CN115893784A - A method for reducing hydrogen sulfide production during sludge treatment - Google Patents
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Abstract
Description
技术领域technical field
本发明属于环境保护以及污泥处理资源化技术领域,具体涉及一种以间歇、脉冲投加过氧化钙来减少污泥处理过程中硫化氢产生的方法。The invention belongs to the technical field of environmental protection and sludge treatment and resource utilization, and in particular relates to a method for reducing the generation of hydrogen sulfide in the process of sludge treatment by adding calcium peroxide intermittently and in pulses.
技术背景technical background
随着城市化进程的不断加快,污水处理厂的污水处理量也在日益增长,同时剩余污泥产量也不断增多。由于污水的来源良莠不齐,其中可能含有各种各样的污染物,这些物质经过市政管网,最终进入到污水处理厂,因此剩余污泥中含有大量病原微生物、重金属和有机污染物,处理处置不当易对环境造成二次污染。With the continuous acceleration of urbanization, the sewage treatment capacity of sewage treatment plants is also increasing, and the output of surplus sludge is also increasing. Because the sources of sewage vary from good to bad, it may contain various pollutants. These substances pass through the municipal pipe network and finally enter the sewage treatment plant. Therefore, the remaining sludge contains a large number of pathogenic microorganisms, heavy metals and organic pollutants, which cannot be properly treated. Easy to cause secondary pollution to the environment.
剩余污泥处理成本高昂,但剩余污泥中富含的有机物和营养物质却可通过生产能源物质进行回收利用。厌氧发酵是一种使实现无害化、资源化的有效处置方法,可以降解可生物降解的有机物,稳定和还原剩余污泥,杀死病原体,而且可以从污泥中回收大量的短链脂肪酸、氢气和甲烷等具有高附加值的产品,达到了变废为宝的效果,对于缓解目前的能源危机具有很大的作用。The cost of excess sludge treatment is high, but the organic matter and nutrients rich in excess sludge can be recycled through the production of energy substances. Anaerobic fermentation is an effective disposal method to achieve harmlessness and resource utilization. It can degrade biodegradable organic matter, stabilize and reduce excess sludge, kill pathogens, and recover a large amount of short-chain fatty acids from sludge. Products with high added value, such as hydrogen, methane, etc., have achieved the effect of turning waste into wealth, which has a great effect on alleviating the current energy crisis.
污泥厌氧发酵在降解有机物产生高附加值产品的同时,还会产生硫化氢气体。而硫化氢散发的恶臭问题除了污染环境,对人体也会产生一定的危害。硫化氢是可溶于水、无色、有臭鸡蛋气味的剧毒气体,是强烈的刺激性、窒息性神经毒素。在很低的浓度下也可以闻到臭味,10ppm以上会产生部分症状反应,如流泪、咳嗽、恶心、呕吐等症状,300ppm以上人体的生命就会受到威胁。由于硫化氢气体对健康的严重危害,使得硫化氢的控制研究成为研究机构等关注的重要热点问题之一。因此,很有必要寻找一种操作简便、安全便宜且高效的抑制污泥厌氧发酵产生硫化氢的方法。Anaerobic fermentation of sludge produces hydrogen sulfide gas while degrading organic matter to produce high value-added products. The stench of hydrogen sulfide not only pollutes the environment, but also causes certain harm to the human body. Hydrogen sulfide is a highly toxic gas that is soluble in water, colorless, and smells like rotten eggs. It is a strong irritant and asphyxiating neurotoxin. Smell can also be smelled at very low concentrations. Above 10ppm will produce some symptoms, such as tearing, coughing, nausea, vomiting and other symptoms. Above 300ppm, human life will be threatened. Due to the serious health hazards of hydrogen sulfide gas, the research on the control of hydrogen sulfide has become one of the important hot issues concerned by research institutions. Therefore, it is necessary to find a simple, safe, cheap and efficient method to inhibit the production of hydrogen sulfide from sludge anaerobic fermentation.
