使用防水性日本雪松(Cryptomeria japonica)森林土壤的热量对不同深度森林土壤防水性的影响

Perera H.T.M., Mori Y., Maeda M., Leelamanie D.A.L.
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引用次数: 0

摘要

一些植物物种(如桉树、松树、桉树、雪松和柏树)下的土壤呈现出拒水状态。野火在以这些植物物种为主的森林中很常见,因为它们会产生极易燃烧的碎屑。野火产生的热量会改变土壤特性,包括土壤憎水性(SWR)。根据加热温度和土壤深度的不同,SWR 对热量的反应也会不同。本研究旨在通过日本雪松(Cryptomeria japonica)森林土壤的土壤剖面,研究不同加热温度对 SWR 的影响。土壤样本从四个不同深度(0-5、5-10、10-15、15-20 厘米)采集。使用可编程马弗炉将土壤分别置于七种加热温度(TH)(50、100、150、200、250、300 和 350°C)下加热 1 小时。使用乙醇液滴摩尔度测试和水滴渗透时间(WDPT)测试分别测量了加热和未加热样品中的 SWR 度(接触角)和持久性。在非加热土壤中,0-5 厘米层的 SWR 最高(接触角 ~110°;WDPT≥3600 秒)。SWR 随深度的增加而减小,在 15-20 厘米处为无排斥性(接触角≤90°;WDPT≤1 秒)。在加热样品中,0-5、5-10 和 10-15 厘米土层的 SWR 随 TH 的增加而降低,而 15-20 厘米土层的选择在所有处理中都是非斥性的。0-5 厘米深度的土壤在 200 摄氏度时表现出极强的 SWR(WDPT=≥3600 秒),在 250 摄氏度时变得不驱避;5-10 厘米深度的土壤在 150 摄氏度时表现出极强的 SWR,在 200 摄氏度时表现出严重的 SWR(WDPT~1350 秒),在 250 摄氏度时变得不驱避。结果表明,具有较高 SWR 的上层土壤需要较高的 TH 值才能变得不驱避,而具有较低 SWR 的下层土壤则在较低 TH 值时变得不驱避。有必要进行进一步的实验,以确定有机物分子水平在热量对 SWR 的影响下发生的变化。 关键词隐花植物 实验室加热 土壤憎水性 野火
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Impact of Heat on Soil Water Repellency in Forest Soils from Different Depths using Water-Repellent Japanese Cedar (Cryptomeria japonica) Forest Soil
ome soils under plant species, such as casuarina, pine, eucalyptus, cedar, and cypress, show water- repellent conditions. Wildfires are common in forests dominated by these plant species as they produce highly flammable debris. The heat generated during wildfires alters soil characteristics, including soil water repellency (SWR). The responses of SWR to heat can differ depending on the heating temperature and the soil depth. This study aimed to examine the effects of different heating temperatures on SWR through a soil profile using Japanese cedar (Cryptomeria japonica) forest soil in Japan. Soil samples were collected from four different depths (0-5, 5-10, 10-15, 15-20 cm). Soils were exposed to heat with seven heating temperatures (TH) (50, 100, 150, 200, 250, 300, and 350° C) separately for 1 h using a programmable muffle furnace. The degree (contact angle) and the persistence of SWR in both heated and non-heated samples were measured using the molarity of an ethanol droplet test and the water drop penetration time (WDPT) test, respectively. In non-heated soils, the 0-5 cm layer showed the highest SWR (contact angle ~110°; WDPT≥3600 s). SWR decreased with depth to be non-repellent at 15-20 cm (contact angle≤90°; WDPT≤1 s). In heated samples, SWR of 0-5, 5-10, and 10-15 cm layers decreased with increasing TH, while the selection from 15-20 cm was non-repellent in all treatments. Soils of 0-5 cm depth showed extreme SWR (WDPT=≥3600 s) up to 200° C and became non-repellant at 250° C, while those of 5-10 cm showed extreme SWR up to 150° C, severe SWR (WDPT~1350 s) at 200° C, and became non- repellent at 250° C. The soils from 10-15 cm showed severe SWR (WDPT~2100 s) at TH of 50° C and became non-repellent at 100° C. Results revealed that upper soil layers with higher SWR required higher TH to become non-repellent, and soils from lower layers with lower SWR became non-repellent at lower TH. Further experiments are necessary to identify the changes in molecular levels of organic matter in response to the impacts of heat on SWR.  Keywords: Cryptomeria japonica, Laboratory heating, Soil water repellency, Wildfires
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