MX2019000176A - Metodo y aparato para la eliminacion de nutrientes con adicion de carbono. - Google Patents

Metodo y aparato para la eliminacion de nutrientes con adicion de carbono.

Info

Publication number
MX2019000176A
MX2019000176A MX2019000176A MX2019000176A MX2019000176A MX 2019000176 A MX2019000176 A MX 2019000176A MX 2019000176 A MX2019000176 A MX 2019000176A MX 2019000176 A MX2019000176 A MX 2019000176A MX 2019000176 A MX2019000176 A MX 2019000176A
Authority
MX
Mexico
Prior art keywords
anammox
electron donor
nitrite
nitrate
reactions
Prior art date
Application number
MX2019000176A
Other languages
English (en)
Inventor
Wett Bernhard
B Bott Charles
N Murthy Sudhir
De Clippeleir Haydee
Debarbadillo Christine
KLAUS Stephanie
Original Assignee
N Murthy Sudhir
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by N Murthy Sudhir filed Critical N Murthy Sudhir
Publication of MX2019000176A publication Critical patent/MX2019000176A/es

Links

Classifications

    • 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
    • C02F3/302—Nitrification and denitrification treatment
    • C02F3/305—Nitrification and denitrification treatment characterised by the denitrification
    • 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
    • C02F3/28—Anaerobic digestion processes
    • C02F3/286—Anaerobic digestion processes including two or more steps
    • 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
    • C02F3/006—Regulation methods for biological treatment
    • 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
    • C02F3/302—Nitrification and denitrification treatment
    • C02F3/307—Nitrification and denitrification treatment characterised by direct conversion of nitrite to molecular nitrogen, e.g. by using the Anammox process
    • 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
    • C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/10—Inorganic compounds
    • C02F2101/16—Nitrogen compounds, e.g. ammonia
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/10—Inorganic compounds
    • C02F2101/16—Nitrogen compounds, e.g. ammonia
    • C02F2101/163—Nitrates
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/10—Inorganic compounds
    • C02F2101/16—Nitrogen compounds, e.g. ammonia
    • C02F2101/166—Nitrites
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/005—Processes using a programmable logic controller [PLC]
    • C02F2209/006—Processes using a programmable logic controller [PLC] comprising a software program or a logic diagram
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/08—Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/14—NH3-N
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/15—N03-N
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/16—Total nitrogen (tkN-N)
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/40—Liquid flow rate
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00—Controlling or monitoring parameters in water treatment
    • C02F2209/44—Time
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00—Use of specific compounds during water treatment
    • C02F2305/06—Nutrients for stimulating the growth of microorganisms
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00—Technologies for the production of fuel of non-fossil origin
    • Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • 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)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

Esta descripción se refiere a la eliminación de nitrógeno con la adición de carbono, incluyendo para el tratamiento de aguas residuales. La reacción de desnitrificación puede ser terminada en un producto de nitrito intermediario, el cual se suministra a la reacción de anammox. El nitrógeno se puede eliminar a través del uso de una fuente de donador de electrones que incluye, pero no se limita a, acetato o glicerol en una zona específica. El donador de electrones se puede utilizar para convertir nitrato a nitrito a través de una dosificación apropiada, SRT anóxico y/o mantenimiento de nitrato residual en aislamiento o en combinación. También se propone el suministro subsecuente de nitrito y amoniaco para las reacciones de anammox. El desarrollo más lento del anammox puede ser selectivamente retenido sobre medios o utilizando otros aspectos físicos. El intento total de la presente descripción es reducir al mínimo el uso de un donador de electrones al incrementar al máximo la desnitración y reacciones de anammox. Se proporcionan resultados de prueba para la retención selectiva de anammox en la biopelicula, granulado o sistema de crecimiento suspendido o control de nitrato residual.
MX2019000176A 2016-07-08 2017-06-22 Metodo y aparato para la eliminacion de nutrientes con adicion de carbono. MX2019000176A (es)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US201662359950P 2016-07-08 2016-07-08
PCT/US2017/038826 WO2018009348A1 (en) 2016-07-08 2017-06-22 Method and apparatus for nutrient removal with carbon addition

Publications (1)

Publication Number Publication Date
MX2019000176A true MX2019000176A (es) 2019-12-05

Family

ID=60893077

Family Applications (1)

Application Number Title Priority Date Filing Date
MX2019000176A MX2019000176A (es) 2016-07-08 2017-06-22 Metodo y aparato para la eliminacion de nutrientes con adicion de carbono.