过氧化钙作为一种氧化性和缓释型兼具的过氧化物,已被广泛应用于水产养殖、农业、医药和水体处理等领域,具有价格低廉、氧化能力强、安全方便操作使用等优点。缓释型是指当过氧化钙溶解在含水介质中时,它会缓慢分解为过氧化氢、氧气和氢氧化钙。基于这种特殊理化特征,过氧化钙已被作为污泥预处理的添加剂。其能够有效的促进污泥细胞的破碎,增加有机物的释放,因此,此前过氧化钙被广泛的用于污水中污染物的去除、污泥的脱水、厌氧发酵产挥发性脂肪酸和氢气,然而,到目前为止,利用过氧化钙减少污泥处理过程中硫化氢产生的方法还没有被报道。Calcium peroxide, as an oxidizing and slow-release peroxide, has been widely used in aquaculture, agriculture, medicine, water treatment and other fields. It has the advantages of low price, strong oxidizing ability, safe and convenient operation and use. . Slow release means that when calcium peroxide is dissolved in an aqueous medium, it slowly decomposes into hydrogen peroxide, oxygen and calcium hydroxide. Based on this special physical and chemical characteristics, calcium peroxide has been used as an additive for sludge pretreatment. It can effectively promote the breakdown of sludge cells and increase the release of organic matter. Therefore, calcium peroxide has been widely used in the removal of pollutants in sewage, dehydration of sludge, and anaerobic fermentation to produce volatile fatty acids and hydrogen. So far, the use of calcium peroxide to reduce hydrogen sulfide production during sludge treatment has not been reported.
发明内容Contents of the invention
本发明的目的在于提供一种抑制污泥厌氧发酵产生硫化氢的方法,即采用间歇、脉冲投加过氧化钙的方式减少污泥处理过程中硫化氢产生。可以有效降低药品的投加频率,节省药品成本和运行成本,从而提供一种快速高效、投入小且对环境无潜在风险的控制污泥厌氧发酵产硫化氢的控制方法。The object of the present invention is to provide a method for inhibiting the generation of hydrogen sulfide by anaerobic fermentation of sludge, that is, to reduce the generation of hydrogen sulfide in the process of sludge treatment by intermittent and pulse dosing of calcium peroxide. It can effectively reduce the frequency of drug dosing, save drug costs and operating costs, and thus provide a fast, efficient, low-input, and no potential risk to the environment control method for controlling the production of hydrogen sulfide by anaerobic fermentation of sludge.
为了实现上述目的,本发明采用的技术方法包括以下步骤:In order to achieve the above object, the technical method adopted in the present invention comprises the following steps:
(1)对来自城市污水处理厂的初沉污泥和剩余污泥进行自然沉降。沉降时间为24小时,温度为4℃。(1) Natural settlement of primary sludge and excess sludge from urban sewage treatment plants. The settling time was 24 hours and the temperature was 4°C.
(2)去除上清液,将其浓缩为挥发性固体含量为20-35g/L的剩余污泥,得到发酵原料。(2) removing the supernatant and concentrating it into excess sludge with a volatile solid content of 20-35g/L to obtain fermentation raw materials.
(3)将过氧化钙投加到上述污泥进行混合处理,在厌氧环境下进行发酵。(3) Calcium peroxide is added to the above sludge for mixed treatment, and fermentation is carried out under anaerobic environment.
上述步骤(3)中,采用3次等量脉冲式投加,投加间隔为10-30分钟,此方式在不增加实际用量的情况下仅通过改变投加方式,能显著的抑制硫化氢的产生,从而达到更好的控制效果。In the above step (3), 3 times of equal-volume pulse dosing are adopted, and the dosing interval is 10-30 minutes. This method can significantly suppress the generation of hydrogen sulfide by changing the dosing method without increasing the actual dosage. resulting in better control.
