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CN104710079B - A kind of applying modified modenite is processed the method for municipal middle water - Google Patents

A kind of applying modified modenite is processed the method for municipal middle water Download PDF

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CN104710079B
CN104710079B CN201510114472.4A CN201510114472A CN104710079B CN 104710079 B CN104710079 B CN 104710079B CN 201510114472 A CN201510114472 A CN 201510114472A CN 104710079 B CN104710079 B CN 104710079B
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CN104710079A (en
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王雪纯
刘冬峰
张丽萍
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Guangdong Namide Environmental Protection Technology Co ltd
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Abstract

本发明公开了一种应用改性丝光沸石处理城市中水的方法,所述中水的COD值在65-95mg/L之间,其特征在于,所述的方法包括顺次进行的粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性丝光沸石吸附处理;本发明中,粉煤灰吸附剂能够吸附水中的大颗粒有机物质,生物除臭剂能够消除中水中的异味,生物净化剂能够消耗中水中的残余有机物,改性沸石能够高效地去除污水中钙镁离子、氟离子以及其他重金属离子。The invention discloses a method for treating urban reclaimed water by using modified mordenite. The COD value of the reclaimed water is between 65-95 mg/L, and the method is characterized in that the method includes sequentially carrying out fly ash Adsorbent treatment, biological deodorant treatment, biological deodorant treatment, modified mordenite adsorption treatment; in the present invention, the fly ash adsorbent can adsorb large particle organic matter in water, and the biological deodorant can eliminate peculiar smell in reclaimed water , Biological purifiers can consume residual organic matter in reclaimed water, and modified zeolite can efficiently remove calcium and magnesium ions, fluoride ions and other heavy metal ions in sewage.

Description

一种应用改性丝光沸石处理城市中水的方法A method for treating urban reclaimed water using modified mordenite

技术领域technical field

本发明为2014年2月20日提交的发明专利申请《一种城市中水的深度处理方法》(申请号:201410057403X)的分案申请。属于城市污水处理环保领域,尤其涉及一种应用改性丝光沸石处理城市中水的方法。The present invention is a divisional application of the invention patent application "A Method for Advanced Treatment of Urban Reclaimed Water" (Application No.: 201410057403X) submitted on February 20, 2014. The invention belongs to the field of urban sewage treatment and environmental protection, and in particular relates to a method for treating urban reclaimed water with modified mordenite.

背景技术Background technique

中水,也称再生水,是指污水经适当处理后,达到一定的水质指标,满足某种使用要求,可以进行有益使用的水,大量的中水用作景观用水。城市中水(以下简称中水)作为城市的第二种水源,具有水量大、水质稳定、来源可靠和不需要长距离引水等特点,是今后可持续发展的一种再生水资源。中水回用能够有效解决水资源不足、提高水资源重复利用率和减少污水排放,具有巨大的社会效益和良好的经济效益。中水中的污染物浓度虽然达到国家排放标准,水质也优于工业污水,但有一些指标仍然较差,不能满足工业生产对水质的要求,如COD、悬浮物和微生物等。因此,城市中水必须进行适当处理后才能回用。Reclaimed water, also known as reclaimed water, refers to water that can be used beneficially after proper treatment to meet certain water quality indicators and meet certain use requirements. A large amount of reclaimed water is used for landscape water. As the second water source for cities, urban reclaimed water (hereinafter referred to as reclaimed water) has the characteristics of large water volume, stable water quality, reliable source and no need for long-distance water diversion. It is a renewable water resource for sustainable development in the future. Reuse of reclaimed water can effectively solve the shortage of water resources, improve the reuse rate of water resources and reduce sewage discharge, which has huge social benefits and good economic benefits. Although the concentration of pollutants in reclaimed water meets the national discharge standards and the water quality is better than industrial sewage, some indicators are still poor and cannot meet the water quality requirements of industrial production, such as COD, suspended solids and microorganisms. Therefore, urban water must be properly treated before it can be reused.

城市中水如果处理不好,会造成水体富营养化、水生态环境不断恶化,在感官上表现为水中藻类呈几何级数增长、水中透明度和溶解氧下降、水质恶化、呈现不同颜色,危害水中动植物及人类健康,使水生态和水功能受到阻碍和破坏,水味变腥臭,水透明度下降,水体浑浊,使景观水体丧失观赏、娱乐等美学价值。因此,提高城市中水的深度处理力度,使之用于景观用水时能够保证对人体、动物体、水体没有损害,是本领域中一大技术研究热点。If urban reclaimed water is not treated properly, it will cause eutrophication of the water body and the deterioration of the water ecological environment. From the sensory perspective, the algae in the water will grow geometrically, the transparency and dissolved oxygen in the water will decrease, the water quality will deteriorate, and different colors will appear, which will endanger the quality of life in the water. The health of animals, plants and human beings will hinder and destroy the water ecology and water functions, the taste of water will become foul, the transparency of water will decrease, and the water body will be turbid, so that the landscape water body will lose its aesthetic value such as viewing and entertainment. Therefore, it is a major technical research hotspot in this field to improve the advanced treatment of urban reclaimed water so that it can ensure no damage to human body, animal body and water body when it is used for landscape water.

