CN115301201A - Volcanic ash soil-based adsorbent for enriching phosphorus in water body and preparation method and application thereof - Google Patents
Volcanic ash soil-based adsorbent for enriching phosphorus in water body and preparation method and application thereof Download PDFInfo
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- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 title claims abstract description 124
- 239000011574 phosphorus Substances 0.000 title claims abstract description 124
- 229910052698 phosphorus Inorganic materials 0.000 title claims abstract description 124
- 239000002689 soil Substances 0.000 title claims abstract description 77
- 239000003463 adsorbent Substances 0.000 title claims abstract description 64
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 20
- 238000002360 preparation method Methods 0.000 title claims abstract description 7
- 239000010865 sewage Substances 0.000 claims abstract description 49
- 239000000843 powder Substances 0.000 claims abstract description 25
- 239000010453 quartz Substances 0.000 claims abstract description 21
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 21
- 238000000034 method Methods 0.000 claims abstract description 18
- 239000002994 raw material Substances 0.000 claims abstract description 10
- 238000012851 eutrophication Methods 0.000 claims abstract description 4
- 238000002156 mixing Methods 0.000 claims abstract 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 19
- 229910017604 nitric acid Inorganic materials 0.000 claims description 19
- 239000000203 mixture Substances 0.000 claims description 13
- 239000002351 wastewater Substances 0.000 claims description 10
- 239000011812 mixed powder Substances 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 6
- 239000003610 charcoal Substances 0.000 claims 2
- 238000001035 drying Methods 0.000 claims 1
- 238000010438 heat treatment Methods 0.000 claims 1
- 235000011837 pasties Nutrition 0.000 claims 1
- 239000010802 sludge Substances 0.000 abstract description 13
- 230000000694 effects Effects 0.000 abstract description 11
- -1 biochar Substances 0.000 abstract description 8
- 230000035558 fertility Effects 0.000 abstract description 7
- 239000000463 material Substances 0.000 abstract description 5
- 238000004519 manufacturing process Methods 0.000 abstract description 2
- 239000008239 natural water Substances 0.000 abstract 1
- 238000001179 sorption measurement Methods 0.000 description 13
- 239000002245 particle Substances 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 5
- 229910019142 PO4 Inorganic materials 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 239000010452 phosphate Substances 0.000 description 3
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 230000004069 differentiation Effects 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000002344 surface layer Substances 0.000 description 2
- 238000010170 biological method Methods 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 239000002734 clay mineral Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 230000003628 erosive effect Effects 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 239000003864 humus Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000008439 repair process Effects 0.000 description 1
- 239000002594 sorbent Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 239000005335 volcanic glass Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/103—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/12—Naturally occurring clays or bleaching earth
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
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- Chemical & Material Sciences (AREA)
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Abstract
Description
技术领域technical field
本发明属于污水处理领域,具体涉及一种基于火山灰土富集水体中磷的吸附剂及其制备方法与应用。The invention belongs to the field of sewage treatment, and in particular relates to an adsorbent for enriching phosphorus in water bodies based on volcanic ash soil and its preparation method and application.
背景技术Background technique
火山灰土为在第四纪火山活动区由火山灰母质形成的各种土壤。分布在世界各地近代火山活动较频繁的地区,在中国的分布面积很小。有些发育程度较深的火山灰土剖面出现明显分化,肥力较高。这种土壤的特点是土壤质地较粗,孔隙度高,受侵蚀危害较大,并含有大量火山起源矿物。Volcanic ash soil is a variety of soils formed from volcanic ash parent material in the Quaternary volcanic activity area. Distributed in areas with frequent modern volcanic activities around the world, the distribution area in China is very small. Some sections of volcanic ash soil with deeper development degree are obviously differentiated and have higher fertility. This soil is characterized by a coarse texture, high porosity, high risk of erosion and high mineral content of volcanic origin.
