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垃圾渗滤液:温带喜马拉雅地区土壤质量的隐形威胁。

Landfill leachate: An invisible threat to soil quality of temperate Himalayas.

机构信息

Division of Environmental Sciences, SKUAST K, Srinagar, Jammu and Kashmir, India.

Division of Basic Science and Humanities, SKUAST K, Srinagar, Jammu and Kashmir, India.

出版信息

PLoS One. 2024 Nov 19;19(11):e0314006. doi: 10.1371/journal.pone.0314006. eCollection 2024.

DOI:10.1371/journal.pone.0314006
PMID:39561139
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11575778/
Abstract

Landfills are the most affordable and popular method for managing waste in many parts of the world, However, in most developing nations, including India, the infiltration of hazardous materials from improperly managed dumping site continues to be a significant environmental problem. Around the world, leachate is a significant point source of contamination in numerous environmental media, including soil, groundwater, and surface water. Soil is an important asset as it is the key factor for food production and has tremendous significance in achieving sustainable development goals (SDGs). The contaminants from soil enter into food chain and ultimately reach humans. So in order to prevent the adverse effects of toxic elements on humans, there is need to maintain the soil quality and to prevent deterioration. Keeping in view the consequences of unscientific management of waste, the goal of the experiment was to determine how landfill leachate from Achan landfill affected the soil quality in the temperate Himalayas. All four seasons of the year, viz Spring, Summer, Autumn, and Winter, at four sites viz, Center of dumping site, inside, Outside and Control were monitored. Among sites center was found to have maximum value of EC (3.04 dS/m), Moisture content (42.51%), N (285.43 mg/kg), P (70.07 mg/kg), K (265.71 mg/kg), Ca (957.67 mg/kg), Mg(402.42 mg/kg), Zn (2.02 mg/kg), Fe (10.56 mg/kg), Cu (2.07 mg/kg), Mn (10.73 mg/kg), Pb (85.02 mg/kg), Cd (4.50 mg/kg), Ni (29.04 mg/kg), Cr (23.37 mg/kg), As (14.10 mg/kg). While as the lowest value of all parameters was reported at control site. From the study it is recommended that the waste generated is mostly organic (65-75%), thus can be segregated and treated at source. The waste can be treated at source using microbial consortium technology in order to transform the waste in to wealth in a sustainable way and to prevent the deterioration of soil quality.

摘要

垃圾填埋场是世界上许多地区管理废物的最具成本效益和最受欢迎的方法。然而,在包括印度在内的大多数发展中国家,管理不善的倾倒场的有害物质渗透仍然是一个重大的环境问题。在全球范围内,渗滤液是许多环境介质(包括土壤、地下水和地表水)中重要的点污染源。土壤是一种重要的资产,因为它是粮食生产的关键因素,对实现可持续发展目标具有巨大意义。土壤中的污染物进入食物链,最终到达人类。因此,为了防止有毒元素对人类产生不利影响,需要保持土壤质量,防止其恶化。鉴于废物管理不善的后果,实验的目的是确定阿昌垃圾填埋场的垃圾渗滤液如何影响喜马拉雅山温带地区的土壤质量。在四个不同的地点,即垃圾场中心、内部、外部和对照点,监测了一年中的四个季节,即春季、夏季、秋季和冬季。结果发现,中心地点的电导率(3.04 dS/m)、含水量(42.51%)、氮(285.43 mg/kg)、磷(70.07 mg/kg)、钾(265.71 mg/kg)、钙(957.67 mg/kg)、镁(402.42 mg/kg)、锌(2.02 mg/kg)、铁(10.56 mg/kg)、铜(2.07 mg/kg)、锰(10.73 mg/kg)、铅(85.02 mg/kg)、镉(4.50 mg/kg)、镍(29.04 mg/kg)、铬(23.37 mg/kg)和砷(14.10 mg/kg)的含量最高。而所有参数的最低值都在对照点报告。因此,建议对产生的废物进行分类,在源头进行处理。可以使用微生物联合体技术在源头处理废物,以可持续的方式将废物转化为财富,并防止土壤质量恶化。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/0065be18fdf5/pone.0314006.g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/702c669ae71e/pone.0314006.g001.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/688267ec15cc/pone.0314006.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/94f084c21a5e/pone.0314006.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/884ab065fb77/pone.0314006.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/4275b0544609/pone.0314006.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/ffcb15cb4491/pone.0314006.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/0cf26f3c1681/pone.0314006.g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/0065be18fdf5/pone.0314006.g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/702c669ae71e/pone.0314006.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/edb6f46d7230/pone.0314006.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/688267ec15cc/pone.0314006.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/94f084c21a5e/pone.0314006.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/884ab065fb77/pone.0314006.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/4275b0544609/pone.0314006.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/ffcb15cb4491/pone.0314006.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/0cf26f3c1681/pone.0314006.g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/1deb/11575778/0065be18fdf5/pone.0314006.g009.jpg

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