发明内容Contents of the invention

为了克服现有技术中的不足,本发明的目的是提供一种应用改性丝光沸石处理城市中水的方法,对城市中水进行深度处理,污染物去除效率高,出水水质稳定,污染物基本被去除,能够满足景观用水放入要求。In order to overcome the deficiencies in the prior art, the object of the present invention is to provide a method for treating urban reclaimed water using modified mordenite, which can carry out advanced treatment of urban reclaimed water, with high pollutant removal efficiency, stable effluent quality, and basically no pollutants. be removed to meet the requirements for landscape water input.

本发明的技术方案如下。The technical scheme of the present invention is as follows.

一种应用改性丝光沸石处理城市中水的方法,所述中水的COD值在65-95mg/L之间,所述的方法包括顺次进行的粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性丝光沸石吸附处理;具体为:A method of applying modified mordenite to treat urban reclaimed water, the COD value of said reclaimed water is between 65-95mg/L, said method comprising sequentially carrying out fly ash adsorbent treatment, biological deodorant Treatment, biological purification agent treatment, modified mordenite adsorption treatment; specifically:

(1)粉煤灰吸附剂处理:将中水引入粉煤灰处理池中,向池中投入粉煤灰吸附剂对中水进行前处理,粉煤灰吸附剂投加重量和中水重量比例在0.8-2.8:100之间,处理时间为3-36h;所述的粉煤灰吸附剂由如下方法制备:(A)、按照重量份数:生石灰10-15份,蒙脱土5-9份,蛭石1-5份,粘土2-20份,甲基纤维素2-6份,溴化钠1-2份,氧化铝5-10份,粉煤灰100-240份,将各原料混合均匀,加水制成直径为35-45mm球形颗粒,再在隧道窑于950-980℃下烧结2-3h,冷却后得到粉煤灰吸附剂前体;(B)、配制摩尔浓度为1-1.5mol/L的溴化钠水溶液,将步骤(A)得到的粉煤灰吸附剂前体倒入所述溴化钠水溶液中进行浸渍处理16-24h,(C)、将经过步骤(B)浸渍处理的粉煤灰吸附剂前体放入真空烘箱中干燥处理10-20h后,得到粉煤灰吸附剂;(1) Fly ash adsorbent treatment: introduce reclaimed water into the fly ash treatment pool, put fly ash adsorbent into the pool to pre-treat the reclaimed water, the ratio of the weight of fly ash adsorbent to the weight of reclaimed water Between 0.8-2.8:100, the treatment time is 3-36h; the described fly ash adsorbent is prepared by the following method: (A), in parts by weight: 10-15 parts of quicklime, 5-9 parts of montmorillonite 1-5 parts of vermiculite, 2-20 parts of clay, 2-6 parts of methyl cellulose, 1-2 parts of sodium bromide, 5-10 parts of alumina, 100-240 parts of fly ash, each raw material Mix evenly, add water to make spherical particles with a diameter of 35-45mm, then sinter in a tunnel kiln at 950-980°C for 2-3h, and obtain a fly ash adsorbent precursor after cooling; (B), prepare a molar concentration of 1- 1.5mol/L sodium bromide aqueous solution, the fly ash adsorbent precursor that step (A) obtains is poured into described sodium bromide aqueous solution and carries out immersion treatment 16-24h, (C), will pass through step (B) The impregnated fly ash adsorbent precursor is put into a vacuum oven for drying treatment for 10-20 hours to obtain the fly ash adsorbent;

(2)生物除臭剂处理:将粉煤灰吸附剂处理的中水引入生物除臭池中,向池中投加生物除臭剂,生物除臭剂投加重量和中水重量比例在0.1-0.8:100之间,处理时间为3-5天;所述的生物除臭剂的微生物菌种组成为:嗜酸乳杆菌106-109个/mL、短小芽孢杆菌106-109个/mL、枯草芽孢杆菌106-109个/mL、荧光假单胞菌105-107个/mL、沼泽红假单胞菌105-107个/mL、班图酒香酵母菌104-106个/mL、平常假丝酵母菌104-106个/mL、扩张青霉104-106个/mL、米根霉104-106个/mL、绿色木霉104-106个/mL、细黄链霉菌104-106个/mL和灰色链霉菌104-106个/mL;(2) Biological deodorant treatment: introduce the reclaimed water treated with fly ash adsorbent into the biological deodorization tank, add biological deodorizer to the pool, and the ratio of the weight of biological deodorant to the weight of reclaimed water is 0.1 Between -0.8:100, the treatment time is 3-5 days; the microbial strain composition of the biological deodorant is: Lactobacillus acidophilus 10 6 -10 9 /mL, Bacillus pumilus 10 6 -10 9 1/mL, Bacillus subtilis 10 6 -10 9 /mL, Pseudomonas fluorescens 10 5 -10 7 /mL, Rhodopseudomonas palustris 10 5 -10 7 /mL, Bantu Brettanomyces Bacteria 10 4 -10 6 /mL, Candida vulgaris 10 4 -10 6 /mL, Penicillium expansica 10 4 -10 6 /mL, Rhizopus oryzae 10 4 -10 6 /mL, green wood Mycobacterium 10 4 -10 6 /mL, Streptomyces luteus 10 4 -10 6 /mL and Streptomyces griseus 10 4 -10 6 /mL;

