CN107055946A - A kind of method that utilization chlorella purifies pig farm fermentation waste water - Google Patents
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Abstract
Description
技术领域technical field
本发明涉及一种利用小球藻净化猪场发酵废水的方法。The invention relates to a method for purifying pig farm fermentation waste water by using chlorella.
背景技术Background technique
随着经济的发展,养猪业的经营模式趋势规模化,发展迅猛,废水排放量也日益增加,随之而来的环境问题也越来越严重。猪场废水进行发酵产沼气是目前集约化养猪场处理废水的较为普遍的方式,但发酵后的沼液仍属于高浓度有机废水,不能达到排放标准。发酵后的沼液处理方式有人工湿地法、生物塘法及MBR反应器处理等,但这些方法由于成本过高等问题难以在实际中应用,因此目前猪场发酵废水处理的主要形式是经过简单的处理后直接排放。With the development of the economy, the business model of the pig industry tends to be large-scale and develop rapidly. The amount of wastewater discharge is also increasing, and the ensuing environmental problems are becoming more and more serious. Fermentation of pig farm wastewater to produce biogas is a relatively common way to treat wastewater in intensive pig farms. However, the biogas slurry after fermentation is still high-concentration organic wastewater and cannot meet the discharge standards. Biogas slurry treatment methods after fermentation include artificial wetland method, biological pond method and MBR reactor treatment, etc., but these methods are difficult to be applied in practice due to problems such as high cost. Therefore, the main form of fermentation wastewater treatment in pig farms is simple Discharge directly after treatment.
小球藻是一种球形单细胞淡水藻类,是一种高效的光合植物,以光合自养生长繁殖,细胞内的蛋白质、脂肪和碳水化合物含量都很高,又有多种维生素,可食用和作为饵料。Chlorella is a spherical single-celled freshwater algae. It is a highly efficient photosynthetic plant. It grows and reproduces by photoautotrophy. The protein, fat and carbohydrate content in the cells are very high, and there are many vitamins. It is edible and as bait.
发明内容Contents of the invention
本发明提出了一种利用小球藻净化猪场发酵废水的方法,解决了目前猪场发酵废水采用传统方法不够经济或者直接排放污染环境的问题。The invention proposes a method for purifying pig farm fermentation waste water by using chlorella, which solves the problem that the current pig farm fermentation waste water is not economical or directly discharged to pollute the environment.
本发明的技术方案是这样实现的:Technical scheme of the present invention is realized like this:
一种利用小球藻净化猪场发酵废水的方法,至少包括以下步骤:A method utilizing chlorella to purify fermented wastewater from pig farms, at least comprising the following steps:
(1)猪场发酵废水预处理后进入调节池调节pH=6.5-7.5及废水浓度;(1) After the pig farm fermentation wastewater is pretreated, it enters the adjustment tank to adjust the pH=6.5-7.5 and the concentration of the wastewater;
(2)小球藻在废水中进行驯化培养,最终获得在体积分数为50%-70%的废水中能快速生长的藻种;(2) Chlorella is domesticated and cultivated in wastewater, and finally obtains algae species that can grow rapidly in wastewater with a volume fraction of 50%-70%;
(3)将驯化后的藻种种子液接种到废水中,在封闭式光生物反应器中培养;(3) Inoculate the acclimated algae seed solution into the waste water and cultivate it in a closed photobioreactor;
(4)采收小球藻,废水处理完成。(4) The chlorella is harvested, and the waste water treatment is completed.
优选地,步骤(1)中预处理过程为:猪场发酵废水经固液分离后,清液进曝气池曝气,曝气48h后进沉淀池沉淀时间2h,上清进消毒池,用强氯精消毒,16-24h后曝气30-60min,加入硫代硫酸钠中和。Preferably, the pretreatment process in step (1) is as follows: after the pig farm fermented wastewater is separated from solid and liquid, the clear liquid enters the aeration tank for aeration, after 48 hours of aeration, enters the sedimentation tank for 2 hours, and the supernatant enters the disinfection tank, and uses strong Disinfect with chlorine essence, aerate for 30-60 minutes after 16-24 hours, and add sodium thiosulfate to neutralize.
优选地,所述强氯精的添加量为6-30g/m3,硫代硫酸钠加入量为强氯精质量的2-3倍。Preferably, the added amount of the strong chloroquine is 6-30g/m3, and the added amount of sodium thiosulfate is 2-3 times of the quality of the strong chloroquine.