成土年龄较轻、发育程度低者,仍保留火山灰原来的特征,剖面分化微弱;发育程度较深者,已有明显的剖面分化,表层有机质含量可达15%以上,土色暗灰,肥力颇高。这种土壤孔隙度高,质地较粗,易受侵蚀,含有大量火山起源的矿物(如火山玻璃、火山碎屑等),其量超过70%;粘土矿物以水铅英石为主,对磷有固定作用。然而在火山灰土壤中有较高的磷吸持量, 并与pH (Na F)值有良好的相关性, 但pH (Na F) 值>9.4时, 磷酸盐吸持量>85%,这是由于火山灰土壤中类水铝英石和铝-腐植质络合物的高磷吸附的特性所致。Those with a younger soil-forming age and a low degree of development still retain the original characteristics of volcanic ash, and the section differentiation is weak; those with a deeper development degree have obvious section differentiation, and the organic matter content in the surface layer can reach more than 15%, and the soil color is dark gray. quite high. This kind of soil has high porosity, coarse texture, and is easy to be eroded. It contains a large amount of minerals of volcanic origin (such as volcanic glass, volcanic debris, etc.), the amount of which exceeds 70%; the clay minerals are mainly plumberite, and phosphorus Has a fixed effect. However, in the volcanic ash soil, there is a higher phosphorus sorption capacity and a good correlation with the pH (NaF) value, but when the pH (NaF) value is > 9.4, the phosphate sorption capacity is > 85%, which is Due to the high phosphorus adsorption properties of allophane-like and aluminum-humic complexes in volcanic soils.
随着新时代的到来,随着社会经济的日益进步和人们生活水平的不断提高,城市生活用水量剧增,污水处理厂所需要处理的生活污水量也在增长。由于污水量的增长导致污水处理厂的有机物含量降低,磷的含量在逐渐地增高,对城市生活污水除磷研究已经成为污水处理的瓶颈。从城市生活污水中磷的来源来看,其主要来自包含排泄物、食物残渣、农药、化肥等的生活污水。若是对其中的磷处理不当的话,必然会引起水体的富营养化。因此,在现阶段对于城市生活污水的处理过程中,则需要研究除磷技术,在提升除磷效率的同时,提升生活污水处理的效率与水平。With the advent of the new era, with the continuous improvement of social economy and people's living standards, urban domestic water consumption has increased sharply, and the amount of domestic sewage that sewage treatment plants need to process is also increasing. Due to the increase of sewage volume, the content of organic matter in sewage treatment plants has decreased, and the content of phosphorus has gradually increased. The research on phosphorus removal in urban domestic sewage has become the bottleneck of sewage treatment. From the perspective of the source of phosphorus in urban domestic sewage, it mainly comes from domestic sewage containing excreta, food residues, pesticides, and chemical fertilizers. If the phosphorus in it is not handled properly, it will inevitably cause eutrophication of the water body. Therefore, in the process of treating urban domestic sewage at this stage, it is necessary to study phosphorus removal technology to improve the efficiency and level of domestic sewage treatment while improving the efficiency of phosphorus removal.
城市生活污水除磷就是指将污水中的磷酸盐通过多种方式转化为固体颗粒,以此来从污水中将磷排除。从这些固体颗粒来看,其属于不可溶解的磷酸盐沉淀物,或者是活性污泥中的微生物固体,亦或是人工湿地植物组分。从城市生活污水除磷技术来看,现阶段污水除磷的技术种类很多,但是除磷效果好、应用范围较广的主要为生物法、化学沉淀法和吸附法。吸附法除磷的关键是吸附剂的选择,除磷吸附剂应具备生产成本低,吸附容量大,原料来源广等特点。目前常用的吸附剂主要为天然材料及废渣、活性氧化铝及其改性物和人工合成吸附剂等三大类。天然材料和活性氧化铝因其吸附容量小,成本高,容易产生二次污染等应用受到限制,现在人工合成除磷吸附剂越来受到重视。Phosphorus removal from urban domestic sewage refers to the conversion of phosphate in sewage into solid particles in various ways, so as to remove phosphorus from sewage. Judging from these solid particles, they belong to insoluble phosphate precipitates, or microbial solids in activated sludge, or plant components in constructed wetlands. From the perspective of urban domestic sewage phosphorus removal technology, there are many types of sewage phosphorus removal technologies at this stage, but the best phosphorus removal effect and wide application range are mainly biological methods, chemical precipitation methods and adsorption methods. The key to phosphorus removal by adsorption is the choice of adsorbent. The phosphorus removal adsorbent should have the characteristics of low production cost, large adsorption capacity, and wide source of raw materials. At present, the commonly used adsorbents are mainly natural materials and waste residues, activated alumina and its modified products, and artificially synthesized adsorbents. The application of natural materials and activated alumina is limited due to their small adsorption capacity, high cost, and easy to produce secondary pollution. Now artificially synthesized phosphorus removal adsorbents are getting more and more attention.