(3)生物净化剂处理:将生物除臭剂处理的中水引入生物净化池中,向池中投加生物净化剂,生物净化剂投加重量和中水重量比例在0.8-6.8:100之间,处理时间为5-9天,调整曝气条件使得中水中的溶解氧的量为3-4mg/L;所述的生物净化剂中的菌种包括血色红假单胞菌,泾阳链霉菌,以及乳酸链球菌,所述的菌种的培养基由下列质量比的组分组成:红糖5-6%,酵母粉1-2%,余量为水;(3) Biological purification agent treatment: introduce the reclaimed water treated with biological deodorizer into the biological purification tank, add biological deodorizer to the pool, and the ratio of the weight of biological deodorizer to the weight of reclaimed water is between 0.8-6.8:100 Between, the treatment time is 5-9 days, adjust the aeration condition so that the amount of dissolved oxygen in the middle water is 3-4mg/L; The strains in the biological purifier include Rhodopseudomonas haemophilus, Streptomyces jingyangii , and Streptococcus lactis, the culture medium of the described bacteria is composed of the following components in mass ratio: brown sugar 5-6%, yeast powder 1-2%, and the balance is water;

(4)改性丝光沸石吸附处理:将生物净化剂处理的中水经过过滤后使用提升泵输送至位于吸附塔底部的吸附塔进水口,吸附塔从下往上依次填充有无纺布层、石英砂层和改性沸石层,其中,无纺布层的厚度在2-20mm之间,石英砂层和改性沸石层的厚度比值为1:0.5-0.8;所述改性丝光沸石的改性步骤是:将丝光沸石、高岭土、硅镁胶、田菁粉和磷酸按照重量比例60:30:30:20:20混合均匀,然后加水制备成固含量为50-55%的浆液;浆液喷雾干燥成粉状颗粒,然后将粉状颗粒在马弗炉中于500-700℃焙烧3-5h,然后冷却至室温,得改性沸石;水从位于吸附塔顶部的吸附塔出水口流出,经泵输送至储水槽,为深度处理产品水。(4) Adsorption treatment of modified mordenite: the reclaimed water treated with biological purifiers is filtered and transported to the water inlet of the adsorption tower at the bottom of the adsorption tower by a lift pump. The adsorption tower is filled with non-woven fabric layers, Quartz sand layer and modified zeolite layer, wherein, the thickness of the non-woven fabric layer is between 2-20mm, and the thickness ratio of the quartz sand layer and the modified zeolite layer is 1:0.5-0.8; the modification of the modified mordenite The specific steps are: mix mordenite, kaolin, silica-magnesia gel, scallop powder and phosphoric acid uniformly according to the weight ratio of 60:30:30:20:20, and then add water to prepare a slurry with a solid content of 50-55%; the slurry is sprayed Dry it into powdery particles, then roast the powdery particles in a muffle furnace at 500-700°C for 3-5 hours, then cool to room temperature to obtain modified zeolite; water flows out from the outlet of the adsorption tower at the top of the adsorption tower, and passes through The pump delivers to the water storage tank for advanced treatment of product water.

优选的,所述的改性步骤中磷酸的摩尔浓度为0.9-1.3mol/L,优选为1.0mol/L。Preferably, the molar concentration of phosphoric acid in the modification step is 0.9-1.3 mol/L, preferably 1.0 mol/L.

所述的丝光沸石为市售的丝光沸石,或者是本领域技术人员可以得到的丝光沸石,本发明发现,丝光沸石由于其特定的结构,在吸附污水中金属离子方面具有良好的作用,经过改性丝光沸石的吸附处理后,水中污染物进一步降低。Described mordenite is commercially available mordenite, or the mordenite that can be obtained by those skilled in the art. The present invention finds that mordenite has a good effect in adsorbing metal ions in sewage due to its specific structure. After the adsorption treatment of active mordenite, the pollutants in the water are further reduced.

本发明中,通过对城市中水进行深度处理,以及经过粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性丝光沸石吸附处理,出水水质稳定,达到景观用水的要求,粉煤灰吸附剂能够吸附水中的大颗粒有机物质,生物除臭剂能够消除中水中的异味,生物净化剂能够消耗中水中的残余有机物,改性沸石能够高效地去除污水中钙镁离子、氟离子以及其他重金属离子。In the present invention, through advanced treatment of urban reclaimed water, as well as fly ash adsorbent treatment, biological deodorant treatment, biological purification agent treatment, and modified mordenite adsorption treatment, the effluent water quality is stable and meets the requirements of landscape water. Fly ash adsorbent can absorb large particles of organic matter in water, biological deodorant can eliminate odor in reclaimed water, biological purifier can consume residual organic matter in reclaimed water, and modified zeolite can efficiently remove calcium and magnesium ions and fluorine in sewage ions and other heavy metal ions.

具体实施方式detailed description

下面结合具体实施例对本发明进行进一步详细说明。The present invention will be further described in detail below in conjunction with specific embodiments.

