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Ammonia Release from Concrete Containing Ammoniated Fly Ash

机译:含氨粉煤灰的混凝土中的氨释放

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The presence of ammonia in fly ash, resulting from the injection of ammonia to controlNO_x emissions, could create a major barrier to the utilization of fly ash in concrete.Practical guidelines for the handling and utilization of ammoniated fly ash are needed tohelp maintain the existing concrete and cement markets, which is the overall goal of thisproject. Specifically, the objective of our work is to determine the amount of ammoniathat is released, over the short- and long-term, from concrete that contains ammoniatedfly ash. The technical approach has been to prepare mortar and concrete slabs andmonitor the loss of ammonia during mixing, the concentration in the air-space above theslabs soon after placement, and the total quantity of ammonia evolved over a longertime period. Variables tested include temperature, ventilation rate, water:cementitiousmaterial (W:C) ratio, and fly ash source. The data indicate that for concrete placed inareas with poor air ventilation the fly ash NH3 concentration should not exceed 110 to170 mg/kg, depending on the water:cement ratio and the fly ash replacement rate, if anexposure limit of 10 ppm is not to be exceeded. Longer-term experiments showed thatthe ammonia loss rate is independent of fly ash source and W:C ratio.
机译:粉煤灰中存在氨,这是由于注入氨来控制 NO_x排放可能对混凝土中粉煤灰的利用形成主要障碍。 需要处理和利用氨化粉煤灰的实用指南,以 帮助维护现有的混凝土和水泥市场,这是此项目的总体目标 项目。具体来说,我们的工作目标是确定氨的含量 短期或长期从含氨的混凝土中释放出来 粉煤灰。技术方法是准备砂浆和混凝土板,然后 监测混合过程中氨气的损失,上方空气空间的浓度 放置后不久便会产生厚板,氨的总量会在较长的时间内放出 时间段。测试的变量包括温度,通风速率,水:胶结物 物料(W:C)比率和粉煤灰来源。数据表明,对于混凝土 空气流通不良的地区,粉煤灰NH3的浓度不应超过110至 170 mg / kg,取决于水:水泥的比例和粉煤灰的替代率,如果 不得超过10 ppm的暴露极限。长期实验表明 氨的损失率与粉煤灰源和W:C比无关。

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