WO2022142950A1 - 一种用于生化法处理炼化废水的活性污泥调节剂 - Google Patents

一种用于生化法处理炼化废水的活性污泥调节剂 Download PDF

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WO2022142950A1
WO2022142950A1 PCT/CN2021/134147 CN2021134147W WO2022142950A1 WO 2022142950 A1 WO2022142950 A1 WO 2022142950A1 CN 2021134147 W CN2021134147 W CN 2021134147W WO 2022142950 A1 WO2022142950 A1 WO 2022142950A1
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refining
activated sludge
biochemical treatment
chemical wastewater
carbon
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PCT/CN2021/134147
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English (en)
French (fr)
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郝润秋
张成凯
李亮
滕厚开
付春明
郝亚超
肖彩英
刘祺
李亚宁
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中海油天津化工研究设计院有限公司
中国海洋石油集团有限公司
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Publication of WO2022142950A1 publication Critical patent/WO2022142950A1/zh

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/341Consortia of bacteria
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • C02F2103/365Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/06Nutrients for stimulating the growth of microorganisms

Definitions

  • the invention relates to the technical field of refining and chemical wastewater treatment, in particular to an activated sludge regulator for biochemical treatment of wastewater in refining and chemical enterprises.
  • Refinery wastewater is mainly produced from electrical desalination, catalytic cracking, atmospheric and vacuum, desulfurization, cooling systems, boilers and other devices.
  • the composition of wastewater is complex, with many types of pollutants, high concentrations and large changes.
  • the pollutants mainly include oil, sulfide, volatile phenol, NH4 + -N and other toxic substances, which have strong harm and impact on the biochemical system, resulting in the decline of biochemical efficiency and the decline of drainage water quality.
  • the biological enhancement technology is selected in a targeted manner to improve the impact resistance and stability of the biochemical system, and improve the efficiency of the sewage treatment process. Guaranteed water quality.
  • the purpose of the present invention is to provide an environment-friendly agent suitable for controlling the sedimentation ratio of activated sludge, inhibiting the expansion of filamentous bacteria, and improving the biological activity of activated sludge and the impact resistance of the system, which is suitable for the biochemical treatment of refining wastewater.
  • the present invention is achieved through the following technical solutions.
  • an activated sludge conditioner for biochemical treatment of refining and chemical wastewater is composed of the following components mixed according to mass percentage: carbon source 20-40%, disodium hydrogen phosphate 10-15%, bentonite 0.05%-3%, nitrogen source 2%-5%, activated carbon 1%-3%, polyglutamic acid 0.001-0.2%, microbial antidote 0.5%-5%, inorganic salt 3%-10%, salt content quality
  • the carbon source is glucose, fructose, sucrose, acetic acid or propionic acid.
  • the nitrogen source is urea, ammonium chloride or ammonium sulfate.
  • the activated carbon is powder activated.
  • the present invention supplements the nutrients necessary for microorganisms such as carbon source and nitrogen source phosphate by adding antidote, activated carbon, bentonite, trace elements and environmentally friendly polyglutamic acid, etc.
  • Antidote is also introduced, which reduces the inhibition of toxic substances, increases the density of activated sludge by introducing bentonite and activated carbon, and provides attachments for bacteria micelles to provide an environment for the competition between bacteria micelles and filamentous bacteria Advantages, control the expansion of filamentous bacteria. At the same time inhibit the expansion of non-filamentous bacteria. It shortens the time of activated sludge cultivation and domestication during the biochemical treatment of refining wastewater, improves the total amount of beneficial bacteria in the domesticated sludge and the stability of the treatment system.
  • the activated sludge regulator for biochemical treatment of the present invention is based on the actual indicators of refining and chemical wastewater, and has a targeted configuration for the biochemical treatment mechanism of sewage and the activated sludge bulking mechanism. If other agents want to achieve this function, they need to be added separately.
  • a variety of drugs, high cost, drug dosage is not easy to control and calculate. The medicament is easy to use, the dosage is precisely controllable, and the relative use cost is low.
  • Test method A refinery sewage plant adopts the activated sludge treatment process. After configuring the activated sludge regulator in the present invention according to the implementation case 1, the implementation case 2 and the implementation case 3, it is put into the system at 50 mg/L for a period of operation. After time, the test results are shown in Table 1, Table 2 and Table 3:
  • the COD removal rate is increased by at least 30 percentage points, and the sludge settling performance is increased by more than 50%.
  • the settling performance of activated sludge is improved, sludge bulking is inhibited, and the total amount of beneficial bacteria is increased.

