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Dewatering sludge originating in water treatment works in reed bed systems

机译:芦苇床系统中水处理厂产生的脱水污泥

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The dewatering process of the liquid water works sludge was examined in a trial with a series of sixntrial beds, each 20 m2n. These were monitored from April 2008 to June 2010. It is possible to get thenvegetation to grow in ferric sludge (∼300,000 mg Fe/kg dry solid, pH 7,7). It has not been necessary tonuse fertilizer. The influence of the loading programs (15–50 kg dry solid/m2n/year) was tested with 1–5ndays of loading and 35–55 days of rest. It is possible to drain and treat ferric sludge. Generally thendewatering profile is a peak with a maximum over 0.015–0.025 L/s/m2n. The times for dewatering ofn6–12 m3nare ∼15 h and over 90% of the load is dewatered in that period. The dry solid (0.16–0.20%)nin the sludge has been concentrated ∼200 times. The dewatering phase results in ferric sludgenwith 30–40% dry solid which cracks up very quickly. The volume reduction is over 99%. The trendnshows that the main volume of reject water has a turbidity level below 5 NTU even in the loadingnperiods.
机译:在一个试验中,对液态水厂污泥的脱水过程进行了试验,该试验有一系列的六层床,每层20平方米。从2008年4月至2010年6月对这些植物进行了监测。然后有可能使植物在铁淤泥中生长(约300,000 mg Fe / kg干固体,pH 7.7)。没必要使用吨肥。测试了加载程序的影响(15–50 kg干固体/ m2n /年),加载了1-5n天,休息了35-55天。可以排放和处理铁污泥。通常,脱水曲线是一个峰值,最大值超过0.015-0.025 L / s / m2n。脱水时间为6-12 m3 nare〜15 h,在此期间脱水量超过90%。污泥中的干燥固体(0.16-0.20%)已浓缩约200倍。脱水阶段会产生含铁量为30%至40%的干燥固体铁,其裂解速度非常快。体积减少超过99%。趋势表明,即使在装料期,主要废水的浊度也低于5 NTU。

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