实施例1Example 1

一种处理城市中水的方法,所述中水的COD值为95mg/L,所述的方法包括顺次进行的粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性沸石吸附处理;具体为:A method for treating urban reclaimed water, the COD value of said reclaimed water is 95mg/L, said method comprising sequentially carried out fly ash adsorbent treatment, biological deodorant treatment, biological purifier treatment, modified Zeolite adsorption treatment; specifically:

(1)粉煤灰吸附剂处理:将中水引入粉煤灰处理池中,向池中投入粉煤灰吸附剂对中水进行前处理,粉煤灰吸附剂投加重量和中水重量比例在2.8:100之间,处理时间为36h;所述的粉煤灰吸附剂由如下方法制备:(A)、按照重量份数:生石灰15份,蒙脱土9份,蛭石5份,粘土20份,甲基纤维素6份,溴化钠2份,氧化铝10份,粉煤灰240份,将各原料混合均匀,加水制成直径为45mm球形颗粒,再在隧道窑于980℃下烧结3h,冷却后得到粉煤灰吸附剂前体;(B)、配制摩尔浓度为1.5mol/L的溴化钠水溶液,将步骤(A)得到的粉煤灰吸附剂前体倒入所述溴化钠水溶液中进行浸渍处理24h,(C)、将经过步骤(B)浸渍处理的粉煤灰吸附剂前体放入真空烘箱中干燥处理20h后,得到粉煤灰吸附剂;(1) Fly ash adsorbent treatment: introduce reclaimed water into the fly ash treatment pool, put fly ash adsorbent into the pool to pre-treat the reclaimed water, the ratio of the weight of fly ash adsorbent to the weight of reclaimed water Between 2.8:100, the treatment time is 36h; the described fly ash adsorbent is prepared by the following method: (A), according to parts by weight: 15 parts of quicklime, 9 parts of montmorillonite, 5 parts of vermiculite, clay 20 parts, 6 parts of methyl cellulose, 2 parts of sodium bromide, 10 parts of alumina, 240 parts of fly ash, mix all raw materials evenly, add water to make spherical particles with a diameter of 45 mm, and then put them in a tunnel kiln at 980 ° C Sintering 3h, obtains the fly ash adsorbent precursor after cooling; (B), preparation molar concentration is the sodium bromide aqueous solution of 1.5mol/L, the fly ash adsorbent precursor that step (A) obtains is poured into said Sodium bromide aqueous solution is impregnated for 24 hours, (C), after the fly ash adsorbent precursor that has been impregnated in step (B) is placed in a vacuum oven for 20 hours, the fly ash adsorbent is obtained;

(2)生物除臭剂处理:将粉煤灰吸附剂处理的中水引入生物除臭池中,向池中投加生物除臭剂,生物除臭剂投加重量和中水重量比例在0.8:100之间,处理时间为5天;所述的生物除臭剂的微生物菌种组成为:嗜酸乳杆菌106-109个/mL、短小芽孢杆菌106-109个/mL、枯草芽孢杆菌106-109个/mL、荧光假单胞菌105-107个/mL、沼泽红假单胞菌105-107个/mL、班图酒香酵母菌104-106个/mL、平常假丝酵母菌104-106个/mL、扩张青霉104-106个/mL、米根霉104-106个/mL、绿色木霉104-106个/mL、细黄链霉菌104-106个/mL和灰色链霉菌104-106个/mL;(2) Biological deodorant treatment: introduce the reclaimed water treated with fly ash adsorbent into the biological deodorization tank, add biological deodorizer to the pool, and the ratio of the weight of biological deodorizer to the weight of reclaimed water is 0.8 : Between 100, the treatment time is 5 days; the microbial strains of the biological deodorant consist of: Lactobacillus acidophilus 10 6 -10 9 /mL, Bacillus pumilus 10 6 -10 9 /mL, Bacillus subtilis 10 6 -10 9 /mL, Pseudomonas fluorescens 10 5 -10 7 /mL, Rhodopseudomonas palustris 10 5 -10 7 /mL, Bantu Brettanomyces 10 4 - 10 6 /mL, Candida vulgaris 10 4 -10 6 /mL, Penicillium expansica 10 4 -10 6 /mL, Rhizopus oryzae 10 4 -10 6 /mL, Trichoderma viride 10 4 - 10 6 /mL, 10 4 -10 6 /mL for Streptomyces flavinus and 10 4 -10 6 /mL for Streptomyces griseus;

(3)生物净化剂处理:将生物除臭剂处理的中水引入生物净化池中,向池中投加生物净化剂,生物净化剂投加重量和中水重量比例在6.8:100之间,处理时间为9天,调整曝气条件使得中水中的溶解氧的量为4mg/L;所述的生物净化剂中的菌种包括血色红假单胞菌,泾阳链霉菌,以及乳酸链球菌,所述的菌种的培养基由下列质量比的组分组成:红糖5-6%,酵母粉1-2%,余量为水;(3) Biological purification agent treatment: introduce the reclaimed water treated by the biological deodorant into the biological purification tank, add the biological deodorizer to the pool, and the ratio of the weight of the biological deodorizer to the weight of the reclaimed water is between 6.8:100, The treatment time was 9 days, and the aeration conditions were adjusted so that the amount of dissolved oxygen in the middle water was 4 mg/L; the bacterial species in the biological purifier included Rhodopseudomonas sanguinus, Streptomyces Jingyang, and Streptococcus lactis, The culture medium of the strain is composed of the following components in mass ratio: brown sugar 5-6%, yeast powder 1-2%, and the balance is water;

(4)改性沸石吸附处理:将生物净化剂处理的中水经过过滤后使用提升泵输送至位于吸附塔底部的吸附塔进水口,吸附塔从下往上依次填充有无纺布层、石英砂层和改性沸石层,其中,无纺布层的厚度为20mm,石英砂层和改性沸石层的厚度比值为1:0.8,水从位于吸附塔顶部的吸附塔出水口流出,经泵输送至储水槽,为深度处理产品水。(4) Modified zeolite adsorption treatment: After the reclaimed water treated by the biological purifier is filtered, the lifting pump is used to transport it to the water inlet of the adsorption tower at the bottom of the adsorption tower. The adsorption tower is filled with non-woven fabric layer, quartz Sand layer and modified zeolite layer, wherein, the thickness of the non-woven fabric layer is 20mm, the thickness ratio of the quartz sand layer and the modified zeolite layer is 1:0.8, and the water flows out from the outlet of the adsorption tower at the top of the adsorption tower, through the pump It is sent to the water storage tank for advanced treatment of product water.

