CN107759017A - 一种粪污处理工艺 - Google Patents
一种粪污处理工艺 Download PDFInfo
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- CN107759017A CN107759017A CN201711065308.4A CN201711065308A CN107759017A CN 107759017 A CN107759017 A CN 107759017A CN 201711065308 A CN201711065308 A CN 201711065308A CN 107759017 A CN107759017 A CN 107759017A
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- 238000000034 method Methods 0.000 title claims abstract description 22
- 241000283690 Bos taurus Species 0.000 title claims abstract description 21
- 239000007788 liquid Substances 0.000 claims abstract description 38
- 235000016693 dipotassium tartrate Nutrition 0.000 claims abstract description 27
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- 230000000694 effects Effects 0.000 description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group 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Classifications
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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
- C02F9/00—Multistage treatment of water, waste water, or sewage
-
- 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
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/10—Energy recovery
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
Abstract
本发明涉及一种污染物的处理方法,具体涉及一种养殖场粪便处理的工艺方法。本发明所述的一种粪污处理工艺,粪污包括干粪和粪水,干粪进行堆肥发酵制成生物肥,粪水依次经过一级沉淀池进行沉淀和水解酸化,再将上清液依次转移至厌氧池、好氧池和二级沉淀池中进行处理,收集干粪堆肥、一级沉淀池和好氧池中的臭气并将所述臭气通入二级沉淀池中后再排出,收集厌氧池中的气体处理后做生活用能;最后再将二级沉淀池中的上清转移至储液池,调节储液池中的营养比例将其制成液态生物肥。本发明所提供的粪污处理工艺,降低了粪污处理过程中的环境污染问题,有效的利用了粪污在处理过程中产生的臭气中的养分,增加了经济效益。
Description
一种粪污处理工艺
技术领域
[0001] 本发明涉及一种污染物的处理方法,具体涉及一种养殖场粪便处理的工艺方法。
背景技术
[0002] 规模化养殖是目前城镇肉食的主要来源,然而因养殖产生的大量牲畜粪便却给环 境带来了严重的困扰,大量的猪粪尿液若处理不当,一是影响水质,由于猪粪尿中含有大量 的有机物、生物,分解时消耗水中溶氧,进而造成生态平衡;二是会妨害环境卫生,滋生蚊 蝇,影响临近社区的居住环境品质;三是会造成疾病传播,猪粪尿中往往夹杂大量的致病 菌,若未处理而直接引用于农作物灌溉或径直排入河流,则存在极大的疾病传播隐患。目前 在对粪污进行处理的过程中常常将含氮等较低的冲洗水和含氮等较高的尿液进行混合处 理,产生的污水较多,增大后期的处理成本;有关资料表明,养猪场NH3的平均排放量为 4 • 35g/ (m2 • d),且排放量随处置方式改变而改变,猪粪在不结皮的情况下排放强度更高。粪 污在处理的过程中往往会产生臭气,臭气一般是细菌作用产生的NH3、H2S等,臭气在扩散的 同时,一方面造成环境的污染,另一方面液造成氮氧分的大量损失。
发明内容
[0003] 针对现有技术中的粪污在处理过程中存在的弊端,本发明的目的在于提供一种新 的粪污处理模式,该粪污处理方式一方面节约了用水,减少了污水的排放,另一方面减少了 粪污处理后养分的损失,同时减少了臭气的排放和环境的污染。
[0004] 本发明通过以下技术方案来实现上述技术目的: 本发明提供的一种粪污处理工艺,所述粪污包括干粪和粪水,所述干粪进行堆肥发酵 制成生物肥,所述粪水依次经过一级沉淀池进行沉淀和水解酸化,再将上清液依次转移至 厌氧池、好氧池和二级沉淀池中进行处理,收集干粪堆肥、一级沉淀池和好氧池中的臭气并 将所述臭气通入二级沉淀池中后再排出,收集厌氧池中的气体处理后做生活用能;最后再 将二级沉淀池中的上清转移至储液池,调节储液池中的营养比例将其制成液态生物肥。
[0005] 优选地,所述粪水包括尿液和浓缩后的冲洗污水。
[0006] 其中,所述冲洗污水经过浓缩后,浓缩出的液体经过消毒处理后用于清洗猪舍。
[0007] 优选地,采用离心装置分别对一级沉淀池、厌氧池和二级沉淀池中的沉淀物进行 离心,离心后的固体粪便和干粪混合后进行堆肥发酵,液体转入好氧池中进行重复利用。