Country Status (6)

Country Link
US (1) US20180009687A1 (es)
EP (1) EP3481779A4 (es)
CN (2) CN116282514A (es)
AU (1) AU2017292627B2 (es)
MX (1) MX2019000176A (es)
WO (1) WO2018009348A1 (es)

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CN108529747B (zh) * 2018-04-25 2021-09-17 浙江工业大学膜分离与水处理协同创新中心湖州研究院 硝化反硝化同步脱氮方法
JP7153135B2 (ja) * 2018-10-12 2022-10-13 ヴェオリア・ウォーター・ソリューションズ・アンド・テクノロジーズ・サポート バイパスの一次排水およびステップ供給を使用したメインストリームの脱アンモニアプロセス
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CN109485157A (zh) * 2018-11-26 2019-03-19 四川山水源环保技术有限公司 一种用于污水脱氮的复合碳源及其制备方法和使用方法
CN109761453A (zh) * 2019-03-20 2019-05-17 哈尔滨工业大学（威海） 利用海洋厌氧氨氧化菌通过反硝化氨氧化途径处理海水养殖废水的方法
CN110451721B (zh) * 2019-08-08 2021-03-26 同济大学 一种垃圾焚烧厂渗滤液除碳脱氮处理装置及方法
CN110510738B (zh) * 2019-08-12 2022-02-01 欧基（上海）环保科技有限公司 一种有氧脱氮除磷强化污水处理***及方法
CN110627320B (zh) * 2019-09-26 2022-01-28 北京工业大学 基于物理-化学-生物法的废水处理组合装置及工艺
CN110632067B (zh) * 2019-10-29 2021-12-24 中国计量大学 基于机器视觉的水体溶解氧检测方法
EP4090634A1 (de) * 2020-01-17 2022-11-23 Bluetector AG Verfahren und system zur biologischen behandlung von hochkonzentriertem abwasser
EP3851418A1 (de) * 2020-01-17 2021-07-21 Bluetector AG Verfahren und system zur biologischen behandlung von hochkonzentriertem abwasser
CN111547853B (zh) * 2020-05-22 2021-02-02 广西春晖环保工程有限责任公司 一种双短程硝化-厌氧氨氧化的脱氮工艺
CN111661924A (zh) * 2020-07-14 2020-09-15 北京城市排水集团有限责任公司 一种硫自养短程反硝化耦合厌氧氨氧化脱氮的***及方法
CN112851026B (zh) * 2021-01-07 2022-08-23 上海碧州环保能源科技有限公司 高浓度难降解有机废水***及其处理工艺
US20220289606A1 (en) 2021-03-12 2022-09-15 Hampton Roads Sanitation District Method and apparatus for nutrient removal using anoxic biofilms
CN117337271A (zh) 2021-03-12 2024-01-02 汉普顿道路卫生局 废水处理中多重除选的方法和装置
FR3121137A1 (fr) 2021-03-25 2022-09-30 Veolia Water Solutions & Technologies Support Procédé de filtration biologique aérée pour le traitement des eaux en vue d’en abattre la teneur en azote (NGL) avec réduction des besoins en source carbonée et en aération
CN113387529B (zh) * 2021-04-08 2023-01-24 北京工业大学 高效污泥减量同步碳氮脱除装置及基于装置的处理方法
CN113307448B (zh) * 2021-05-24 2022-12-06 东华大学 一种零价铁自养反硝化耦合生物炭prb地下水脱氮方法及反应器
CN113248025B (zh) * 2021-05-31 2021-11-23 大唐融合通信股份有限公司 一种农村生活污水处理的控制方法、云端服务器及***
CN113200604A (zh) * 2021-06-07 2021-08-03 浙江大学 基于固态碳源短程反硝化-厌氧氨氧化的脱氮装置及方法
CN113562845A (zh) * 2021-07-29 2021-10-29 汕尾粤海环保有限公司 一种适用于活性污泥法的反硝化强化装置
CN113845222B (zh) * 2021-10-03 2023-06-02 北京工业大学 一种两次排水内源短程反硝化/厌氧氨氧化两段式工艺实现生活污水深度脱氮的装置和方法
CN114804514B (zh) * 2022-04-12 2023-08-11 北京大学 一种与铁絮凝过程耦合的生物脱氮方法
CN114906929B (zh) * 2022-06-13 2023-03-14 海南大学 一种实现发酵型内碳源短程反硝化的装置与方法
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Also Published As

Publication number Publication date
US20180009687A1 (en) 2018-01-11
CN109996766A (zh) 2019-07-09
AU2017292627B2 (en) 2023-03-23
WO2018009348A1 (en) 2018-01-11
AU2017292627A1 (en) 2019-02-07
EP3481779A4 (en) 2020-01-15
CN116282514A (zh) 2023-06-23
CN109996766B (zh) 2022-11-22
EP3481779A1 (en) 2019-05-15

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