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  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Activated Sludge Processes (AREA)

Abstract

一种生化法处理炼化废水用活性污泥调节剂,由以下质量百分含量的组分构成:碳源20~40%、磷酸氢二钠10~15%、膨润土0.05%~3%、氮源2%~5%、活性炭1%-3%,聚谷氨酸0.001~0.2%,微生物解毒剂0.5%-5%、无机盐3~10%,其中无机盐含量质量比为K:Ca:Mg:Fe:Zn:Cu=21.25~30.14:30~45:2~5:2~7:5~10:4~10,其余为水。

Description

一种用于生化法处理炼化废水的活性污泥调节剂 技术领域
本发明涉及炼化废水处理技术领域,具体为炼化企业废水生化处理用活性污泥调节剂。
背景技术
据统计,我国2017年工业废水排放总量约为690亿吨,其中高盐废水占比5%,且每年以2%的速度增长,我国水污染防治所面临的严峻形势。
炼化废水主要由来自电脱盐、催化裂化、常减压、脱硫、冷却***、锅炉等装置。废水成分复杂,污染物的种类多,浓度高、变化大。污染物主要有油类、硫化物、挥发酚、NH4 +-N以及其他有毒物质,对生化***有强烈的危害及冲击性,导致生化效率下降,排水水质下降。
在生化***受到冲击,污泥沉降性能变差,生化效率下降的情况下,有针对性的选用生物增效技术,提高生化***抗冲击性及稳定性,提高污水处理工序的效率,为进一步提高出水质量提供保障。
发明内容
本发明的目的在于:提供一种适用于炼化废水生化处理过程的控制活性污泥沉降比例,抑制丝状菌膨胀,提高活性污泥生物活性及***抗冲击性能的环境友好型药剂。
本发明通过以下技术方案予以实现。
一种用于生化法处理炼化废水的活性污泥调节剂,该活性污泥调节剂由下列组分按照质量百分比混合组成:碳源20~40%、磷酸氢二钠10~15%、膨润土0.05%~3%、氮源2%~5%、活性炭1%-3%、聚谷氨酸0.001~0.2%,微生物解毒剂0.5%-5%、无机盐3%~10%,盐含量质量比为K:Ca:Mg:Fe:Zn:Cu=21.25~30.14:30~45:2~5:2~7:5~10:4~10:0.2~0.5,其余为水。
所述的碳源为葡萄糖、果糖、蔗糖、乙酸或丙酸。
所述的氮源为尿素、氯化铵或硫酸铵。
所述的活性炭为粉末活性。
本发明的有益效果:本发明在补充碳源和氮源磷酸盐等微生物必须的营养的基础上通过添加解毒剂、活性炭、膨润土及微量元素及对环境友好的聚谷氨酸等,该调节剂还引入解毒剂,降低了有毒物质的抑制性,通过引入膨润土及活性炭增加了活性污泥的密度及为菌胶团菌提供了附着物为菌胶团菌与丝状菌的竞争中提供了环境优势,控制了丝状菌膨胀。同时抑制非丝状菌膨胀。缩短炼化污水生化处理过程中活性污泥培养与驯化的时间,提高驯化污泥中有益菌的总量及处理***的稳定性。
本发明的生化处理用活性污泥调节剂以炼化废水的实际指标为基础,针对污水生化处理机理及活性污泥膨胀机理,有针对性的配置,若其他药剂要实现此功能,需要分别添加多种药剂,成本高、药剂投加不容易控制和计算。本药剂使用简单,投加量根据精确可控,相对使用成本低。
具体实施方式
实施例1:一种用于生化法处理炼化废水的活性污泥调节剂,由下列组分按照质量百分比混合组成:葡萄糖35%、磷酸氢二钠10%、尿素5%、膨润1%、硫酸铵5%、粉末活性炭1%、聚谷氨酸0.01%、微生物解毒剂0.5%、无机盐5%,盐含量质量比为K:Ca:Mg:Fe:Zn:Cu:=21:32:2.6:3.3:5.5:4,其余为蒸馏水。
实施例2:一种用于生化法处理炼化废水的活性污泥调节剂,由下列组分按照质量百分比混合组成:葡萄糖40%、磷酸氢二钠15%、尿素2%、膨润土0.2%、硫酸铵2%、粉末活性炭1.2%,聚谷氨酸0.01%,微生物解毒剂0.8%、无机盐10%,盐含量质量比为K:Ca:Mg:Fe:Zn:Cu=25:30:2:3.1:2.5:5.5,其余为蒸馏水。
实施例3:一种用于生化法处理炼化废水的活性污泥调节剂,由下列组分按照质量百分比混合组成:葡萄糖30%、磷酸氢二钠12%、尿素4%、膨润土0.05%、硫酸铵2%、微生物解毒剂1%、无机盐3%,盐含量质量比为K:Ca:Mg:Fe:Zn:Cu=25:35:3:3:6:4,其余为蒸馏水。
试验方法:某炼化污水厂采用活性污泥法处理工艺,将本发明中的活性污泥调节剂按实施案例1、实施案例2、实施案例3进行配置后,按50mg/L投入***运行一段时间后,试验结果见表1、表2和表3:
表1驯化10天前后实验结果
驯化方式 空白 实施案例1 实施案例2 实施案例3
有益菌总量(亿个/g) 0.75 1.35 1.33 1.36
SV30(%) 70 28 26 29
COD去除率(%) 45 83 81 86
表2驯化20天前后实验结果
驯化方式 空白 实施案例1 实施案例2 实施案例3
有益菌总量(亿个/g) 0.85 1.78 1.75 1.82
SV30(%) 89 35 33 37
COD去除率(%) 45 91 90 93
表3驯化30天前后实验结果
驯化方式 空白 实施案例1 实施案例2 实施案例3
有益菌总量(亿个/g) 0.88 1.86 1.85 1.88
SV30(%) 64 38 37 39
COD去除率(%) 61 93 91 94
从上述对比试验结果看,在同样的驯化期内,投加本发明中的活性污泥调节剂后COD去除率提高至少30个百分点,污泥沉降性能提高50%以上。尤其对活性污泥沉降性能差,微生物活性差,进水有一定生物毒性或者抑制性的炼化及化工废水效果显著,同时反应***的酸度也较为稳定。大大增强了炼化废水生化处理***的处理效果。从数据看,提高了活性污泥沉降性能,抑制了污泥膨胀,同时提高了有益菌总量。