优选地,步骤(2)中依次在体积分数为20%-100%的废水中驯化小球藻,小球藻置于恒温培养室中的摇床上培养,培养温度23-26℃,摇床转速180rmp/min,光照3000-4000lux,最终筛出能在体积分数为50%-70%的废水中能够快速生长的藻种。Preferably, in step (2), the chlorella is domesticated sequentially in waste water with a volume fraction of 20%-100%, and the chlorella is cultivated on a shaker in a constant temperature culture room, the culture temperature is 23-26°C, and the shaker speed is 180rmp/min, light 3000-4000lux, and finally screen out algae species that can grow rapidly in wastewater with a volume fraction of 50%-70%.
优选地,步骤(3)具体为:将驯化好并扩培的种子液接种到预处理后的废水中,在密闭式光生物反应器中培养,接种量体积分数为10%-20%,使OD=0.2-0.3,培养条件为pH=6.5-7.5,光照5000-6000lux,温度23-26℃,培养9-12天。Preferably, step (3) specifically includes: inoculating the seed liquid that has been acclimatized and cultivated into the pretreated wastewater, and cultivating it in a closed photobioreactor with an inoculum volume fraction of 10%-20%, so that OD=0.2-0.3, the culture condition is pH=6.5-7.5, the light is 5000-6000 lux, the temperature is 23-26° C., and the culture is 9-12 days.
优选地,步骤(4)中采收小球藻所用絮凝剂为三氯化铁,藻液中三氯化铁终浓度为200-500mg/L、pH=6-7。Preferably, the flocculant used for harvesting the chlorella in step (4) is ferric chloride, and the final concentration of ferric chloride in the algae liquid is 200-500mg/L, pH=6-7.
本发明产生的有益效果为:采用在适应性较强的小球藻来净化猪场发酵废水,能较好的去除废水的TN、TP及COD,解决目前猪场发酵废水采用传统方法不够经济或者直接排放污染环境的问题;另外,收获的小球藻可作为其他用途,产生一定的经济效益。The beneficial effects produced by the present invention are as follows: the use of chlorella with strong adaptability to purify pig farm fermentation wastewater can better remove TN, TP and COD in wastewater, and solve the problem that traditional methods for pig farm fermentation wastewater are not economical or Directly discharge the problem of polluting the environment; in addition, the harvested chlorella can be used for other purposes and generate certain economic benefits.
具体实施方式detailed description
下面将结合本发明实施例对本发明的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The technical solutions of the present invention will be clearly and completely described below in conjunction with the embodiments of the present invention. Apparently, the described embodiments are only some of the embodiments of the present invention, not all of them. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.
实施例Example
(1)猪场发酵废水经固液分离后清液进曝气池曝气,曝气48h后进沉淀池,沉淀时间2h,上层清液进消毒池,用15g/m3强氯精消毒,16h后曝气30min,加入强氯精2.5倍质量的硫代硫酸钠中和,随后进入调节池调节PH为7并用自来水调节废水浓度。( 1 ) After solid-liquid separation, the fermented wastewater from the pig farm enters the aeration tank for aeration. After aeration for 48 hours, it enters the sedimentation tank. The sedimentation time is 2 hours. After aeration for 30 minutes, add sodium thiosulfate 2.5 times the mass of strong chlorine to neutralize, then enter the adjustment tank to adjust the pH to 7 and adjust the concentration of wastewater with tap water.
(2)上述处理后的猪场发酵废水从低浓度开始,依次在体积分数为20-100%的浓度的废水中驯化小球藻,小球藻置于恒温培养室中的摇床上培养,培养温度23-26℃,摇床转速180rmp/min,光照3000-4000lux,最终筛出能在浓度为50%-70%猪场发酵废水中能够快速生长的藻种。(2) The fermented wastewater from pig farms after the above-mentioned treatment starts from a low concentration, and domesticates Chlorella in the wastewater with a volume fraction of 20-100% successively. The temperature is 23-26°C, the rotation speed of the shaker is 180rmp/min, and the light is 3000-4000lux. Finally, the algae species that can grow rapidly in the fermented wastewater of pig farms with a concentration of 50%-70% are screened out.
(3)将驯化好并扩培的藻种种子液接种到预处理后的废水中,选取50%、60%、70%三个浓度,分别在密闭式光生物反应器中培养,接种量体积分数为废水的10%-20%,使OD=0.2-0.3,培养条件为PH=7、光照5000-6000lux,温度25℃,培养12天。(3) Inoculate the algae seed solution that has been domesticated and expanded into the pretreated waste water, select three concentrations of 50%, 60%, and 70%, and cultivate them in a closed photobioreactor respectively. The fraction is 10%-20% of the waste water, so that OD=0.2-0.3, the culture conditions are PH=7, light of 5000-6000 lux, temperature 25°C, and culture for 12 days.
