CN108889268A - 一种改性废弃水泥块在去除雨水中磷方面的应用 - Google Patents

一种改性废弃水泥块在去除雨水中磷方面的应用 Download PDF

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CN108889268A
CN108889268A CN201810808502.5A CN201810808502A CN108889268A CN 108889268 A CN108889268 A CN 108889268A CN 201810808502 A CN201810808502 A CN 201810808502A CN 108889268 A CN108889268 A CN 108889268A
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phosphorus
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于江华
陶柄臣
黄啸谷
蔡昱
龚超
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Nanjing University of Information Science and Technology
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Abstract

本发明公开了一种改性废弃水泥块在去除雨水中磷方面的应用,所述改性废弃水泥块由如下方法制备而成:在常温下,将1mol/L铁盐溶液和0.5mol/L铝盐溶液与1mol/L氢氧化钠溶液1:1:5.4混合,其中加入经过预处理的废弃水泥块,使混合液与砖块的固液比为1:3,并在常温下使用恒温振荡器进行混合,在4h后取出水泥块,放入烘箱干燥后使用马弗炉灼烧,取出,蒸馏水洗净。本方法实现了废弃水泥块的再利用,节约了大量可再生利用的资源并对雨水径流中的磷的吸附的同时也做到了保护环境,发展循环经济的特点。

