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DL/T 1939-2018 in English

DL/T 1939-2018 in English

VALID

Technical specification for leachate treatment of waste-to-energy plant

  • Issued on:2018-12-25
  • Implemented on:2019-05-01
  • File Format:PDF
  • Delivery:Via email within 1~3 business days
Price(USD): $190.00
$185.00
Standard No: DL/T 1939-2018
Document status: VALID
Title in English: Technical specification for leachate treatment of waste-to-energy plant
Title in Chinese: 垃圾发电厂渗沥液处理技术规范
Language: English
File Format: Electronic (PDF)
Delivery: Via email within 1~3 business days
Issued on: 2018-12-25
Implemented on: 2019-05-01
Professional Classification: DL-Electricity
Related Topics: Rubbish
Treatment fluid
Garbage liquid detection
Waste-to-energy
Leachate Treatment
seepage + English
power plant
Waste-to-energy
landfill leachate
landfill leachate
How to dispose of garbage
dispose of garbage
Garbage plant
Lai Waste-to-energy
Underground waste disposal
Underground Waste Treatment Plant
Disposal of foreign garbage
Treatment plant waste
Foreign countries and garbage disposal
Garbage treatment plant garbage
Leachate
liquid treatment
junk tech
Exudate
liquid treatment
How to Dispose of Garbage
Garbage disposal methods by country
Foreign garbage disposal methods
Food Waste Treatment Plant
How to deal with large garbage
rubbish standard
Garbage disposal method
Large waste disposal
What to do with space junk
Space Junk Treatment Technology
14th Five-Year Waste Disposal
Technical specification for flue gas purification system of waste-to-energy plant
"Technical Specifications for Slag Treatment in Waste-to-Energy Power Plants" DL/T1938
E-waste disposal
Fully quantitative treatment technology for domestic waste leachate
Waste-to-energy power plant slag treatment technology


Introduction

Analysis of the core content of the standard

DL/T1939-2018 is my country's first technical standard specifically for the treatment of leachate from waste-to-energy plants. It systematically specifies the technical requirements for the entire process from regulating tank to reverse osmosis. The standard highlights the following technical features:

  • Innovatively proposes a regional difference coefficient (10-30% in South China, 15-30% in North China)
  • Clearly defines the hierarchical control of MBR membrane flux (6-12L/(h·㎡) for submerged type, 60-70L/(h·㎡) for external type)
  • Establishes a three-stage process combination benchmark (pretreatment + anaerobic + MBR + deep treatment)

Comparative Analysis of Key Processes

Process Unit Control Parameters Core Equipment Efficiency Index
Anaerobic Treatment Temperature 30-38℃, volumetric load 5-15kgCOD/(m³·d) UASB/IC reactor COD removal rate ≥60%
MBR system DO 1-3mg/L, sludge concentration 8-12g/L Submerged ultrafiltration membrane Ammonia nitrogen removal rate ≥95%
Advanced treatment NF flux ≤14L/(h·㎡), RO flux ≤12L/(h·㎡) DTRO/STRO Desalination rate ≥ 98%

Typical water treatment case

Take a 1500t/d waste-to-energy plant in East China as an example, adopting the IC+MBR+DTRO combined process:

  1. The influent COD of 65000mg/L is reduced to 15000mg/L through the IC reactor
  2. The MBR effluent COD is stabilized below 800mg/L
  3. The final DTRO product water COD is ≤60mg/L, meeting the standard in Table 2 of GB16889

Critical Control Points: The equalization tank is maintained at a negative pressure of -50Pa, the anaerobic system is maintained at a positive pressure of 2000Pa, and the MBR membrane group is regularly chemically cleaned for ≤3 months


Implementation Suggestions

Key Points of Operation and Management

  • Establish a three-level inspection system (shift inspection, daily inspection, special inspection)
  • Configure online water quality analyzers (COD, NH3-N, flow meter)
  • Implement redundancy design for key equipment (membrane group, water pump, aeration system)

Safety Prevention and Control Measures

  • Configure explosion-proof electrical appliances in explosion-hazardous areas in accordance with GB50058
  • The installation distance between methane detection alarms is ≤15m
  • A negative pressure collection system is installed in the sludge dewatering room.

Technological evolution trend

Comparing the project data before and after 2010, the technological development shows three major characteristics:

  1. The treatment process has shifted from single AO to a combined process (IC+MBR+NF)
  2. The emission standard has been upgraded from GB16889-2008 to Surface Water Level IV
  3. The treatment of concentrated liquid has shifted from backspray to evaporation and crystallization with zero emission

In the future, the focus will be on the development of high-efficiency anaerobic bacteria cultivation and membrane fouling control technology

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