本实施例中的改性沸石为氯化钠改性沸石,其制备方法为在内径为14mm的有机玻璃柱中装入粒径为0.5~1.0mm的沸石,改性剂NaCl溶液以0.5m/h的流速通过沸石层至离子交换完全为止。The modified zeolite in this example is a sodium chloride modified zeolite, and its preparation method is to load a zeolite with a particle size of 0.5 to 1.0 mm in a plexiglass column with an inner diameter of 14 mm, and the modifier NaCl solution at 0.5 m/ The flow rate of h passes through the zeolite layer until the ion exchange is complete.

实施例2Example 2

一种应用改性丝光沸石处理城市中水的方法,所述中水的COD值为65mg/L,所述的方法包括顺次进行的粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性丝光沸石吸附处理;具体为:A method of applying modified mordenite to treat urban reclaimed water, the COD value of said reclaimed water is 65mg/L, said method comprising sequentially carrying out fly ash adsorbent treatment, biological deodorant treatment, biological purification Agent treatment, modified mordenite adsorption treatment; specifically:

(1)粉煤灰吸附剂处理:将中水引入粉煤灰处理池中,向池中投入粉煤灰吸附剂对中水进行前处理,粉煤灰吸附剂投加重量和中水重量比例在0.8:100之间,处理时间为3h;所述的粉煤灰吸附剂由如下方法制备:(A)、按照重量份数:生石灰10份,蒙脱土5份,蛭石1份,粘土2份,甲基纤维素2份,溴化钠1份,氧化铝5份,粉煤灰100份,将各原料混合均匀,加水制成直径为35mm球形颗粒,再在隧道窑于950℃下烧结2h,冷却后得到粉煤灰吸附剂前体;(B)、配制摩尔浓度为1mol/L的溴化钠水溶液,将步骤(A)得到的粉煤灰吸附剂前体倒入所述溴化钠水溶液中进行浸渍处理16h,(C)、将经过步骤(B)浸渍处理的粉煤灰吸附剂前体放入真空烘箱中干燥处理10h后,得到粉煤灰吸附剂;(1) Fly ash adsorbent treatment: introduce reclaimed water into the fly ash treatment pool, put fly ash adsorbent into the pool to pre-treat the reclaimed water, the ratio of the weight of fly ash adsorbent to the weight of reclaimed water Between 0.8:100, the treatment time is 3h; the described fly ash adsorbent is prepared by the following method: (A), in parts by weight: 10 parts of quicklime, 5 parts of montmorillonite, 1 part of vermiculite, clay 2 parts, 2 parts of methyl cellulose, 1 part of sodium bromide, 5 parts of alumina, 100 parts of fly ash, mix all raw materials evenly, add water to make spherical particles with a diameter of 35 mm, and then put them in a tunnel kiln at 950 ° C Sinter 2h, obtain the fly ash sorbent precursor after cooling; (B), preparation molar concentration is the sodium bromide aqueous solution of 1mol/L, the fly ash sorbent precursor that step (A) obtains is poured into the bromine Sodium chloride aqueous solution is impregnated for 16 hours, (C), the fly ash adsorbent precursor that has been impregnated in step (B) is put into a vacuum oven for drying for 10 hours, and the fly ash adsorbent is obtained;

(2)生物除臭剂处理:将粉煤灰吸附剂处理的中水引入生物除臭池中,向池中投加生物除臭剂,生物除臭剂投加重量和中水重量比例在0.1:100之间,处理时间为3天;所述的生物除臭剂的微生物菌种组成为:嗜酸乳杆菌106-109个/mL、短小芽孢杆菌106-109个/mL、枯草芽孢杆菌106-109个/mL、荧光假单胞菌105-107个/mL、沼泽红假单胞菌105-107个/mL、班图酒香酵母菌104-106个/mL、平常假丝酵母菌104-106个/mL、扩张青霉104-106个/mL、米根霉104-106个/mL、绿色木霉104-106个/mL、细黄链霉菌104-106个/mL和灰色链霉菌104-106个/mL;(2) Biological deodorant treatment: introduce the reclaimed water treated with fly ash adsorbent into the biological deodorization tank, add biological deodorizer to the pool, and the ratio of the weight of biological deodorant to the weight of reclaimed water is 0.1 : between 100, the treatment time is 3 days; the microbial strains of the biological deodorant consist of: Lactobacillus acidophilus 10 6 -10 9 /mL, Bacillus pumilus 10 6 -10 9 /mL, Bacillus subtilis 10 6 -10 9 /mL, Pseudomonas fluorescens 10 5 -10 7 /mL, Rhodopseudomonas palustris 10 5 -10 7 /mL, Bantu Brettanomyces 10 4 - 10 6 /mL, Candida vulgaris 10 4 -10 6 /mL, Penicillium expansica 10 4 -10 6 /mL, Rhizopus oryzae 10 4 -10 6 /mL, Trichoderma viride 10 4 - 10 6 /mL, 10 4 -10 6 /mL for Streptomyces flavinus and 10 4 -10 6 /mL for Streptomyces griseus;