(4)利用过氧化钙间断性地处理发酵污泥,在短期内往反应器中投加过氧化钙,经过5-10天,再次利用过氧化钙在短时间内处理污泥。事实上,本发明人相信用于处理污泥的最佳时期将取决于该特定环境的具体运行参数。本领域技术人员可容易地通过进行相当直接的实验来确定处理和静息的最佳时期。(4) Use calcium peroxide to treat fermented sludge intermittently, add calcium peroxide to the reactor in a short period of time, and after 5-10 days, use calcium peroxide to treat sludge again in a short period of time. In fact, the inventors believe that the optimal period for treating sludge will depend on the specific operating parameters of that particular environment. Optimum periods of treatment and resting can be readily determined by those skilled in the art by performing fairly straightforward experiments.
上述步骤(3)中,过氧化钙的投加总量为0.05~0.25g/g VSS,优选为0.1~0.15g/gVSS。发酵环境为厌氧环境,即向污泥中添加过氧化钙后通入氮气(氮气纯度为90.00%-99.99%)5min,以除去反应器中氧气的存在,密封之后将反应器放入至35℃,震荡速度为125rpm/min的摇床中。In the above-mentioned step (3), the total amount of calcium peroxide added is 0.05~0.25g/gVSS, preferably 0.1~0.15g/gVSS. The fermentation environment is an anaerobic environment, that is, after adding calcium peroxide to the sludge, nitrogen gas (nitrogen purity is 90.00%-99.99%) is introduced for 5 minutes to remove the presence of oxygen in the reactor. After sealing, the reactor is put into 35 °C in a shaker with a shaking speed of 125 rpm/min.
上述步骤(3)中,污泥厌氧发酵的时间为12-25天。In the above step (3), the time for sludge anaerobic fermentation is 12-25 days.
在一个优选的实施案例中,过氧化钙的投加量为0.1~0.15g/g VSS。虽然过氧化钙用量在一定范围内都能抑制污泥厌氧发酵产生硫化氢,并且在一定范围内,随着过氧化钙的用量的增加,对污泥厌氧发酵产硫化氢的抑制效果越明显。但是考虑到原料成本和硫化氢产量的关系,本发明采用的较理想的过氧化钙的用量范围在0.1~0.15g/g VSS。In a preferred implementation case, the dosage of calcium peroxide is 0.1-0.15g/g VSS. Although the amount of calcium peroxide can inhibit the production of hydrogen sulfide by anaerobic fermentation of sludge within a certain range, and within a certain range, with the increase of the amount of calcium peroxide, the inhibitory effect on the production of hydrogen sulfide by anaerobic fermentation of sludge is more effective. obvious. But consider the relation of raw material cost and hydrogen sulfide output, the consumption scope of the ideal calcium peroxide that the present invention adopts is at 0.1~0.15g/g VSS.
上述步骤(3)中采用分步脉冲方式投加过氧化钙时,优选投加间隔时间为10-20分钟。When calcium peroxide is dosed in a step-by-step pulse manner in the above step (3), the preferred dosing interval is 10-20 minutes.
上述步骤(4)中采用间歇方式投加过氧化钙时,优选投加间隔时间为6-8天。When adopting intermittent mode to add calcium peroxide in the above-mentioned step (4), preferably adding interval time is 6-8 days.
由于采用了以上的技术方案,本发明具有以下成果:Owing to adopting above technical scheme, the present invention has following achievement:
1.本发明利用过氧化钙与水反应产生过氧化氢、氢氧化钙和氧气,并进而产生羟基自由基等活性氧自由基等优点来抑制污泥厌氧发酵产硫化氢。它能够显著的抑制剩余污泥中硫酸盐还原菌的丰度,降低相关微生物酶的活性,对实现污泥厌氧发酵的大规模的应用具有重要的意义,对环境的保护具有积极的影响。1. The present invention utilizes calcium peroxide to react with water to produce hydrogen peroxide, calcium hydroxide and oxygen, and then produce active oxygen free radicals such as hydroxyl radicals to suppress sludge anaerobic fermentation and produce hydrogen sulfide. It can significantly inhibit the abundance of sulfate-reducing bacteria in excess sludge and reduce the activity of related microbial enzymes, which is of great significance for the large-scale application of sludge anaerobic fermentation and has a positive impact on environmental protection.
