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Method for deeply purifying landfill leachate

A landfill leachate and deep purification technology, applied in chemical instruments and methods, sedimentation treatment, water/sewage treatment, etc., can solve the problems of difficult and efficient treatment of discharge standards, inability to completely remove total nitrogen, and harsh reaction conditions, etc., to achieve improved Economic benefits, high value for large-scale promotion and application, and mild treatment conditions

Active Publication Date: 2020-06-16
云南兴滇实业有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

Currently common landfill leachate treatment methods include biochemical methods (anaerobic, aerobic treatment, etc.), physical methods (membrane treatment, adsorption, flocculation, etc.), chemical methods (redox, electrocatalysis, etc.) and land methods (recharge, Constructed wetlands, etc.), a single treatment method has major problems, and it is difficult to treat it efficiently and meet the emission standards required by the country
For example, biochemical methods are often inhibited because bacteria cannot adapt to the toxic substances in landfill leachate, oxidation methods cannot completely remove total nitrogen, and membrane treatment methods are too costly to treat
China Invention Patent Authorization Announcement No. CN 102701515B, CN 106348499B use electrochemical method to treat landfill leachate, China Invention Patent Authorization Announcement No. CN 106045058B, CN 102774926B use photocatalytic method to treat landfill leachate, China Invention Patent Authorization Announcement No. CN 104876363B8 uses high temperature The high-pressure catalytic wet oxidation method has achieved good results in the treatment of landfill leachate, but the reaction conditions of these methods are harsh, and electricity, light, or heating and pressure are required, and the process is relatively complicated.

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0027] This embodiment relates to a method for deep purification of landfill leachate, comprising the following steps:

[0028] Step 1. Transport 5L of landfill leachate wastewater to the coagulation sedimentation tank. The main parameters of the initial water quality range are as follows: COD Cr : 12785mg / L, total nitrogen: 898mg / L, chroma: 3800, suspended solids: 829mg / L. Add compound coagulation precipitant; compound coagulation precipitant is divided into A component and B component; Wherein A component is the mixed aqueous solution of basic ferric chloride and cement, the mass fraction of basic ferric chloride is 20 %, the mass fraction of cement is 2%; component B is a mixed aqueous solution of amphoteric polyacrylamide and sodium edetate, the mass fraction of amphoteric polyacrylamide is 0.2%, and the mass fraction of sodium edetate The fraction is 0.02%; add component A first, and its dosage is 1g / L; add B component after 20s, and its dosage is 1g / L. During the addit...

Embodiment 2

[0055] This embodiment relates to a method for deep purification of landfill leachate, comprising the following steps:

[0056] Step 1. Transport 5L of landfill leachate wastewater to the coagulation sedimentation tank. The main parameters of the initial water quality range are as follows: COD Cr : 19855mg / L, total nitrogen: 4654mg / L, chroma: 7800, suspended solids: 3697mg / L. Add compound coagulation precipitant; compound coagulation precipitant is divided into A component and B component; Wherein A component is the mixed aqueous solution of basic ferric chloride and cement, the mass fraction of basic ferric chloride is 35 %, the mass fraction of cement is 5%; component B is a mixed aqueous solution of amphoteric polyacrylamide and sodium edetate, the mass fraction of amphoteric polyacrylamide is 0.3%, and the mass fraction of sodium edetate The fraction is 0.05%; first add component A, the dosage is 2g / L, after 20s, add component B, the dosage is 1g / L. Mix and stir continuo...

Embodiment 3

[0065] This embodiment relates to a method for deep purification of landfill leachate, comprising the following steps:

[0066] Step 1. Transport 5L of landfill leachate wastewater to the coagulation sedimentation tank. The main parameters of the initial water quality range are as follows: COD Cr : 1058mg / L, total nitrogen: 114mg / L, color: 200, suspended solids: 121mg / L. Add compound coagulation precipitant; compound coagulation precipitant is divided into A component and B component; Wherein A component is the mixed aqueous solution of basic ferric chloride and cement, the mass fraction of basic ferric chloride is 10 %, the mass fraction of cement is 1%; component B is a mixed aqueous solution of non-ionic polyacrylamide and sodium edetate, the mass fraction of non-ionic polyacrylamide is 0.1%, and sodium edetate The mass fraction is 0.01%; first add component A, the dosage is 0.2g / L, after 10s, add component B, the dosage is 0.1g / L. During the addition process, keep mixing...

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PUM

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Abstract

The invention discloses a method for deeply purifying landfill leachate. The method comprises the following steps: 1, conveying the landfill leachate to a coagulative precipitation tank, continuouslystirring, adding a compound coagulative precipitation agent, uniformly mixing, stirring, naturally settling, and taking the supernatant; 2, separating ammonia nitrogen in the wastewater obtained in the step 1 by using a gas stripping method, and introducing ammonia nitrogen into acid to recover ammonia nitrogen; 3, conveying the wastewater obtained in the step 2 to a first degradation tank, and adding an oxidant and a first decomposition accelerator; 4, conveying the wastewater obtained in the step 3 to a second degradation tank, and adding an oxidant and a second decomposition accelerator; and 5, conveying the wastewater obtained in the step 4 to a biochemical reaction tank, and treating for 12-48 hours under a facultative condition. The effluent of the water body subjected to deep purification treatment in the steps can be directly discharged after reaching the standard. The treatment method organically combines precipitation-ammonia nitrogen recovery, deep decomposition, biochemicalnitrogen and phosphorus removal and other treatment units, and has the advantages of high treatment efficiency, mild treatment conditions and excellent treatment effect.

Description

technical field [0001] The invention relates to a method for deep purification treatment of landfill leachate, belonging to the technical field of sewage purification treatment. Background technique [0002] With the rapid development of the economy and the continuous improvement of living standards, domestic garbage and industrial solid waste have also increased sharply, and the resulting landfill leachate has become increasingly harmful to the environment. Landfill leachate generally refers to high-concentration wastewater formed during the process of garbage dumping and landfilling due to fermentation, surface water and groundwater immersion, and rainfall leaching, which contains organic acids, alkanes, lipids, heterocycles, etc. Organic compounds and high concentrations of ammonia nitrogen. Landfill leachate has the characteristics of complex pollutant components, high COD value, poor biodegradability, high ammonia nitrogen content and high chroma, and is one of the int...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F9/14C02F101/20C02F101/30C02F103/06
CPCC02F9/00C02F2103/06C02F1/56C02F1/5236C02F2001/007C02F1/20C02F1/54C02F1/725C02F1/722C02F3/00C02F2101/30C02F2101/20Y02W10/10
Inventor 陈世良洪秋林黄亦军谢文杰黄嘉驰
Owner 云南兴滇实业有限公司
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