Description

一种改性废弃水泥块在去除雨水中磷方面的应用
技术领域
本发明专利涉及一种改性废弃水泥块去除雨水中磷的方法,属于含磷污水的处理领域。
背景技术
城市非点源污染问题是伴随城市快速发展而出现的新问题,长期以来,农业非点源污染已经引起了广泛的重视,但是对城市非点源污染的研究相对较少.近年来,随着环保工作力度的不断加大,城市点源污染基本上已经得到了较好控制,非点源污染就成为了城市水质恶化的主要原因之一。而在多种非点源污染类型中,城市降雨径流是仅次于农业的非点源污染的第二大污染源。目前,城市水体面临的主要问题为富营养化,因而城市降雨径流中对水体影响最大、效果最为直观的为磷类化合物。如何处理径流中的磷成为了需要解决的问题。
同时,进入21世纪以来,我国基础设施建设事业得到了飞速发展。伴随着道路、桥梁、楼房的建设,产生了大量废弃水泥混凝土。据不完全统计,2018年我国建筑物拆除和施工过程中产生废混凝土总量达3.5亿t左右,预计到2020年我国将产生20亿t废弃水泥混凝土。目前,我国绝大部分废弃水泥混凝土是作为垃圾处理的,这不仅对环境造成了巨大影响,也浪费了大量可再生利用的资源。
随着人们保护环境、节约资源、发展循环经济意识的增强,再生集料的推广应用逐渐成为一种趋势。针对普通的硅酸盐水泥的主要化学成分为氧化钙、二氧化硅、三氧化二铁、三氧化二铝,本专利通过同时使用铁盐,铝盐对废弃水泥块的改性,制备新型的除磷材料,将再生集料的主要应用于路面基层、底基层或路基与园林绿化结构物填料中,对控制雨水径流中的磷污染与遏制城市水体富营养化具有重要意义。
发明内容
本发明旨在提供一种具有可以有效吸附雨水径流中的磷的改性废弃水泥块用于去磷。
本发明的上述目的是通过下面的技术方案得以实现的:
一种改性废弃水泥块在去除雨水中磷方面的应用,改性废弃水泥块由如下方法制备而成:
在常温下,将1mol/L铁盐溶液和0.5mol/L铝盐溶液与1mol/L氢氧化钠溶液1:1:5.4混合,其中加入经过预处理的废弃水泥块,使混合液与砖块的固液比为1:3,并在常温下使用恒温振荡器进行混合,在4h后取出水泥块,放入烘箱干燥后使用马弗炉灼烧,取出,蒸馏水洗净;
其中,废弃水泥块的预处理方法为:将回收的废弃砖水泥块进行粉碎研磨,过筛,选取0.5-1mm粒径的粉末,进行清洗,烘干,收集备用。
优选地,所述铁盐为三氯化铁。
优选地,所述铝盐为三氯化铝。
优选地,灼烧温度为600℃,灼烧时间为6h。
优选地,预处理方法中烘干温度为100℃。
有益效果:
(1)采用铁盐铝盐和氢氧化钠联合的方法改性的废弃水泥块,具有较好的除磷能力,其磷的吸附率由原来的未改性废弃水泥块的28%增加到63.36%,这一吸附效果远高于等量的废弃水泥块的吸附除磷量。
(2)本方法实现了废弃水泥块的再利用,节约了大量可再生利用的资源并对雨水径流中的磷的吸附的同时也做到了保护环境,发展循环经济的特点。
具体实施方式
下面结合实施例具体介绍本发明实质性内容,但并不以此限定本发明的保护范围。
实施例1
本发明改性废弃水泥块去除水中磷的方法,包括以下步骤:
1、废弃水泥块的预处理过程:
将回收的废弃水泥块块进行粉碎研磨,过筛,选取0.5-1mm粒径的粉末,进行清洗,在100℃下烘干,收集备用。
2、废弃水泥块改性过程:
在25℃下,将1mol/L铁盐溶液和0.75mol/L铝盐溶液与1mol/L氢氧化钠溶液1:1:5.4混合其中加入经过预处理的废弃水泥块,使混合液与砖块的固液比为1:3,并在常温下使用恒温振荡器进行混合,在4h后取出砖块,放入烘箱干燥后使用马弗炉在600℃下进行灼烧,灼烧6h后取出改性后的水泥块,用蒸馏水洗净后干燥收集备用。
3、改性后砖块除磷过程:
称取0.5g的上述改性废弃砖块加入浓度为5mg/L的50ml的含磷溶液中,溶液pH为7,在25℃下,以160r/min的速度进行恒温振荡。22h后过0.45μm滤膜,用钼锑抗比色法测滤液中磷的浓度,测得改性后水泥块对磷的吸附率为63.36%。
实施例2用0.5g废弃水泥块直接吸附
实施例3用0.1mol/L铁盐溶液和0.75mol/L铝盐溶液
实施例4用0.25mol/L铁盐溶液和0.75mol/L铝盐溶液改性
实施例5用0.75mol/L铁盐溶液和0.75mol/L铝盐溶液
实施例6用0.75mol/L铁盐溶液和0.5mol/L铝盐溶液
实施例7用0.75mol/L铁盐溶液和0.1mol/L铝盐溶液
实施例2中将0.5g废弃水泥块,加入浓度为5mg/L的50ml的含磷溶液,在25℃的温度下以转速160r/min的速度进行恒温振荡22h,后经过0.45μm滤膜进行过滤,测得水泥块对磷的吸附率为28%。在后续的试验中发现,该吸附在22h时达到平衡,即使时间增加,吸附量也没有很大变化。
由实施例1、2可以看出,改性废弃水泥块对水中磷的去除效果远远高于等量的废弃水泥块的吸附效果。
实施3、4、5仅改变了铁盐浓度其他步骤与实施1的相同,实施3、4、5最后得到吸附率为60%,61%,63.05%。
由实施例1、3、4、5可以看出,在吸附平衡时,铁盐的浓度越高,吸附率越高。
实施6、7仅改变了铝盐浓度其他步骤与实施1的相同,实施6、7最后得到吸附率为63.05%,63.29%,在吸附平衡时,铝盐的浓度越高,会提升吸附效果但效果不高。
上述实施例的作用在于具体介绍本发明的实质性内容,但本领域技术人员应当知道,不应将本发明的保护范围局限于该具体实施例。

Claims (5)

1.一种改性废弃水泥块在去除雨水中磷方面的应用,其特征在于,所述改性废弃水泥块由如下方法制备而成:
在常温下,将1mol/L铁盐溶液和0.5mol/L铝盐溶液与1mol/L氢氧化钠溶液1:1:5.4混合,其中加入经过预处理的废弃水泥块,使混合液与砖块的固液比为1:3,并在常温下使用恒温振荡器进行混合,在4h后取出水泥块,放入烘箱干燥后使用马弗炉灼烧,取出,蒸馏水洗净;
其中,废弃水泥块的预处理方法为:将回收的废弃砖水泥块进行粉碎研磨,过筛,选取0.5-1mm粒径的粉末,进行清洗,烘干,收集备用。
2.根据权利要求1所述的应用,其特征在于:所述铁盐为三氯化铁。
3.根据权利要求1所述的应用,其特征在于:所述铝盐为三氯化铝。
4.根据权利要求1所述的应用,其特征在于:灼烧温度为600℃,灼烧时间为6h。
5.根据权利要求1所述的应用,其特征在于:预处理方法中烘干温度为100℃。
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