2.与现有技术相比,本发明能够在极短的作用时间内能明显降低污泥处理过程中内硫化氢的产生,采用间歇、脉冲投加方式,有效降低了过氧化钙的投加频率,节省了药品成本和运行成本费用。2. Compared with the prior art, the present invention can significantly reduce the generation of internal hydrogen sulfide in the process of sludge treatment within a very short action time, and adopts intermittent and pulse dosing methods to effectively reduce the dosing of calcium peroxide frequency, saving drug costs and running costs.
3.本发明抑制了污泥厌氧发酵中硫化氢这种有毒有害物质的产生,既减轻了对环境乃至人体的危害,又能够促进污泥厌氧发酵这项技术安全有效的推广,对于污泥的减量和资源化具有重要的意义。添加过氧化钙预处理的策略对实际应用具有环境友好性和环境经济性的优点,也进一步拓展了过氧化钙在工程上的应用领域。3. The present invention suppresses the production of toxic and harmful substances such as hydrogen sulfide in sludge anaerobic fermentation, which not only reduces the harm to the environment and even the human body, but also promotes the safe and effective promotion of sludge anaerobic fermentation technology. The reduction and resource utilization of mud is of great significance. The strategy of adding calcium peroxide pretreatment has the advantages of environmental friendliness and environmental economy for practical application, and further expands the application field of calcium peroxide in engineering.
附图说明Description of drawings
图1为本发明的工艺流程图。Fig. 1 is a process flow diagram of the present invention.
具体实施方式Detailed ways
以下结合具体实际案例对本发明做进一步的描述,但并不限制本发明的保护范围。The present invention will be further described below in conjunction with specific practical cases, but the protection scope of the present invention will not be limited.
实施案例1:过氧化钙单次简单投加对硫化氢产生的影响Implementation case 1: Effect of single simple dosing of calcium peroxide on hydrogen sulfide production
(1)在工作体积为4L的有机玻璃容器中,将城市污水处理厂产生的污泥放在4℃下自然沉降1d,除去上清液后得到发酵的原料。(1) In a plexiglass container with a working volume of 4L, the sludge produced by the municipal sewage treatment plant was placed at 4°C for 1 day to naturally settle, and the fermented raw material was obtained after removing the supernatant.
(2)将500mL(1)中得到的污泥加入反应器中,并投加0.1g/g VSS的过氧化钙,搅拌均匀,往反应器中充入氮气,持续5min以去除氧气,密封反应器放入摇床进行厌氧发酵,其中,摇床发酵温度为35±1℃,震荡速度为125rpm/min,发酵时间(即污泥在反应器中的停留时间)为13d,硫化氢的产量为152.3978*10-4mg/g VSS。(2) Add 500mL of the sludge obtained in (1) into the reactor, and add 0.1g/g VSS calcium peroxide, stir evenly, fill the reactor with nitrogen, continue for 5min to remove oxygen, and seal the reaction The shaker was placed in a shaker for anaerobic fermentation, wherein the shaker fermentation temperature was 35±1°C, the shaking speed was 125rpm/min, the fermentation time (that is, the residence time of the sludge in the reactor) was 13 days, and the hydrogen sulfide output It is 152.3978*10 -4 mg/g VSS.
实施案例2:过氧化钙单次简单投加对硫化氢产生的影响Implementation case 2: Effect of single simple dosing of calcium peroxide on hydrogen sulfide production
(1)在工作体积为4L的有机玻璃容器中,将城市污水处理厂产生的污泥放在4℃下自然沉降1d,除去上清液后得到发酵的原料。(1) In a plexiglass container with a working volume of 4L, the sludge produced by the municipal sewage treatment plant was placed at 4°C for 1 day to naturally settle, and the fermented raw material was obtained after removing the supernatant.
