Department of Molecular Bioscience and Bioengineering, 1955 East-West Road, Agricultural Science 218, University of Hawaii at Manoa, Honolulu, HI 96822, USA.
Water Res. 2010 Oct;44(18):5334-44. doi: 10.1016/j.watres.2010.06.015. Epub 2010 Jun 12.
In order to gain more information about the fate of Cryptosporidium parvum oocysts in tropical volcanic soils, the transport and attachment behaviors of oocysts and oocyst-sized polystyrene microspheres were studied in the presence of two soils. These soils were chosen because of their differing chemical and physical properties, i.e., an organic-rich (43-46% by mass) volcanic ash-derived soil from the island of Hawaii, and a red, iron (22-29% by mass), aluminum (29-45% by mass), and clay-rich (68-76% by mass) volcanic soil from the island of Oahu. A third agricultural soil, an organic- (13% by mass) and quartz-rich (40% by mass) soil from Illinois, was included for reference. In 10-cm long flow-through columns, oocysts and microspheres advecting through the red volcanic soil were almost completely (98% and 99%) immobilized. The modest breakthrough resulted from preferential flow-path structure inadvertently created by soil-particle aggregation during the re-wetting process. Although a high (99%) removal of oocysts and microsphere within the volcanic ash soil occurred initially, further examination revealed that transport was merely retarded because of highly reversible interactions with grain surfaces. Judging from the slope of the substantive and protracted tail of the breakthrough curve for the 1.8-μm microspheres, almost all (>99%) predictably would be recovered within ∼4000 pore volumes. This suggests that once contaminated, the volcanic ash soil could serve as a reservoir for subsequent contamination of groundwater, at least for pathogens of similar size or smaller. Because of the highly reversible nature of organic colloid immobilization in this soil type, C. parvum could contaminate surface water should overland flow during heavy precipitation events pick up near-surface grains to which they are attached. Surprisingly, oocyst and microsphere attachment to the reference soil from Illinois appeared to be at least as sensitive to changes in pH as was observed for the red, metal-oxide rich soil from Oahu. In contrast, colloidal attachment in the organic-rich, volcanic ash soil was relatively insensitive to changes in pH in spite of the high iron content. Given the fundamental differences in transport behavior of oocyst-sized colloids within the two volcanic soils of similar origin, agricultural practices modified to lessen C. parvum contamination of ground or surface water would necessitate taking the individual soil properties into account.
为了深入了解微小隐孢子虫卵囊在热带火山土壤中的命运,研究了两种土壤中卵囊和卵囊大小聚苯乙烯微球的迁移和附着行为。选择这些土壤是因为它们具有不同的化学和物理性质,即来自夏威夷岛的富含有机物(质量分数为 43-46%)的火山灰衍生土壤,以及来自瓦胡岛的红色、铁(质量分数为 22-29%)、铝(质量分数为 29-45%)和粘土丰富(质量分数为 68-76%)的火山土壤。还包括伊利诺伊州的一种农业土壤,即富含有机物(质量分数为 13%)和石英(质量分数为 40%)的土壤作为参考。在 10 厘米长的穿透流柱中,通过红色火山土壤的卵囊和微球几乎完全(98%和 99%)被固定。适度的突破是由于土壤颗粒在重新润湿过程中团聚而无意中形成的优先流路径结构造成的。尽管最初在火山灰土壤中卵囊和微球的去除率很高(99%),但进一步的研究表明,由于与颗粒表面的高度可逆相互作用,运输只是被延迟了。从 1.8μm 微球实质性且持久的突破曲线的斜率来看,几乎所有(>99%)都可以在大约 4000 个孔隙体积内回收。这表明,一旦受到污染,火山灰土壤可能成为地下水随后污染的储层,至少对于大小相似或更小的病原体而言是如此。由于这种土壤类型中有机胶体固定的高度可逆性,微小隐孢子虫可能会污染地表水,如果在强降水事件中地表水携带了它们附着的近地表颗粒,就会发生这种情况。令人惊讶的是,伊利诺伊州土壤中卵囊和微球的附着对 pH 值的变化似乎至少与瓦胡岛富金属氧化物土壤一样敏感。相比之下,尽管铁含量很高,但在富含有机物的火山灰土壤中胶体的附着对 pH 值的变化相对不敏感。鉴于两种起源相似的火山土壤中卵囊大小胶体的迁移行为存在根本差异,为减少微小隐孢子虫对地下水或地表水的污染而修改的农业实践将需要考虑到个别土壤特性。