发明内容Contents of the invention
本发明的第一目的在于提供一种基于火山灰土富集水体中磷的吸附剂;第二目的在于提供所述吸附剂的制备方法;第三目的在于提供所述吸附剂的应用。The first purpose of the present invention is to provide an adsorbent for enriching phosphorus in water based on volcanic ash soil; the second purpose is to provide a preparation method of the adsorbent; the third purpose is to provide the application of the adsorbent.
本发明的第一目的是这样实现的,所述基于火山灰土富集水体中磷的吸附剂,包括以下原料:火山灰土、生物炭、石英粉和稀硝酸。The first object of the present invention is achieved in that the volcanic ash soil-based adsorbent for enriching phosphorus in water includes the following raw materials: volcanic ash soil, biochar, quartz powder and dilute nitric acid.
进一步的,所述原料的质量百分比为:Further, the mass percent of the raw material is:
火山灰土70%~90%;Volcanic ash soil 70%~90%;
石英粉10%~30%;Quartz powder 10%~30%;
生物炭5%~20%;Biochar 5%~20%;
每100g的火山灰土、生物炭、石英粉混合粉末中,加入稀硝酸40~50mL。Add 40~50mL of dilute nitric acid to every 100g of mixed powder of volcanic ash soil, biochar, and quartz powder.
进一步的,所述稀硝酸为质量百分比不大于 1%的稀硝酸,因为硝酸的不稳定性,越浓越容易分解。Further, the dilute nitric acid is dilute nitric acid with a mass percentage not greater than 1%. Because of the instability of nitric acid, the thicker it is, the easier it is to decompose.
本发明的第二目的是这样实现的,所述基于火山灰土富集水体中磷的吸附剂的制备方法,包括以下步骤:The second object of the present invention is achieved in that the preparation method of the sorbent based on pozzolanic soil enrichment of phosphorus in the water body comprises the following steps:
(1)按比例将火山灰土、生物炭、石英粉混合均匀得到混合粉末;(1) Mix volcanic ash soil, biochar, and quartz powder evenly in proportion to obtain mixed powder;
(2)向步骤(1)所得混合粉末中加入质量百分比不大于1%的稀硝酸,搅拌,形成泥状混合物;(2) Add dilute nitric acid with a mass percentage not greater than 1% to the mixed powder obtained in step (1), and stir to form a muddy mixture;
(3)将步骤(2)所得泥状混合物挤成块状,自然风干,之后经过600~800℃条件下加热2~3h,最终得到磷吸附剂。(3) Extrude the muddy mixture obtained in step (2) into blocks, air-dry naturally, and then heat at 600-800°C for 2-3 hours to finally obtain the phosphorus adsorbent.
进一步的,步骤(3)所述块状长度为30~50mm,宽度为20~30mm,高度为5~10mm。Further, the block length in step (3) is 30-50 mm, the width is 20-30 mm, and the height is 5-10 mm.
本发明的第三目的是这样实现的,所述吸附剂在生活污水中的磷去除或水体富营养化治理修复中的应用。The third object of the present invention is achieved by using the adsorbent in the removal of phosphorus in domestic sewage or in the treatment and repair of eutrophication in water bodies.