Claims (4)

  1. 一种生化法处理炼化废水用活性污泥调节剂,其特征在于,由以下质量百分含量的组分构成:碳源20~40%、磷酸氢二钠10~15%、膨润土0.05%~3%、氮源2%~5%、活性炭1%-3%,聚谷氨酸0.001~0.2%,微生物解毒剂0.5%-5%、无机盐3~10%,其中无机盐含量质量比为K:Ca:Mg:Fe:Zn:Cu:Ni:B:Mo=21.25~30.14:30~45:2~5:2~7:5~10:4~10其余为水。
  2. 根据权利要求1所述的生化法处理炼化废水用活性污泥调节剂,其特征在于,所述的碳源为葡萄糖、果糖、蔗糖、乙酸或丙酸。
  3. 根据权利要求1所述的生化法处理炼化废水用活性污泥调节剂,其特征在于,所述的氮源为尿素、氯化铵或硫酸铵。
  4. 根据权利要求1所述的生化法处理炼化废水用活性污泥调节剂,其特征在于,所述的活性炭为粉末活性炭。
PCT/CN2021/134147 2020-12-29 2021-11-29 一种用于生化法处理炼化废水的活性污泥调节剂 WO2022142950A1 (zh)

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Publication number Priority date Publication date Assignee Title
CN112607872A (zh) * 2020-12-29 2021-04-06 中海油天津化工研究设计院有限公司 一种用于生化法处理炼化废水的活性污泥调节剂

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1597569A (zh) * 2003-09-15 2005-03-23 中国石油化工股份有限公司 一种高温废水生化处理的微生物的培养方法
US20140305868A1 (en) * 2013-04-10 2014-10-16 Ya-Chung Wei Process of stabilizing activated sludge in wastewater treatment
CN104355403A (zh) * 2014-11-27 2015-02-18 新疆环境工程技术有限责任公司 一种用于化工废水处理的活性污泥培养驯化方法
CN104649405A (zh) * 2015-03-20 2015-05-27 中蓝连海设计研究院 一种含盐高温废水生化处理的活性污泥培养方法
CN104743658A (zh) * 2015-03-12 2015-07-01 山东省环科院环境科技有限公司 一种废水生化处理活性污泥调理剂及其制备方法
CN106336018A (zh) * 2016-08-30 2017-01-18 中蓝连海设计研究院 一种改善污泥活性的微生物生长促进剂及方法
CN112607872A (zh) * 2020-12-29 2021-04-06 中海油天津化工研究设计院有限公司 一种用于生化法处理炼化废水的活性污泥调节剂

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4765908A (en) * 1985-02-04 1988-08-23 Barbara Monick Process and composition for removing contaminants from wastewater
CN103910475B (zh) * 2013-12-30 2015-12-02 新疆环境工程技术有限责任公司 一种耐盐活性污泥驯化的方法
CN107344751B (zh) * 2017-07-14 2020-12-01 河海大学 一种耐烟碱的厌氧活性污泥驯化方法
CN109052663B (zh) * 2018-08-27 2020-08-28 华东理工大学 一种耐盐除碳微生物颗粒材料快速培育方法

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1597569A (zh) * 2003-09-15 2005-03-23 中国石油化工股份有限公司 一种高温废水生化处理的微生物的培养方法
US20140305868A1 (en) * 2013-04-10 2014-10-16 Ya-Chung Wei Process of stabilizing activated sludge in wastewater treatment
CN104355403A (zh) * 2014-11-27 2015-02-18 新疆环境工程技术有限责任公司 一种用于化工废水处理的活性污泥培养驯化方法
CN104743658A (zh) * 2015-03-12 2015-07-01 山东省环科院环境科技有限公司 一种废水生化处理活性污泥调理剂及其制备方法
CN104649405A (zh) * 2015-03-20 2015-05-27 中蓝连海设计研究院 一种含盐高温废水生化处理的活性污泥培养方法
CN106336018A (zh) * 2016-08-30 2017-01-18 中蓝连海设计研究院 一种改善污泥活性的微生物生长促进剂及方法
CN112607872A (zh) * 2020-12-29 2021-04-06 中海油天津化工研究设计院有限公司 一种用于生化法处理炼化废水的活性污泥调节剂

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