(3)生物净化剂处理:将生物除臭剂处理的中水引入生物净化池中,向池中投加生物净化剂,生物净化剂投加重量和中水重量比例在0.8:100之间,处理时间为5天,调整曝气条件使得中水中的溶解氧的量为3mg/L;所述的生物净化剂中的菌种包括血色红假单胞菌,泾阳链霉菌,以及乳酸链球菌,所述的菌种的培养基由下列质量比的组分组成:红糖5-6%,酵母粉1-2%,余量为水;(3) Biological purification agent treatment: introduce the reclaimed water treated with biological deodorant into the biological purification tank, add biological deodorizer to the pool, the ratio of the weight of biological deodorizer to the weight of reclaimed water is between 0.8:100, The treatment time was 5 days, and the aeration conditions were adjusted so that the amount of dissolved oxygen in the middle water was 3 mg/L; the bacterial species in the biological purifier included Rhodopseudomonas sanguinus, Streptomyces Jingyang, and Streptococcus lactis, The culture medium of the strain is composed of the following components in mass ratio: brown sugar 5-6%, yeast powder 1-2%, and the balance is water;

(4)改性丝光沸石吸附处理:将生物净化剂处理的中水经过过滤后使用提升泵输送至位于吸附塔底部的吸附塔进水口,吸附塔从下往上依次填充有无纺布层、石英砂层和改性沸石层,其中,无纺布层的厚度为2mm,石英砂层和改性沸石层的厚度比值为1:0.5,水从位于吸附塔顶部的吸附塔出水口流出,经泵输送至储水槽,为深度处理产品水;所述的改性沸石为改性丝光沸石,改性步骤是:将丝光沸石、高岭土、硅镁胶、田菁粉和磷酸按照重量比例60:30:30:20:20混合均匀,然后加水制备成固含量为50-55%的浆液;浆液喷雾干燥成粉状颗粒,然后将粉状颗粒在马弗炉中于500-700℃焙烧3-5h,然后冷却至室温,得改性沸石,其中磷酸的摩尔浓度为1.3mol/L。(4) Adsorption treatment of modified mordenite: the reclaimed water treated with biological purifiers is filtered and transported to the water inlet of the adsorption tower at the bottom of the adsorption tower by a lift pump. The adsorption tower is filled with non-woven fabric layers, Quartz sand layer and modified zeolite layer, wherein, the thickness of the non-woven fabric layer is 2mm, the thickness ratio of the quartz sand layer and the modified zeolite layer is 1:0.5, and the water flows out from the outlet of the adsorption tower at the top of the adsorption tower. The pump is transported to the water storage tank for advanced treatment of product water; the modified zeolite is modified mordenite, and the modification step is: mix mordenite, kaolin, silica-magnesium gel, scallop powder and phosphoric acid in a weight ratio of 60:30 :30:20:20 Mix evenly, then add water to prepare a slurry with a solid content of 50-55%; the slurry is spray-dried into powder particles, and then the powder particles are roasted in a muffle furnace at 500-700°C for 3-5h , and then cooled to room temperature to obtain a modified zeolite, wherein the molar concentration of phosphoric acid is 1.3mol/L.

实施例3Example 3

一种应用改性丝光沸石处理城市中水的方法,所述中水的COD值为70mg/L,所述的方法包括顺次进行的粉煤灰吸附剂处理、生物除臭剂处理、生物净化剂处理、改性丝光沸石吸附处理;具体为:A method of applying modified mordenite to treat urban reclaimed water, the COD value of the reclaimed water is 70mg/L, and the method comprises sequentially carrying out fly ash adsorbent treatment, biological deodorant treatment, biological purification Agent treatment, modified mordenite adsorption treatment; specifically:

(1)粉煤灰吸附剂处理:将中水引入粉煤灰处理池中,向池中投入粉煤灰吸附剂对中水进行前处理,粉煤灰吸附剂投加重量和中水重量比例在0.8:100之间,处理时间为3h;所述的粉煤灰吸附剂由如下方法制备:(A)、按照重量份数:生石灰10份,蒙脱土5份,蛭石1份,粘土2份,甲基纤维素2份,溴化钠1份,氧化铝5份,粉煤灰100份,将各原料混合均匀,加水制成直径为35mm球形颗粒,再在隧道窑于950℃下烧结2h,冷却后得到粉煤灰吸附剂前体;(B)、配制摩尔浓度为1mol/L的溴化钠水溶液,将步骤(A)得到的粉煤灰吸附剂前体倒入所述溴化钠水溶液中进行浸渍处理16h,(C)、将经过步骤(B)浸渍处理的粉煤灰吸附剂前体放入真空烘箱中干燥处理10h后,得到粉煤灰吸附剂;(1) Fly ash adsorbent treatment: introduce reclaimed water into the fly ash treatment pool, put fly ash adsorbent into the pool to pre-treat the reclaimed water, the ratio of the weight of fly ash adsorbent to the weight of reclaimed water Between 0.8:100, the treatment time is 3h; the described fly ash adsorbent is prepared by the following method: (A), in parts by weight: 10 parts of quicklime, 5 parts of montmorillonite, 1 part of vermiculite, clay 2 parts, 2 parts of methyl cellulose, 1 part of sodium bromide, 5 parts of alumina, 100 parts of fly ash, mix all raw materials evenly, add water to make spherical particles with a diameter of 35 mm, and then put them in a tunnel kiln at 950 ° C Sinter 2h, obtain the fly ash sorbent precursor after cooling; (B), preparation molar concentration is the sodium bromide aqueous solution of 1mol/L, the fly ash sorbent precursor that step (A) obtains is poured into the bromine Sodium chloride aqueous solution is impregnated for 16 hours, (C), the fly ash adsorbent precursor that has been impregnated in step (B) is put into a vacuum oven for drying for 10 hours, and the fly ash adsorbent is obtained;

