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Valorization of faecal and sewage sludge via pyrolysis for application as crop organic fertilizer

机译:粪便和污水污泥通过热解的算法作为作物有机肥

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In developing countries, faecal sludge treatment facilities are non-existent in most cities and small towns resulting in untreated and improper disposal of sludge. In Ghana 85 % of faecal sludge produced each day is discharged into the earth with no effective treatment. Converting sewage and faecal sludge to biochar addresses the stigma of fertilizer obtained from human excreta, since the pyrolysis process guarantees a 100 % pathogen elimination, and enrich nutrients in faecal sludge biochar. The interest to convert sludge waste into biochar is that it ensures a pathogen free fertilizer. Sewage sludge and faecal sludge with sawdust were pyrolysed at different temperatures in this study. Sewage sludge (SSB1 -300 degrees C, 55B2-450 degrees C and 55B3-600 degrees C) as well as faecal sludge with sawdust (CTB1-300 degrees C, CTB2-450 degrees C and CTB3-600 degrees C) were both converted to biochar at 300 degrees C, 450 degrees C and 600 degrees C, respectively using an electric kiln. Physicochemical parameters such as Total Nitrogen (TN), Total Potassium (TK), Total Phosphorous (TP), Calcium (Ca), Magnesium (Mg), Organic Carbon (OC), Organic Matter (OM), Cadmium (Cd), Arsenic (As), Ash content, pH, Electrical Conductivity (EC), Moisture content, Porosity and Bulk Density and germination test were performed. It was found that at 300 degrees C nitrogen content, organic matter, bulk density, biochar yield and moisture content were high, and longer root lengths were observed as well. Biochars produced at 450 degrees C produced the longest shoot lengths. Also, biochars produced at 600 degrees C had high phosphorous, potassium, calcium and magnesium levels, high porosity, pH and high heavy metal concentration as well. The outcomes demonstrate that biochars produced at higher temperatures are high in heavy metal concentration, but were within acceptable limits for application in agriculture. Biochar produced at moderately lower temperature is favourable for agriculture purposes. SSB1-300 degrees C, SSB2-450 degrees C, CTB1 - 300 degrees C and CTB2 -450 degrees C had moderate pH and ash levels and so are less toxic to the growth of plants. Faecal sludge biochar produced at the three temperatures were suitable for use as fertilizer. The conversion of sludge waste into biochar will help improve faecal sludge management.
机译:在发展中国家,大多数城市和小城镇都不存在粪便污泥处理设施,导致污泥处置未经治疗和不当。加纳,每天生产的粪便污泥的85%被排入地球,没有有效的治疗。将污水和粪便污泥转化为生物炭地址从人排泄物获得的肥料的耻骨,因为热解过程保证了100%的病原体消除,并富集粪便污泥BioChar中的营养。将污泥废物转化为生物炭的兴趣是它确保了一种病原体自由肥料。污水污泥和粪便污泥在本研究中的不同温度下被热解。污水污泥(SSB1 -300℃,55b2-450 c和55b3-600c)以及粪便污泥(CTB1-300c,CTB2-450 C和CTB3-600c)都转换在300摄氏度,450摄氏度和600摄氏度的BioChar分别使用电窑。诸如总氮(TN),总钾(TK),总磷(TP),钙(CA),镁(OC),有机物(OM),镉(CD),砷,砷(CD),砷(CD),砷(CD),砷(CD),砷(AS),进行灰分含量,pH,电导率(EC),水分含量,孔隙率和散装密度和萌发试验。发现,在300℃的氮含量下,有机物,堆积密度,生物炭产率和水分含量高,并且也观察到更长的根长度。在450摄氏度下产生的生物触发器产生了最长的枝条。此外,在600摄氏度下产生的生物脉基也具有高磷,钾,钙和镁水平,孔隙率高,pH和高重金属浓度。结果表明,在较高温度下产生的生物脉质量高,重金属浓度高,但在农业中的应用范围内是可接受的。生物炭在适度较低的温度下产生有利于农业目的。 SSB1-300度C,SSB2-450℃,CTB1 - 300摄氏度和CTB2 -450 C具有中等的pH和灰分水平,对植物的生长且毒性的生长较小。在三个温度下生产的粪便污泥生物炭适用于肥料。污泥废物转化为生物炭,有助于提高粪便污泥管理。

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