Grantz D A, Garner J H B, Johnson D W
Department of Botany and Plant Sciences, Air Pollution Research Center, University of California at Riverside, Kearney Agricultural Center, 9240 South Riverbend Avenue, 93648, Parlier, CA, USA.
Environ Int. 2003 Jun;29(2-3):213-39. doi: 10.1016/S0160-4120(02)00181-2.
Atmospheric particulate matter (PM) is a heterogeneous material. Though regulated as un-speciated mass, it exerts most effects on vegetation and ecosystems by virtue of the mass loading of its chemical constituents. As this varies temporally and spatially, prediction of regional impacts remains difficult. Deposition of PM to vegetated surfaces depends on the size distribution of the particles and, to a lesser extent, on the chemistry. However, chemical loading of an ecosystem may be determined by the size distribution as different constituents dominate different size fractions. Coating with dust may cause abrasion and radiative heating, and may reduce the photosynthetically active photon flux reaching the photosynthetic tissues. Acidic and alkaline materials may cause leaf surface injury while other materials may be taken up across the cuticle. A more likely route for metabolic uptake and impact on vegetation and ecosystems is through the rhizosphere. PM deposited directly to the soil can influence nutrient cycling, especially that of nitrogen, through its effects on the rhizosphere bacteria and fungi. Alkaline cation and aluminum availability are dependent upon the pH of the soil that may be altered dramatically by deposition of various classes of PM. A regional effect of PM on ecosystems is linked to climate change. Increased PM may reduce radiation interception by plant canopies and may reduce precipitation through a variety of physical effects. At the present time, evidence does not support large regional threats due to un-speciated PM, though site-specific and constituent-specific effects can be readily identified. Interactions of PM with other pollutants and with components of climate change remain important areas of research in assessment of challenges to ecosystem stability.
大气颗粒物(PM)是一种非均质物质。尽管它被作为未分类的质量进行监管,但其对植被和生态系统的影响主要是通过其化学成分的质量负荷来实现的。由于这种负荷在时间和空间上存在变化,区域影响的预测仍然很困难。PM在植被表面的沉积取决于颗粒的大小分布,在较小程度上还取决于其化学性质。然而,生态系统的化学负荷可能由大小分布决定,因为不同的成分在不同的粒径级分中占主导地位。灰尘覆盖可能会导致磨损和辐射加热,并可能减少到达光合组织的光合有效光子通量。酸性和碱性物质可能会导致叶片表面损伤,而其他物质可能会穿过角质层被吸收。代谢吸收以及对植被和生态系统产生影响的更可能途径是通过根际。直接沉积到土壤中的PM可以通过对根际细菌和真菌的影响来影响养分循环,尤其是氮的循环。碱性阳离子和铝的有效性取决于土壤的pH值,而土壤pH值可能会因各类PM的沉积而发生显著变化。PM对生态系统的区域影响与气候变化有关。增加的PM可能会减少植物冠层对辐射的截留,并可能通过各种物理效应减少降水。目前,虽然特定地点和特定成分的影响很容易识别,但尚无证据支持未分类的PM会造成重大区域威胁。在评估对生态系统稳定性的挑战时,PM与其他污染物以及气候变化成分之间的相互作用仍然是重要的研究领域。