2019
DOI: 10.1016/j.chemosphere.2019.06.127
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Photochemical release of dissolved organic matter from particulate organic matter: Spectroscopic characteristics and disinfection by-product formation potential

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Cited by 39 publications
(14 citation statements)
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“…For surface water, those ratios were even 2 times larger than the DOC/POC ratios, probably because unsaturated organic matter in particles is likely to photodissolve into the water phase, as demonstrated in previous studies. 13,62 The hardness and bivalent cations like Mg 2+ and Ca 2+ are other factors affecting the DOM/POM ratios. 23 Groundwater has higher hardness than surface water, as shown in Table S2 (SI).…”
Section: Sample Analysismentioning
confidence: 99%
“…For surface water, those ratios were even 2 times larger than the DOC/POC ratios, probably because unsaturated organic matter in particles is likely to photodissolve into the water phase, as demonstrated in previous studies. 13,62 The hardness and bivalent cations like Mg 2+ and Ca 2+ are other factors affecting the DOM/POM ratios. 23 Groundwater has higher hardness than surface water, as shown in Table S2 (SI).…”
Section: Sample Analysismentioning
confidence: 99%
“…C2(E x /E m :265/496 nm)属于疏水性高分子类腐殖酸物质 [32] ,是由复杂分子结构的腐殖质产生, 通常来源于植物残体等的腐烂和降解产物 [41,42] ;C3(E x /E m :200, 289/294 nm)属于类蛋白质样荧光 团 [43] ,由新鲜植物的凋落物产生 [44] 。由于发射波长与高分子量腐殖质类结构的数量呈正相关关 系,与 C1 相比,C2 组分具有较大的发射波长,因此 C2 组分具有更高的疏水性和更大的分子尺 寸,C2 可以被鉴定为一种高分子量的陆生源腐殖酸,广泛分布在湿地和森林土壤环境中 [30,31] , 此结果与之前的研究结果相似 [41,45][19] ,因此,DOM 三种组分的 变化特征说明在沙生植物对沙地恢复的过程中, 植被凋落物和微生物降解产物为土壤腐殖质的产 生提供了重要来源,进一步加速土壤腐殖质化,提高了有机质与土壤碳储量,有效地促进土壤中 类腐殖酸和类富里酸的积累 [46] 。在不同的植被覆盖地,草地的类腐殖质组分(C1 和 C2)的比例仅 次于杨树区和油松区,是由于草本植物根系发达且主要密集于表层,根系分泌物和死亡的根系可 为微生物提供丰富的能源物质 [47] ,易促进土壤微生物生长 [48] ,从而有利于根系分解而生成腐殖 化物质稳定下来。除草地外的植被覆盖地中,不同的树种类型类腐殖质组分(C1 和 C2)的比例有…”
Section: 土壤中unclassified
“…11,[21][22][23][24] For example, humic-like components identied by PARAFAC were linked to different sources of DOM (e.g., terrestrial and microbial) and were shown to have dissimilar treatability during water and waste treatment. 21,25,26 Some studies have indicated a high correlation between trihalomethane formation potential (THMsFP) and some PAR-AFAC components in natural aquatic environments 27,28 and in laboratory-scale water treatments. 29 In another study, ve EEM-PARAFAC components, including four terrestrially derived humic-like substances (C1, C2, C3, and C4) and one tryptophanlike substance (C5), were identied in the sub-alpine Lake Tiancai.…”
Section: Introductionmentioning
confidence: 99%