进一步的,所述的基于火山灰土富集水体中磷的吸附剂的应用方法为:Further, the application method of the described adsorbent based on volcanic ash soil enrichment of phosphorus in water is:
将制作好的吸附剂放进含磷污水中,将污水与吸附剂充分接触,使废水中的磷与其中的吸附剂反应6-10小时,火山灰土的吸附能力将会吸附富集污水中的磷,从而达到显著除磷的效果,进而可以保证污水的达标排放。吸附后的除磷吸附剂附着大量的磷和悬浮物形成含磷污泥,污泥中火山灰土吸附富集污水中的磷,进一步提升火山灰土中磷的含量,从而提高火山灰土肥力,使其更适合用于改良土壤,并且所添加量会大幅度降低,不会造成二次污染,实现环境-经济的良性循环。Put the prepared adsorbent into the phosphorus-containing sewage, fully contact the sewage with the adsorbent, and make the phosphorus in the wastewater react with the adsorbent for 6-10 hours. The adsorption capacity of the volcanic ash soil will absorb and enrich the phosphorus in the sewage. Phosphorus, so as to achieve a significant effect of phosphorus removal, which can ensure the discharge of sewage up to standard. After adsorption, the phosphorus-removing adsorbent attaches a large amount of phosphorus and suspended matter to form phosphorus-containing sludge. The volcanic ash soil in the sludge absorbs and enriches phosphorus in the sewage, and further increases the phosphorus content in the volcanic ash soil, thereby improving the fertility of the volcanic ash soil and making it It is more suitable for improving soil, and the amount added will be greatly reduced, without causing secondary pollution, and realizing a virtuous circle of environment and economy.
与现有技术相比,本发明具有以下技术效果:Compared with the prior art, the present invention has the following technical effects:
1、本发明方法所用的火山灰土通常多孔, 渗水性良好,表层腐殖质含量极高,腐殖化作用明显,土壤容重小,对磷有固定作用。火山灰土有较高的磷吸持量。相较于其他材料,极大地提高了磷的去除效率。1. The volcanic ash soil used in the method of the present invention is generally porous, has good water permeability, extremely high humus content in the surface layer, obvious humification effect, small soil bulk density, and has a fixing effect on phosphorus. Volcanic ash soil has a higher phosphorus uptake capacity. Compared with other materials, the phosphorus removal efficiency is greatly improved.
2、本发明方法所制备的吸附剂表面积大,接触面大,除磷效率高。2. The adsorbent prepared by the method of the present invention has large surface area, large contact surface and high phosphorus removal efficiency.
3、本发明方法所得到的富集污水中的磷后的污泥,其更适合用于改良土壤,并且所添加量会大幅度降低。3. The sludge enriched with phosphorus in sewage obtained by the method of the present invention is more suitable for improving soil, and the added amount will be greatly reduced.
4、本发明方法所得到的除磷吸附剂,在一定比例下,火山灰土添加量越多,除磷效果越好,除磷效率可达95%。4. The phosphorus removal adsorbent obtained by the method of the present invention, under a certain ratio, the more pozzolanic soil is added, the better the phosphorus removal effect, and the phosphorus removal efficiency can reach 95%.
5、本发明方法所得到的除磷吸附剂除磷效果好,操作简单方便。5. The phosphorus removal adsorbent obtained by the method of the present invention has good phosphorus removal effect and simple and convenient operation.
具体实施方式Detailed ways
下面对本发明作进一步的说明,但不以任何方式对本发明加以限制,基于本发明教导所作的任何变换或替换,均属于本发明的保护范围。The present invention will be further described below, but the present invention is not limited in any way. Any transformation or replacement based on the teaching of the present invention belongs to the protection scope of the present invention.
结合实施例1~4对本发明作进一步说明。The present invention will be further described in conjunction with embodiment 1~4.
实施例1Example 1
一种利用火山灰土吸收生活污水中磷的方法,包括以下步骤:A method for absorbing phosphorus in domestic sewage by using volcanic ash soil, comprising the following steps:
S1、除磷吸附剂的原料包括火山灰土、生物炭、石英粉和稀硝酸。S1. The raw materials of phosphorus removal adsorbent include volcanic ash soil, biochar, quartz powder and dilute nitric acid.