(4)培养一个周期后,采收小球藻,所用絮凝剂为三氯化铁,藻液中三氯化铁终浓度为200-500mg/L,PH=6,2h后,小球藻的沉降率可达95%以上,上层清液排出收集完成废水处理;采收小球藻后,取絮凝后的上清测COD、TN、TP等指标数值。(4) After cultivating for one cycle, harvest Chlorella, the flocculant used is ferric chloride, and the final concentration of Ferric chloride in the algae liquid is 200-500mg/L, PH=6, after 2h, the chlorella The sedimentation rate can reach more than 95%, and the supernatant is discharged and collected to complete the wastewater treatment; after the chlorella is harvested, the supernatant after flocculation is taken to measure the COD, TN, TP and other index values.
猪场发酵废水经过上述步骤处理后,发现60%的废水能达到最好的净化效果,且处理结果如表1所示,处理后最终各污染指标均能达到畜禽养殖废水排放标准。After the pig farm fermentation wastewater was treated through the above steps, it was found that 60% of the wastewater could achieve the best purification effect, and the treatment results are shown in Table 1. After treatment, the final pollution indicators could meet the livestock and poultry breeding wastewater discharge standards.
表1:猪场发酵废水处理前后污染指标Table 1: Pollution indicators before and after treatment of fermented wastewater from pig farms
以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the scope of the present invention. within the scope of protection.
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| CN107629961A (en) * | 2017-10-16 | 2018-01-26 | 韶关学院 | A kind of method using breeding wastewater culture microalgae |
| CN107686815A (en) * | 2017-10-17 | 2018-02-13 | 中国水产科学研究院渔业机械仪器研究所 | A kind of method that chlorella is cultivated using food garbage |
| CN107827328A (en) * | 2017-12-14 | 2018-03-23 | 陈英 | A process for repairing aquaculture wastewater |
| CN108865892A (en) * | 2018-05-29 | 2018-11-23 | 深圳文科园林股份有限公司 | A method of utilizing livestock breeding biogas slurry high yield microalgae |
| CN109502914A (en) * | 2018-12-24 | 2019-03-22 | 江西洁地环境治理生态科技有限公司 | A kind of sewage disposal system using chlorella processing biogas slurry |
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| CN113045133A (en) * | 2021-03-24 | 2021-06-29 | 重庆大学 | System and method for treating livestock and poultry breeding wastewater by anaerobic fermentation coupled with microalgae organisms |
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Cited By (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107629961A (en) * | 2017-10-16 | 2018-01-26 | 韶关学院 | A kind of method using breeding wastewater culture microalgae |
| CN107686815A (en) * | 2017-10-17 | 2018-02-13 | 中国水产科学研究院渔业机械仪器研究所 | A kind of method that chlorella is cultivated using food garbage |
| CN107827328A (en) * | 2017-12-14 | 2018-03-23 | 陈英 | A process for repairing aquaculture wastewater |
| CN108865892A (en) * | 2018-05-29 | 2018-11-23 | 深圳文科园林股份有限公司 | A method of utilizing livestock breeding biogas slurry high yield microalgae |
| CN109502914B (en) * | 2018-12-24 | 2023-10-31 | 江西洁地环境治理生态科技有限公司 | Sewage treatment system for treating biogas slurry by using chlorella |
| CN109502914A (en) * | 2018-12-24 | 2019-03-22 | 江西洁地环境治理生态科技有限公司 | A kind of sewage disposal system using chlorella processing biogas slurry |
| CN110894467A (en) * | 2019-11-12 | 2020-03-20 | 湖南工业大学 | Method for culturing chlorella by using starch processing wastewater anaerobic fermentation liquid |
| CN111635080A (en) * | 2020-06-30 | 2020-09-08 | 福州科力恩生物科技有限公司 | Sewage treatment system and application thereof in purification of breeding sewage and black and odorous water |
| CN112551700A (en) * | 2020-11-25 | 2021-03-26 | 武汉市农业科学院 | Method for purifying biogas slurry by using microalgae |
| CN112551700B (en) * | 2020-11-25 | 2024-02-13 | 武汉市农业科学院 | Method for purifying biogas slurry by utilizing microalgae |
| CN113045133A (en) * | 2021-03-24 | 2021-06-29 | 重庆大学 | System and method for treating livestock and poultry breeding wastewater by anaerobic fermentation coupled with microalgae organisms |
| CN113717854A (en) * | 2021-09-01 | 2021-11-30 | 东北农业大学 | Oil-producing chlorella ZM-5 and application thereof |
| CN113717854B (en) * | 2021-09-01 | 2023-05-02 | 东北农业大学 | Chlorella oleaginous ZM-5 and application thereof |
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