洗车洗涤剂和生物表面活性剂(鼠李糖脂)对土壤环境的比较效果:寻找更环保的替代品

Rinret Anthony Best, Jalmet Sinkit Youmnan, Tama Sudhir Caleb, Rejoice Helma Abimiku
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引用次数: 0

摘要

目的:研究合成洗车水和生物基表面活性剂生物张紧素对土壤环境的影响。研究设计:评价研究。学习地点和时间:2018年,基尔大学威廉·史密斯大楼地质与林地实验室。方法:从当地商店购买1000 g表土,在1100C烤箱中干燥24小时,测定其水分含量。100g土壤用稀释的洗涤剂和清洗液灌溉5天。收集渗滤液进行pH、电导率(EC)分析,并用红外光谱(IR)进一步分析,并用x射线荧光(XRF)机对土壤样品颗粒进行分析。结果:经物理观察,土壤渗滤液的颜色在自来水中基本保持清澈,在生物张力剂中呈浅黄色,在洗车剂中呈深棕色。同一时期,不同样品的土壤渗滤液pH值介于中性和轻度碱性之间。然而,对于EC,记录的最大EC是在用洗车洗涤剂(1157、1181、1242、1390和1876µS/cm)灌溉的土壤中,所有5天。然后用BioTensidon(732、757、796、799和836µS/cm)灌溉土壤,同时用自来水(456、487、500、505和553µS/cm)灌溉土壤,记录5天的最低EC。土壤渗滤液的红外光谱分析结果显示,每天采集的3种渗滤液的峰值没有差异,而XRF分析结果显示,所分析样品的主要元素SiO2、Al2O3和Fe2O3占主导地位。结论:两种洗涤剂的成分组成相似。众所周知,其中一些成分对人体、土壤、水和植物有害,这些成分在不同的洗涤剂之间有所不同。这两种洗涤剂也有相似的微量元素组成,这些微量元素是植物生长所必需的,有些对植物有毒。然而,洗车洗涤剂中没有显示出铅元素(Pb)。经物理检测,洗车洗涤剂显著漂白了表层土壤的有机组分。与生物表面活性剂相比,经过5天的洗车洗涤剂测试,土壤pH值增加了8%,土壤EC增加了43%。此外,生物表面活性剂含有一些有毒浓度,可能是不安全的。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Comparative Effects of Car Wash Detergents and Biosurfactants (Rhamnolipids) on the Soil Environment: In Search of a Greener Alternative
Aims: This study investigates the comparative effects of synthetic car wash and a bio-based surfactant detergent, biotensidon, on the soil environment. Study Design: Evaluation studies. Place and Duration of Study: Geology and Woodland laboratory at William Smith Building, University of Keele, in 2018. Methodology: 1000 g of Topsoil purchased from a local store was dried in the oven at 1100C for 24 hours and its moisture content was determined. 100 g of the soil was irrigated with diluted detergents and cleaning solutions for 5 days. The leachates were then collected and analyzed for pH and Electrical Conductivity (EC) and further analyzed with Infrared Spectroscopy (IR) while the soil sample pellets were with X-Ray Fluorescence (XRF) machine. Results: The colour of soil leachate when physically observed was consistently almost clear for tap water, light yellow for the biotensidon detergent and dark brown for the car wash detergent. For the pH for the same period, the soil leachates were between neutral and mildly alkaline among the different samples. However, for EC, the maximum EC recorded was in soil irrigated with Car Wash Detergent (1157, 1181, 1242, 1390 and 1876 µS/cm) for all of the 5 days. This is followed by soil irrigated with BioTensidon (732, 757, 796, 799 and 836 µS/cm) for the same period while the minimum EC was recorded in soil irrigated with tap water (456, 487, 500, 505 and 553 µS/cm) for the 5 days. The IR analysis of soil leachates showed peak values that did not differ with all the three leachates collected each day, while the XRF analysis showed the major elements SiO2, Al2O3 and Fe2O3 to be the most dominant for analyzed samples. Conclusion: Both detergents examined had similar compositions of ingredients for making detergents. Some of these ingredients are well known to be harmful to humans, soil, water and plants, and these compositions vary between the detergents. Both detergents also have similar compositions of microelements that are essential for plant growth and some that are toxic to plants. However, the car wash detergents showed no amount of the element Lead (Pb). The car wash detergents significantly bleached organic fractions of the topsoil when examined physically. An 8% soil pH increase and 43% soil EC increase were recorded after 5 days of testing by car wash detergents when compared to the biosurfactants. Also, biosurfactants were shown to contain some toxic concentrations that may be unsafe.
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