[0008] 优选地,所述干粪堆肥、一级沉淀池和好氧池均为密封结构,好氧池中通过不断的 充入空气提供氧气。
[0009] 具体地,所述干粪堆肥、一级沉淀池和好氧池上设置有空气管道,所述干粪堆肥、 一级沉淀池上的空气管道深入二级沉淀池底部,所述好氧池中的空气管道深入二级沉淀池 的中部。
[0010] 本发明所提供的粪污处理工艺,减少了常规粪污处理中臭气的排放量,节约了用 水,也减少了污水的排放,同时该处理工艺有效的利用了粪污在处理过程中产生的臭气中 的养分,减少了粪污处理中养分的损失和臭气的排放,降低了粪污处理过程中的环境污染 问题,增加了经济效益。
具体实施方式
[0011] 下面结合具体实施例对本发明进行进一步的说明: 实施例1 一种粪污处理工艺,首先将粪污进行分离分为干粪和粪水,干粪进行堆肥发酵制成生 物肥,粪水依次经过一级沉淀池进行沉淀和水解酸化,再将上清液依次转移至厌氧池、好氧 池和二级沉淀池中进行处理,收集干粪堆肥、一级沉淀池和好氧池中的臭气并将收集到的 臭气通入二级沉淀池中后再排出,收集厌氧池中的气体处理后做生活用能;最后再将二级 沉淀池中的上清转移至储液池,调节储液池中的营养比例将其制成液态生物肥。
[0012] 本发明中将干粪直接进行堆肥发酵制成生物有机肥,粪水经过一级沉淀池进行沉 淀分离并在一级沉淀池中进行水解酸化,使其中的部分大分子降解为小分子,同时使其满 足厌氧发酵的工艺要求;之后将一级沉淀池中的上清转移至厌氧池中进行厌氧发酵处理, 厌氧发酵过程中产生的气体即沼气经过处理后做生活用能,厌氧发酵时粪污中的虫卵不断 下沉,病原体逐渐死亡,粪污得到进一步的无害化处理;再将厌氧池中的上清转移至好氧池 中,好氧池中不断的鼓气用于提供氧气,经过好氧处理后,粪污得到进一步的无害化处理, 最后再将好氧池中的上清转移至二级沉淀池中;在干粪堆肥发酵、粪污在一级沉淀池和好 氧池中进行处理的过程中,会不断的散发出臭气,收集该臭气,并将该臭气通入二级沉淀池 中,臭气中的N H3等溶于二级沉淀池的液体中,一方面对臭气进行了处理,减少了粪污所 散发出的臭气,另一方面减少了粪污处理过程中的营养损失,将二级沉淀池中的上清液转 移至储液池中进行营养的调节后制成液态生物肥,增加了经济效益,同时解决了现有的模 式中植物蔬菜基地处理粪污具有季节性的问题。
[0013] 实施例2 本实施例与实施例1基本相同,其区别在于,粪水包括尿液和浓缩后的冲洗污水。因冲 洗污水中养分含量较低,在本实施例中,我们将冲洗污水进行了浓缩,浓缩后浓缩液和养分 含量较高的尿液混合,提高了整个设备粪污的处理能力。
[0014] 实施例3 本实施例与上述实施例基本相同,其区别在于,冲洗污水经过浓缩处理后,浓缩出的液 体经过消毒处理后用于清洗猪舍,节约了用水,消毒优选为高温消毒的方式进行,彻底的杀 死其中的病原微生物等。
[0015] 实施例4 本实施例与上述实施例基本相同,其区别在于,采用离心装置分别对一级沉淀池、厌氧 池和二级沉淀池中的沉淀物进行离心,离心后的固体粪便和干粪混合后进行堆肥发酵,液 体转入好氧池中进行重复利用,有效的减少了污染物的产生,将有养分的粪液进行了充分 的利用。
[0016] 实施例5 本实施例与上述实施例基本相同,其区别在于,干粪在进行堆肥发酵的过程中、一级沉 淀池和好氧池均为密封的结构,好氧池中通过不断的充入空气提供氧气。
[0017]实施例6 本实施例与上述实施例基本相同,其区别在于,千粪堆肥发酵的容器、一级沉淀池和好 氧池上设置有空气管道,干粪堆肥、一级沉淀池上的空气管道深入二级沉淀池底部,好氧池 中的空气管道深入二级沉淀池的中部,这是因为干粪堆肥和一级沉淀中产生的臭气中N H 3等养分的含量较高,且整个气体的量较少,一方面不会对二级沉淀池的沉淀效果产生很 大的影响,另一方面可以保证臭气中的养分溶于粪液中;好氧池中进行处理的过程中因为 不断的通入空气,产生的气体较多,而粪液在进行过前面一系列的处理后能够产生的臭气 中的养分也较少,将该管道深入到二级沉淀池的中部,减少其对二级沉淀池沉淀效果的影 响,通过将臭气通入二级沉淀池中处理后的粪液中,还有效的减少处理过程中散发出的臭 气,减少对环境的污染。
[0018]以上所述仅为本发明的一些实施方式,对于本领域的技术人员来说,凡在本发明 的额精神和原则之内所做的任何改进和等同替换,均包含在本发明权利要求书的保护范围 之内。
Claims (6)
1. 一种粪污处理工艺,所述粪污包括干粪和粪水,所述干粪进行堆肥发酵制成生物肥, 所述粪水依次经过一级沉淀池进行沉淀和水解酸化,再将上清液依次转移至厌氧池、好氧 池和二级沉淀池中进行处理,其特征在于,收集干粪堆肥、一级沉淀池和好氧池中的臭气并 将所述臭气通入二级沉淀池中后再排出,收集厌氧池中的气体处理后做生活用能;最后再 将二级沉淀池中的上清转移至储液池,调节储液池中的营养比例将其制成液态生物肥。
2. 根据权利要求1所述的粪污处理工艺,其特征在于,所述粪水包括尿液和浓缩后的冲 洗污水。
3. 根据权利要求2所述的粪污处理工艺,其特征在于,所述冲洗污水经过浓缩后,浓缩 出的液体经过消毒处理后用于清洗猪舍。
4. 根据权利要求1所述的粪污处理工艺,其特征在于,采用离心装置分别对一级沉淀 池、厌氧池和二级沉淀池中的沉淀物进行离心,离心后的固体粪便和干粪混合后进行堆肥 发酵,液体转入好氧池中进行重复利用。
5. 根据权利要求1所述的粪污处理工艺,其特征在于,所述干粪堆肥、一级沉淀池和好 氧池均为密封结构,好氧池中通过不断的充入空气提供氧气。
6. 根据权利要求5所述的粪污处理工艺,其特征在于,所述干粪堆肥、一级沉淀池和好 氧池上设置有空气管道,所述干粪堆肥、一级沉淀池上的空气管道深入二级沉淀池底部,所 述好氧池中的空气管道深入二级沉淀池的中部。
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