S2、按质量将其混合:S2, mix it by mass:
火山灰土70g;70g of volcanic ash soil;
石英粉20g;Quartz powder 20g;
生物炭10g;Biochar 10g;
将火山灰土、生物炭和石英粉混合粉末,加入质量百分比不大于1%的稀硝酸40mL。搅拌成泥状,挤压制成块状,自然风干后制成长度为30mm,宽度为20mm,高度为5mm。将所得块状颗粒平铺在坩埚底部,放入中频炉中在600℃加热2h,最终将其取出,得到除磷吸附剂。Mix pozzolanic soil, biochar and quartz powder into powder, and add 40mL of dilute nitric acid with a mass percentage not greater than 1%. Stir it into mud, extrude it into a block, and dry it naturally to make a length of 30mm, a width of 20mm, and a height of 5mm. Spread the obtained massive particles on the bottom of the crucible, put them into an intermediate frequency furnace and heat them at 600° C. for 2 hours, and finally take them out to obtain the phosphorus removal adsorbent.
将上述除磷吸附剂投放在污水处理厂的预反应池中,每处理1吨含磷污水需消耗2.6千克除磷吸附剂。使废水中的磷与其中的除磷吸附剂反应8小时,最终废水中磷的浓度可从处理前的5.0mg/L降至处理后的0.5mg/L,除磷率可高达90%,从而可以保证污水的达标排放。吸附后的除磷吸附剂附着大量的磷和悬浮物形成含磷污泥,污泥中火山灰土吸附富集污水中的磷,进一步提升火山灰土中磷的含量,从而提高火山灰土肥力,使其更适合用于改良土壤,并且所添加量会大幅度降低,不会造成二次污染,实现环境-经济的良性循环。持续投加该除磷吸附剂可保证稳定的除磷率。Putting the above-mentioned phosphorus-removing adsorbent in the pre-reaction tank of the sewage treatment plant will consume 2.6 kg of phosphorus-removing adsorbent for every ton of phosphorus-containing sewage. The phosphorus in the wastewater reacts with the phosphorus removal adsorbent in it for 8 hours, the concentration of phosphorus in the final wastewater can be reduced from 5.0mg/L before treatment to 0.5mg/L after treatment, and the phosphorus removal rate can be as high as 90%. It can ensure that the discharge of sewage reaches the standard. After adsorption, the phosphorus-removing adsorbent attaches a large amount of phosphorus and suspended matter to form phosphorus-containing sludge. The volcanic ash soil in the sludge absorbs and enriches phosphorus in the sewage, and further increases the phosphorus content in the volcanic ash soil, thereby improving the fertility of the volcanic ash soil and making it It is more suitable for improving soil, and the amount added will be greatly reduced, without causing secondary pollution, and realizing a virtuous circle of environment and economy. Continuous dosing of the phosphorus removal adsorbent can ensure a stable phosphorus removal rate.
实施例2Example 2
一种利用火山灰土吸收生活污水中磷的方法,包括以下步骤:A method for absorbing phosphorus in domestic sewage by using volcanic ash soil, comprising the following steps:
S1、除磷吸附剂的原料包括火山灰土、生物炭、石英粉和稀硝酸。S1. The raw materials of phosphorus removal adsorbent include volcanic ash soil, biochar, quartz powder and dilute nitric acid.
S2、按质量将其混合:S2, mix it by mass:
火山灰土75g;75g of volcanic ash soil;
石英粉15g;Quartz powder 15g;
生物炭10g;Biochar 10g;
将火山灰土、生物炭和石英粉混合粉末,加入质量百分比不大于1%的稀硝酸40mL。搅拌成泥状,挤压制成块状,自然风干后制成长度为40mm,宽度为30mm,高度为5mm。将所得块状颗粒平铺在坩埚底部,放入中频炉中在800℃加热2h,最终将其取出,得到除磷吸附剂。Mix pozzolanic soil, biochar and quartz powder into powder, and add 40mL of dilute nitric acid with a mass percentage not greater than 1%. Stir it into mud, extrude it into a block, and dry it naturally to make a length of 40mm, a width of 30mm, and a height of 5mm. Spread the obtained massive particles on the bottom of the crucible, put them into an intermediate frequency furnace and heat them at 800°C for 2 hours, and finally take them out to obtain the phosphorus removal adsorbent.