(2)生物除臭剂处理:将粉煤灰吸附剂处理的中水引入生物除臭池中,向池中投加生物除臭剂,生物除臭剂投加重量和中水重量比例在0.1:100,处理时间为3天;所述的生物除臭剂的微生物菌种组成为:嗜酸乳杆菌108-109个/mL、短小芽孢杆菌108-109个/mL、枯草芽孢杆菌106-107个/mL、荧光假单胞菌106-107个/mL、沼泽红假单胞菌106-107个/mL、班图酒香酵母菌105-106个/mL、平常假丝酵母菌105-106个/mL、扩张青霉105-106个/mL、米根霉105-106个/mL、绿色木霉105-106个/mL、细黄链霉菌105-106个/mL和灰色链霉菌105-106个/mL;(2) Biological deodorant treatment: introduce the reclaimed water treated with fly ash adsorbent into the biological deodorization tank, add biological deodorizer to the pool, and the ratio of the weight of biological deodorant to the weight of reclaimed water is 0.1 : 100, and the treatment time was 3 days; the microbial strains of the biological deodorant consisted of: Lactobacillus acidophilus 10 8 -10 9 /mL, Bacillus pumilus 10 8 -10 9 /mL, Bacillus subtilis Bacillus 10 6 -10 7 /mL, Pseudomonas fluorescens 10 6 -10 7 /mL, Rhodopseudomonas palustris 10 6 -10 7 /mL, Bantu Brettanomyces 10 5 -10 6 1/mL, Candida vulgaris 10 5 -10 6 /mL, Penicillium expansica 10 5 -10 6 /mL, Rhizopus oryzae 10 5 -10 6 /mL, Trichoderma viride 10 5 -10 6 1/mL, Streptomyces flavinus 10 5 -10 6 /mL and Streptomyces griseus 10 5 -10 6 /mL;

(3)生物净化剂处理:将生物除臭剂处理的中水引入生物净化池中,向池中投加生物净化剂,生物净化剂投加重量和中水重量比例在0.8:100,处理时间为5天,调整曝气条件使得中水中的溶解氧的量为3mg/L;所述的生物净化剂中的菌种包括血色红假单胞菌,泾阳链霉菌,以及乳酸链球菌,所述的菌种的培养基由下列质量比的组分组成:红糖5%,酵母粉2%,余量为水;(3) Biological purification agent treatment: introduce the reclaimed water treated with biological deodorant into the biological purification tank, add biological deodorizer to the pool, the ratio of the weight of biological deodorizer to the weight of reclaimed water is 0.8:100, and the treatment time For 5 days, adjust the aeration condition so that the amount of dissolved oxygen in the middle water is 3mg/L; The bacterial classification in the described bio-cleaning agent comprises Rhodopseudomonas sanguinus, Streptomyces jingyang, and Streptococcus lactis, described The culture medium of the bacterial classification is made up of the component of following mass ratio: brown sugar 5%, yeast powder 2%, surplus is water;

(4)改性丝光沸石吸附处理:将生物净化剂处理的中水经过过滤后使用提升泵输送至位于吸附塔底部的吸附塔进水口,吸附塔从下往上依次填充有无纺布层、石英砂层和改性沸石层,其中,无纺布层的厚度为20mm,石英砂层和改性沸石层的厚度比值为1:0.8,水从位于吸附塔顶部的吸附塔出水口流出,经泵输送至储水槽,为深度处理产品水;所述的改性沸石为改性丝光沸石,改性步骤是:将丝光沸石、高岭土、硅镁胶、田菁粉和磷酸按照重量比例60:30:30:20:20混合均匀,然后加水制备成固含量为55%的浆液;浆液喷雾干燥成粉状颗粒,然后将粉状颗粒在马弗炉中于500℃焙烧3h,然后冷却至室温,得改性沸石,其中磷酸的摩尔浓度为0.9mol/L。(4) Adsorption treatment of modified mordenite: the reclaimed water treated with biological purifiers is filtered and transported to the water inlet of the adsorption tower at the bottom of the adsorption tower by a lift pump. The adsorption tower is filled with non-woven fabric layers, Quartz sand layer and modified zeolite layer, wherein, the thickness of the non-woven fabric layer is 20mm, the thickness ratio of the quartz sand layer and the modified zeolite layer is 1:0.8, and the water flows out from the outlet of the adsorption tower at the top of the adsorption tower. The pump is transported to the water storage tank for advanced treatment of product water; the modified zeolite is modified mordenite, and the modification step is: mix mordenite, kaolin, silica-magnesium gel, scallop powder and phosphoric acid in a weight ratio of 60:30 :30:20:20 Mix evenly, then add water to prepare a slurry with a solid content of 55%; the slurry is spray-dried into powder particles, and then the powder particles are roasted in a muffle furnace at 500°C for 3 hours, and then cooled to room temperature, A modified zeolite was obtained, wherein the molar concentration of phosphoric acid was 0.9 mol/L.

