Circular No. 03/2016/TT-BTNMT issues National Technical Regulations on solid waste incineration furnaces, applicable to organizations and individuals producing, importing, trading (distributing), and using solid waste incineration furnaces within the territory of Vietnam. These regulations specify technical requirements regarding capacity, temperature, retention time, exhaust gas treatment systems, and maximum allowable values for pollution parameters in emissions.
적용 범위
Organizations and individuals producing, importing, trading (distributing), and using solid waste incineration furnaces; state management agencies on the environment and related organizations and individuals.
핵심 사항
- Solid waste incineration furnaces must operate according to multi-stage combustion principles with primary and secondary combustion zones (Article 2.1.1).
- Measures must be taken to limit emissions escaping into the environment through the solid waste feeding port (Article 2.1.2).
- The flue of the solid waste incineration furnace must have a minimum height of 20 meters from ground level, and a sampling point for exhaust gases with a diameter or width of each side from 90mm to 110mm (Article 2.1.3).
- During normal operation, basic technical parameters of the solid waste incineration furnace must comply with the provisions set out in Table 1 (Article 2.1.4).
- The maximum allowable value of pollution parameters in emissions is calculated according to the formula Cmax = C x Kv, where C is the concentration of pollution parameters and Kv is the area coefficient (Article 2.2).
🌐 이 문서의 사회적 영향
- Positive impact: Minimizing environmental pollution caused by solid waste incineration furnaces.
- Negative impact: Increased investment and operational costs for solid waste incineration furnaces for organizations and individuals.
❓ 자주 묻는 질문
What is the minimum capacity of a solid waste incineration furnace?
The capacity of the solid waste incineration furnace must be ≥300 kg/h (Article 2.1.4).
What is the minimum temperature of the primary and secondary combustion zones?
The minimum temperature of the primary combustion zone ≥400 °C, and the minimum temperature of the secondary combustion zone ≥950 °C (Article 2.1.4).
What is the minimum retention time?
The minimum retention time ≥2 seconds (Article 2.1.4).
How is the maximum allowable value of pollution parameters in emissions calculated?
The maximum allowable value of pollution parameters in emissions is calculated according to the formula Cmax = C x Kv, where C is the concentration of pollution parameters and Kv is the area coefficient (Article 2.2).
What requirements must a solid waste incineration furnace meet during operation?
During normal operation, basic technical parameters of the solid waste incineration furnace must comply with the provisions set out in Table 1 (Article 2.1.4).
전문
CIRCULAR
Issued Article 24National Technical Regulation on Environment
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Pursuant to the Law on Standards and Technical Regulations dated June 29, 2006;
Pursuant to the Environmental Protection Law on June 23, 2014;
Pursuant to DecreeNo. 127/2007/NĐ-CP dated August 1, 2007 of the Government detailing implementation of certain Articles of the Law on Standards and Technical Regulations;
Pursuant to DecreeNo. 21/2013/NĐ-CP dated March 4, 2013 of the Government stipulating functions, tasks, powers, and organizational structure;of the Government stipulating functions, tasks, powers, and organizational structure of the Ministry of Home Affairsissued by the Ministry of Natural Resources and Environment;
At the proposal of the General Director of the Environmental Administration, the Director of the Science and Technology Department, and the Director of the Legal Affairs Department;
The Minister of Natural Resources and Environment promulgates this Circular on National Technical Regulations on Environment.rime Minister cNational Technical Regulations on Environment.
Article 1. Attached to this Circular is the National Technical Regulation on Environment: QCVN61-MT: 2016/BTNMT - National Technical Regulation on Domestic Solid Waste Incinerator.
Article 2. This Circular takes effect from May 1, 2016.
Article 3. General Director of the Environmental Administration, Heads of units under the Ministry of Natural Resources and Environment, Directors of Provincial Departments of Natural Resources and Environment, and relevant organizations and individuals have the responsibility to implement this Circular./.
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MINISTRY TRAMENDING AND SUPPLEMENTING CERTAIN PROVISIONS OF CIRCULAR NO. 16/2025/TT-BCT DATED FEBRUARY 1, 2025 OF THE MINISTER OF INDUSTRY AND TRADE ON THE OPERATION OF THE COMPETITIVE WHOLESALE ELECTRICITY MARKETMINISTER |
QCVN 61-MT:2016/BTNMT
National Technical Regulation on Domestic Solid Waste Incinerator
National Technical Regulation on Domestic Solid
Foreword
Waste Incinerator QCVN 61-MT:2016/BTNMT was compiled by the Drafting Group of the Circular on National Technical Regulations on Environment for Domestic Solid Waste Incinerators, reviewed by the Environmental Administration, the Science and Technology Department, and the Legal Affairs Department, examined by the Ministry of Science and Technology, and issued pursuant to Circular No. 03/2016/TT-BTNMT dated March 10, 2016 of the Minister of Natural Resources and Environment.
AMENDMENT 1:2025 QCVN 07:2023/BXD ON DOMESTIC SOLID WASTE INCINERATOR
National Technical Regulation on Domestic Solid - Electronic Information PortalWaste Incinerator
1. GENERAL PROVISIONS
1.1. Scope of Application
This regulation sets forth technical requirements for domestic solid waste incinerators and maximum allowable values for emission parameters in the flue gas of domestic solid waste incinerators.