将上述除磷吸附剂投放在污水处理厂的预反应池中,每处理1吨含磷污水需消耗2.4千克除磷吸附剂。使废水中的磷与其中的除磷吸附剂反应8小时,最终废水中磷的浓度可从处理前的5.0mg/L降至处理后的0.42mg/L,除磷率可高达91.6%,从而可以保证污水的达标排放。吸附后的除磷吸附剂附着大量的磷和悬浮物形成含磷污泥,污泥中火山灰土吸附富集污水中的磷,进一步提升火山灰土中磷的含量,从而提高火山灰土肥力,使其更适合用于改良土壤,并且所添加量会大幅度降低,不会造成二次污染,实现环境-经济的良性循环。持续投加该除磷吸附剂可保证稳定的除磷率。Put the above-mentioned phosphorus removal adsorbent in the pre-reaction tank of the sewage treatment plant, and it will consume 2.4 kg of phosphorus removal adsorbent to treat 1 ton of phosphorus-containing sewage. By reacting the phosphorus in the wastewater with the phosphorus-removing adsorbent for 8 hours, the concentration of phosphorus in the final wastewater can be reduced from 5.0mg/L before treatment to 0.42mg/L after treatment, and the phosphorus removal rate can be as high as 91.6%. It can ensure that the discharge of sewage reaches the standard. After adsorption, the phosphorus-removing adsorbent attaches a large amount of phosphorus and suspended matter to form phosphorus-containing sludge. The volcanic ash soil in the sludge absorbs and enriches phosphorus in the sewage, and further increases the phosphorus content in the volcanic ash soil, thereby improving the fertility of the volcanic ash soil and making it It is more suitable for improving soil, and the amount added will be greatly reduced, without causing secondary pollution, and realizing a virtuous circle of environment and economy. Continuous dosing of the phosphorus removal adsorbent can ensure a stable phosphorus removal rate.
实施例3Example 3
一种利用火山灰土吸收生活污水中磷的方法,包括以下步骤:A method for absorbing phosphorus in domestic sewage by using volcanic ash soil, comprising the following steps:
S1、除磷吸附剂的原料包括火山灰土、生物炭、石英粉和稀硝酸。S1. The raw materials of phosphorus removal adsorbent include volcanic ash soil, biochar, quartz powder and dilute nitric acid.
S2、按质量将其混合:S2, mix it by mass:
火山灰土80g;Volcanic ash soil 80g;
石英粉10g;Quartz powder 10g;
生物炭10g;Biochar 10g;
将火山灰土、生物炭和石英粉混合粉末,加入质量百分比不大于1%的稀硝酸40mL。搅拌成泥状,挤压制成块状,自然风干后制成长度为50mm,宽度为30mm,高度为5mm。将所得块状颗粒平铺在坩埚底部,放入中频炉中在600~800℃加热2h,最终将其取出,得到除磷吸附剂。Mix pozzolanic soil, biochar and quartz powder into powder, and add 40mL of dilute nitric acid with a mass percentage not greater than 1%. Stir it into mud, extrude it into a block, and dry it naturally to make it into a length of 50mm, a width of 30mm, and a height of 5mm. Spread the obtained massive particles on the bottom of the crucible, put them into an intermediate frequency furnace and heat them at 600-800°C for 2 hours, and finally take them out to obtain the phosphorus removal adsorbent.
将上述除磷吸附剂投放在污水处理厂的预反应池中,每处理1吨含磷污水需消耗2.2千克除磷吸附剂。使废水中的磷与其中的除磷吸附剂反应8小时,最终废水中磷的浓度可从处理前的5.0mg/L降至处理后的0.38mg/L,除磷率可高达92.4%,从而可以保证污水的达标排放。吸附后的除磷吸附剂附着大量的磷和悬浮物形成含磷污泥,污泥中火山灰土吸附富集污水中的磷,进一步提升火山灰土中磷的含量,从而提高火山灰土肥力,使其更适合用于改良土壤,并且所添加量会大幅度降低,不会造成二次污染,实现环境-经济的良性循环。持续投加该除磷吸附剂可保证稳定的除磷率。Put the above-mentioned phosphorus removal adsorbent in the pre-reaction tank of the sewage treatment plant, and it will consume 2.2 kg of phosphorus removal adsorbent to treat 1 ton of phosphorus-containing sewage. By reacting the phosphorus in the wastewater with the phosphorus-removing adsorbent for 8 hours, the concentration of phosphorus in the final wastewater can be reduced from 5.0mg/L before treatment to 0.38mg/L after treatment, and the phosphorus removal rate can be as high as 92.4%. It can ensure that the discharge of sewage reaches the standard. After adsorption, the phosphorus-removing adsorbent attaches a large amount of phosphorus and suspended matter to form phosphorus-containing sludge. The volcanic ash soil in the sludge absorbs and enriches phosphorus in the sewage, and further increases the phosphorus content in the volcanic ash soil, thereby improving the fertility of the volcanic ash soil and making it It is more suitable for improving soil, and the amount added will be greatly reduced, without causing secondary pollution, and realizing a virtuous circle of environment and economy. Continuous dosing of the phosphorus removal adsorbent can ensure a stable phosphorus removal rate.