为了测试实施例1、2、3的产品水水质,发明人将实施例1、2、3得到的产品水按照《城镇污水处理厂污染物排放标准GB18918-2002》进行检测,检测结果如表1所示,可以看出,水质均优于国家一级A标准,能够用于景观用水。表1为实施例1、2的结果。In order to test the product water quality of Examples 1, 2, and 3, the inventor tested the product water obtained in Examples 1, 2, and 3 according to the "Urban Sewage Treatment Plant Pollutant Discharge Standard GB18918-2002", and the test results are shown in Table 1 As shown, it can be seen that the water quality is better than the national first-class A standard and can be used for landscape water. Table 1 is the result of embodiment 1,2.

尽管上述实施例对本发明做出了详尽的描述,但它仅仅是本发明一部分实施例,而不是全部实施例,人们还可以根据本实施例在不经创造性前提下获得其他实施例,这些实施例都属于本发明的保护范围。Although the foregoing embodiment has described the present invention in detail, it is only a part of the embodiments of the present invention, rather than all embodiments, and people can also obtain other embodiments according to the present embodiment without inventive step, these embodiments All belong to the protection scope of the present invention.

Claims (1)

1. the method for an applying modified modenite processing municipal middle water, the COD value of described middle water is between 65-95mg/L, it is characterized in that, described method comprises fly ash absorbent processing, biological deodorant processing, biological cleanser processing, the modified mordenite adsorption treatment of carrying out in turn; Be specially:
(1) fly ash absorbent processing: middle water is introduced in flyash treatment pond, and Xiang Chizhong drops into fly ash absorbent centering water and carries out pre-treatment, fly ash absorbent adds weight and middle water weight ratio example between 0.8-2.8:100, and the processing time is 3-36h; Described fly ash absorbent is prepared by the following method: (A), according to parts by weight: quick lime 10-15 part, imvite 5-9 part, vermiculite 1-5 part, clay 2-20 part, methylcellulose 2-6 part, sodium bromide 1-2 part, aluminium oxide 5-10 part, flyash 100-240 part, each raw material is mixed, adding water and making diameter is 35-45mm spheric granules, then at tunnel cave sintering 2-3h at 950-980 DEG C, obtains fly ash absorbent precursor after cooling; (B) aqueous sodium bromide that, preparation molar concentration is 1-1.5mol/L, the fly ash absorbent precursor that step (A) is obtained is poured into and in described aqueous sodium bromide, is carried out impregnation process 16-24h, (C), by putting into through the fly ash absorbent precursor of step (B) impregnation process after the dry 10-20h of processing of vacuum drying oven, obtain fly ash absorbent;
(2) biological deodorant processing: the middle water of fly ash absorbent processing is introduced in biological deodorization tank, and Xiang Chizhong adds biological deodorant, biological deodorant adds weight and middle water weight ratio example between 0.1-0.8:100, and the processing time is 3-5 days; The microorganism fungus kind of described biological deodorant consists of: lactobacillus acidophilus 106-109Individual/mL, bacillus pumilus 106-109Individual/mL, bacillus subtilis 106-109Individual/mL, Pseudomonas fluorescens 105-107Individual/mL, Rhodopseudomonas palustris 105-107Individual/mL, the figure of class British mold 104-106Individual/mL, candida inconspicua bacterium 104-106Individual/mL, expansion mould 104-106Individual/mL, Rhizopus oryzae 104-106Individual/mL, Trichoderma viride 104-106Individual/mL, streptomyces microflavus 104-106Individual/mL and streptomyces griseus 104-106Individual/mL;
(3) biological cleanser processing: the middle water of biological deodorant processing is introduced in biological purifying tank, Xiang Chizhong adds biological cleanser, biological cleanser adds weight and middle water weight ratio example between 0.8-6.8:100, processing time is 5-9 days, and it is 3-4mg/L that adjustment aeration condition makes the amount of the dissolved oxygen in middle water; Bacterial classification in described biological cleanser comprises Rhodopseudomonas rutila, Jingyang streptomycete, and streptococcus lactis, and the culture medium of described bacterial classification is made up of the component of following mass ratio: brown sugar 5-6%, dusty yeast 1-2%, surplus is water;
(4) modified mordenite adsorption treatment: the adsorption tower water inlet that the middle water of biological cleanser processing is used elevator pump to be delivered to be positioned at after filtering adsorption tower bottom, adsorption tower is filled with nonwoven layer from the bottom up successively, quartz sand layer and modified zeolite layer, wherein, the thickness of nonwoven layer is between 2-20mm, the thickness ratio of quartz sand layer and modified zeolite layer is 1:0.5-0.8, the modification procedure of described modified mordenite is: by modenite, kaolin, silicon magnesium glue, sesbania powder and phosphoric acid mix according to part by weight 60:30:30:20:20, then add water and be prepared into the slurries that solid content is 50-55%, slurries are spray dried to powdery particle, then by powdered granule in Muffle furnace in 500-700 DEG C of roasting 3-5h, be then cooled to room temperature, obtain modified zeolite, water flows out from the adsorption tower delivery port that is positioned at adsorption tower top, is delivered to aqua storage tank through pump, is advanced treating product water.
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