(2)将500mL(1)中得到的污泥加入反应器中,并投加0.15g/g VSS的过氧化钙,搅拌均匀,往反应器中充入氮气,持续5min以去除氧气,密封反应器放入摇床进行厌氧发酵,其中,摇床发酵温度为35±1℃,震荡速度为125rpm/min,发酵时间(即污泥在反应器中的停留时间)为13d,硫化氢的产量为90.5266*10-4mg/g VSS。(2) Add 500mL of the sludge obtained in (1) into the reactor, and add 0.15g/g VSS calcium peroxide, stir evenly, fill the reactor with nitrogen, continue for 5min to remove oxygen, and seal the reaction The shaker was placed in a shaker for anaerobic fermentation, wherein the shaker fermentation temperature was 35±1°C, the shaking speed was 125rpm/min, the fermentation time (that is, the residence time of the sludge in the reactor) was 13 days, and the hydrogen sulfide output It is 90.5266*10 -4 mg/g VSS.
实施案例3:过氧化钙间歇、脉冲投加对硫化氢产生的影响Implementation Case 3: Effect of Intermittent and Pulse Dosing of Calcium Peroxide on Hydrogen Sulfide Production
(1)在工作体积为4L的有机玻璃容器中,将城市污水处理厂产生的污泥放在4℃下自然沉降1d,除去上清液后得到发酵的原料。(1) In a plexiglass container with a working volume of 4L, the sludge produced by the municipal sewage treatment plant was placed at 4°C for 1 day to naturally settle, and the fermented raw material was obtained after removing the supernatant.
(2)将500mL(1)中得到的污泥加入反应器中,并采用间歇、脉冲的方式投加0.1g/gVSS的过氧化钙(投加总量与实施案例(1)相同,投加间歇时间为8天,脉冲间隔为15分钟),搅拌均匀,往反应器中充入氮气,持续5min以去除氧气,密封反应器放入摇床进行厌氧发酵,其中,摇床发酵温度为35±1℃,震荡速度为125rpm/min,发酵时间(即污泥在反应器中的停留时间)为13d,硫化氢的产量为121.5547*10-4mg/g VSS。(2) Add 500mL of the sludge obtained in (1) into the reactor, and add calcium peroxide of 0.1g/gVSS in an intermittent and pulsed manner (the total amount of addition is the same as that of the implementation case (1). The intermittent time is 8 days, and the pulse interval is 15 minutes), stir evenly, fill the reactor with nitrogen, continue for 5min to remove oxygen, seal the reactor and put it into a shaker for anaerobic fermentation, wherein the shaker fermentation temperature is 35 ±1°C, the shaking speed was 125rpm/min, the fermentation time (that is, the residence time of the sludge in the reactor) was 13 days, and the production of hydrogen sulfide was 121.5547*10 -4 mg/g VSS.
实施案例4:过氧化钙间歇、脉冲投加对硫化氢产生的影响Implementation Case 4: Effect of Intermittent and Pulse Dosing of Calcium Peroxide on Hydrogen Sulfide Production
(1)在工作体积为4L的有机玻璃容器中,将城市污水处理厂产生的污泥放在4℃下自然沉降1d,除去上清液后得到发酵的原料。(1) In a plexiglass container with a working volume of 4 L, put the sludge produced by the urban sewage treatment plant at 4° C. for 1 day, and remove the supernatant to obtain the fermented raw material.