实施例4Example 4
一种利用火山灰土吸收生活污水中磷的方法,包括以下步骤:A method for absorbing phosphorus in domestic sewage by using volcanic ash soil, comprising the following steps:
S1、除磷吸附剂的原料包括火山灰土、生物炭、石英粉和稀硝酸。S1. The raw materials of phosphorus removal adsorbent include volcanic ash soil, biochar, quartz powder and dilute nitric acid.
S2、按质量将其混合:S2, mix it by mass:
火山灰土85g;Volcanic ash soil 85g;
石英粉10g;Quartz powder 10g;
生物炭5g;Biochar 5g;
将火山灰土、生物炭和石英粉混合粉末,加入质量百分比不大于1%的稀硝酸40mL。搅拌成泥状,挤压制成块状,自然风干后制成长度为50mm,宽度为40mm,高度为5mm。将所得块状颗粒平铺在坩埚底部,放入中频炉中在600~800℃加热2h,最终将其取出,得到除磷吸附剂。Mix pozzolanic soil, biochar and quartz powder into powder, and add 40mL of dilute nitric acid with a mass percentage not greater than 1%. Stir it into mud, extrude it into a block, and dry it naturally to make it with a length of 50mm, a width of 40mm, and a height of 5mm. Spread the obtained massive particles on the bottom of the crucible, put them into an intermediate frequency furnace and heat them at 600-800°C for 2 hours, and finally take them out to obtain the phosphorus removal adsorbent.
将上述除磷吸附剂投放在污水处理厂的预反应池中,每处理1吨含磷污水需消耗2.0千克除磷吸附剂。使废水中的磷与其中的除磷吸附剂反应8小时,最终废水中磷的浓度可从处理前的5.0mg/L降至处理后的0.28mg/L,除磷率可高达94.4%,从而可以保证污水的达标排放。吸附后的除磷吸附剂附着大量的磷和悬浮物形成含磷污泥,污泥中火山灰土吸附富集污水中的磷,进一步提升火山灰土中磷的含量,从而提高火山灰土肥力,使其更适合用于改良土壤,并且所添加量会大幅度降低,不会造成二次污染,实现环境-经济的良性循环。持续投加该除磷吸附剂可保证稳定的除磷率。Put the above-mentioned phosphorus removal adsorbent in the pre-reaction tank of the sewage treatment plant, and it will consume 2.0 kg of phosphorus removal adsorbent to treat 1 ton of phosphorus-containing sewage. The phosphorus in the wastewater reacts with the phosphorus removal adsorbent in it for 8 hours, and the concentration of phosphorus in the final wastewater can be reduced from 5.0mg/L before treatment to 0.28mg/L after treatment, and the phosphorus removal rate can be as high as 94.4%. It can ensure that the discharge of sewage reaches the standard. After adsorption, the phosphorus-removing adsorbent attaches a large amount of phosphorus and suspended matter to form phosphorus-containing sludge. The volcanic ash soil in the sludge absorbs and enriches phosphorus in the sewage, and further increases the phosphorus content in the volcanic ash soil, thereby improving the fertility of the volcanic ash soil and making it It is more suitable for improving soil, and the amount added will be greatly reduced, without causing secondary pollution, and realizing a virtuous circle of environment and economy. Continuous dosing of the phosphorus removal adsorbent can ensure a stable phosphorus removal rate.
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