineering College, Inner Mongolia Agricultural University, Hohhot, 010018, China; Autonomous Region Collaborative Innovation Center for Integrated Management of Water Resources and Water Environment in the Inner Mongolia Reaches of the Yellow River, Hohhot, 010018, China.
Environ Pollut. 2023 Apr 15;323:121268. doi: 10.1016/j.envpol.2023.121268. Epub 2023 Feb 11.
Understanding the spatial distribution and characteristics of microplastics (MPs) in lake waters is essential to assessing and addressing lacustrine MP pollution. This study investigated how lake ice affects the abundance, spatial distribution, and characteristics (size, shape) of MPs in Lake Ulansuhai by analyzing samples collected at ten sites uniformly distributed throughout the lake during ice-free and ice-covered periods. The abundance of MPs ranged between 204 ± 28 and 1224 ± 185 n·L in lake waters during the ice-free period, and from 34 ± 8 to 216 ± 21 n·L and 269 ± 84 to 915 ± 117 n·L in water and ice during the ice-covered period, respectively. During the ice-covered period, MPs were 2.74-8.14 times higher in the ice than in water beneath the ice. Ice formation decreased MP abundance in lake waters, in part, by incorporating a relatively high percentage of MPs into the ice mass during freezing and by inhibiting atmospheric MPs from reaching the lake waters. The abundance of MPs in the water during the ice-free period was 4.50-11.30 times greater than during the ice-covered period. Seasonal variations in MP shape also occurred; the proportion of fibrous MPs in water decreased during the ice-covered period. Variations in MP abundance were partly due to differences in sedimentation rates; the settling of fibrous MPs is slower, making it easier for them to be captured during the formation of surface ice. Spatially, MPs were uniformly distributed during the ice-free period, but exhibited a spatially distinct pattern during ice-covered periods, when MPs in lake waters were higher in the northeast and lower in the southwest portions of the lake. During the ice-free period, small MPs (0.05-0.5 mm) were more likely to move with currents in the lake, whereas water velocities were reduced by ice formation, allowing small MPs to accumulate near the lake inlet.
了解湖水中微塑料(MPs)的空间分布和特征对于评估和应对湖泊微塑料污染至关重要。本研究通过分析在乌兰苏海湖无冰期和冰封期从全湖均匀分布的10个站点采集的样本,调查了湖冰如何影响微塑料的丰度、空间分布和特征(尺寸、形状)。无冰期湖水中微塑料的丰度在204±28至1224±185 n·L之间,冰封期水体和冰中的微塑料丰度分别为34±8至216±21 n·L和269±84至915±117 n·L。在冰封期,冰中的微塑料比其下方水体中的微塑料高2.74至8.14倍。结冰过程会降低湖水中微塑料的丰度,部分原因是在冻结过程中将相对较高比例的微塑料纳入冰块中,并阻止大气中的微塑料进入湖水。无冰期水中微塑料的丰度比冰封期高4.50至11.30倍。微塑料形状也存在季节性变化;冰封期水体中纤维状微塑料的比例下降。微塑料丰度的变化部分归因于沉降速率的差异;纤维状微塑料沉降较慢,使其在表层冰形成过程中更容易被捕获。在空间上,无冰期微塑料分布均匀,但在冰封期呈现出空间上不同的模式,此时湖水中的微塑料在湖的东北部较高,在西南部较低。在无冰期,小尺寸微塑料(0.05 - 0.5毫米)更有可能随湖水流移动,而结冰会降低水流速度,使小尺寸微塑料在湖口附近积聚。