(2)将500mL(1)中得到的污泥加入反应器中,并采用间歇、脉冲的方式投加0.15g/g VSS的过氧化钙((投加总量与实施案例(2)相同,投加间歇时间为8天,脉冲间隔为15分钟),搅拌均匀,往反应器中充入氮气,持续5min以去除氧气,密封反应器放入摇床进行厌氧发酵,其中,摇床发酵温度为35±1℃,震荡速度为125rpm/min,发酵时间(即污泥在反应器中的停留时间)为13d,硫化氢的产量为71.0537*10-4mg/g VSS。(2) The sludge obtained in 500mL (1) is added to the reactor, and the calcium peroxide of 0.15g/g VSS is added intermittently and pulsed ((the total amount of addition is the same as that of the implementation case (2), Dosing intermittent time is 8 days, pulse interval is 15 minutes), stir evenly, fill nitrogen into the reactor, continue 5min to remove oxygen, seal the reactor and put it into the shaker for anaerobic fermentation, wherein, the shaker fermentation temperature The temperature is 35±1°C, the shaking speed is 125rpm/min, the fermentation time (that is, the residence time of the sludge in the reactor) is 13 days, and the hydrogen sulfide production is 71.0537*10 -4 mg/g VSS.
对比案例1Comparative case 1
(1)在工作体积为4L的有机玻璃容器中,将城市污水处理厂产生的污泥放在4℃下自然沉降1d,除去上清液后得到发酵的原料。(1) In a plexiglass container with a working volume of 4 L, put the sludge produced by the urban sewage treatment plant at 4° C. for 1 day, and remove the supernatant to obtain the fermented raw material.
(2)将500mL(1)中得到的污泥加入反应器中,不投加过氧化钙,搅拌均匀,往反应器中充入氮气,持续5min以去除氧气,密封反应器放入摇床进行厌氧发酵,其中,摇床发酵温度为35±1℃,震荡速度为125rpm/min,发酵时间(即污泥在反应器中的停留时间)为13d,硫化氢的产量为309.0909*10-4mg/g VSS。(2) Add 500mL of the sludge obtained in (1) into the reactor without adding calcium peroxide, stir evenly, fill the reactor with nitrogen, and continue for 5min to remove oxygen, seal the reactor and put it in a shaker Anaerobic fermentation, wherein the shaking table fermentation temperature is 35±1°C, the shaking speed is 125rpm/min, the fermentation time (that is, the residence time of the sludge in the reactor) is 13 days, and the hydrogen sulfide production is 309.0909*10 -4 mg/g VSS.
实施案例和对比例的氢气产量如表1所示:The hydrogen output of implementation case and comparative example is as shown in table 1:
表1实施例与对比例的发酵比较表The fermentation comparative table of table 1 embodiment and comparative example
从表中可以看出,实施案例1至实施案例4的硫化氢产量比对比案例1的硫化氢产量有了很大的减少,尤其是在最优条件下,采用间歇、脉冲的方式投加的实施案例2和4的硫化氢产量比对比案例1的硫化氢产量减少最大。It can be seen from the table that the hydrogen sulfide production of implementation cases 1 to 4 has been greatly reduced compared with the production of hydrogen sulfide in comparative case 1, especially under optimal conditions, the mode of intermittent and pulse feeding is adopted. The hydrogen sulfide production of the implementation cases 2 and 4 is the largest reduction compared with the hydrogen sulfide production of the comparative case 1.
上述对实施例的描述是为了便于该技术领域的普通技术人员能理解和使用本发明。虽然本发明已以较佳的实施例揭示如上,然而并非用以限定本发明。在不脱离本发明的精神实质和技术方案的情况下,熟悉本领域技术的人员可以对本发明技术方案做出许多可能的修改,或者修改为等同变化的等效实施例。因此,凡是不脱离本发明范畴所做任何简单的改进和修改都应该在本发明的保护范围之内。The above description of the embodiments is for those of ordinary skill in the art to understand and use the present invention. Although the present invention has been disclosed above with preferred embodiments, it is not intended to limit the present invention. Without departing from the spirit and technical solutions of the present invention, those skilled in the art can make many possible modifications to the technical solutions of the present invention, or modify them into equivalent embodiments with equivalent changes. Therefore, any simple improvements and modifications that do not depart from the scope of the present invention should fall within the protection scope of the present invention.
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