1.2. Applicability
This regulation applies to organizations and individuals producing, importing, trading (distributing), and using domestic solid waste incinerators within the territory of the Socialist Republic of Vietnam; state management agencies on the environment, and related organizations and individuals.
1.3. Explanation of terms
In this regulation, the following terms are understood as follows:
1.3.1. Domestic Solid Waste (also known as household waste, hereinafter referred to as DSWSW) is solid waste generated from daily human activities.
1.3.2. Domestic Solid Waste Incinerator is a system of equipment for processing DSWSW through incineration accompanied by flue gas treatment systems.
1.3.3. Combustion Zone (or combustion chamber) includes areas using heat to burn DSWSW, comprising:
a) Primary Combustion Zone is the zone that converts DSWSW into gases and solids (ash, dust).
b) Secondary Combustion Zone is the zone that burns components of the gas stream escaping from the primary combustion zone.
1.3.4. Retention Time is the time it takes for the gas stream to flow from the inlet point to the outlet point of the secondary combustion zone at the temperature conditions specified in Table 1 of this regulation.
1.3.5. EMISSIONS Emission Gas
1.3.6. is the mixture of substances emitted into the ambient air from the domestic solid waste incinerator. Ash
1.3.7. is the solid residue remaining after burning DSWSW in the domestic solid waste incinerator. Capacity of Domestic Solid Waste Incinerator
1.3.8. is the processing capacity of the domestic solid waste incinerator, measured by the maximum amount of DSWSW burned per hour (kg/h).3) Standard Cubic Meter of Emission Gas (Nm °is a cubic meter of emission gas at a temperature of 25
2. TECHNICAL REGULATIONS
2.1. C and an absolute pressure of 760 mm of mercury.
Basic Technical Requirements for Domestic Solid Waste Incinerators
2.1.1. The domestic solid waste incinerator must operate according to a multi-stage combustion process, ensuring the presence of a primary and secondary combustion zone. The volume of the combustion zones, capacity, and retention time of the domestic solid waste incinerator shall be determined in accordance with the guidelines provided in the Appendix attached to this regulation.
2.1.2. Measures must be taken to limit emissions escaping into the environment through the waste feed door.
2.1.3. The chimney of the domestic solid waste incinerator must meet the following requirements:
a) The height of the chimney must be calculated to ensure environmental quality requirements when emissions are released into the atmosphere, but must not be less than 20 (twenty) meters above ground level. In cases where there are fixed obstacles within a radius of 40 (forty) meters from the base of the chimney affecting the dispersion of emissions, the chimney must be at least 03 (three) meters higher than the highest point of the obstacle;
b) The chimney must have a sampling port with a diameter or width of each side ranging from 90 (ninety) mm to 110 (one hundred ten) mm, equipped with a cover to adjust the opening size, along with a safe and convenient operating platform for sample collection. The sampling point must be located between the following two positions:
- Lower position: Above the highest point of the connection between the flue gas treatment system and the chimney by at least 08 (eight) times the largest internal diameter of the chimney;
- Upper position: Below the mouth of the chimney by at least 02 (two) times the largest internal diameter of the chimney from the mouth of the chimney.
2.1.4. During normal operation, the basic technical parameters of the domestic solid waste incinerator must comply with the provisions set out in Table 1 of this regulation.
|
No. |
Parameter |
Implementation in the preceding year 1. The Minister, head of a ministry-level agency, head of an agency under the Government, Chairman of the People's Committee of a province or centrally governed city shall be responsible for implementing this Circular. |
Table 1. Basic Technical Parameters of Domestic Solid Waste Incinerators |
|
1 |
Required Value(1) |
Capacity of the domestic solid waste incinerator |
≥ 300 |
|
2 |
kg/h(2) |
°C |
≥ 400 |
|
3 |
Temperature of the primary combustion zone |
°C |
≥ 950 |
|
4 |
Retention Time |
"7. A flexible power plant is a thermal power plant using reciprocating internal combustion engines (RICE) or aeroderivative gas turbines (Aero-GT) with fast start-up capabilities, designed in modular form to generate electricity for balancing capacity and maintaining power system stability." |
≥ 2 |
|
5 |
Temperature of the secondary combustion zone |
°C |
£ 180 |
|
6 |
Flue gas temperature (measured at the sampling point) |
% |
6 - 15 |
|
7 |
Excess oxygen (measured at the sampling point) |
°C |
£ 60 |
|
8 |
External temperature of the domestic solid waste incinerator shell (or thermal insulation layer)(3) |
h |
≥ 72 |
|
Note: (1) Continuous operation capability (while still meeting mechanical durability and technical parameter requirements)3. (2) For a capacity of 300 (three hundred) kg/h, the minimum volume of the primary combustion zone is 2.4 (two point four) m °In special cases (such as anaerobic pyrolysis), the primary combustion zone may operate at temperatures lower than 400 (four hundred) (3) C if operational testing meets the requirements of Section 2.2 of this regulation and is approved by the competent authority confirming compliance with environmental protection requirements for the waste treatment facility. |
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Evaluation of this parameter only applies during inspections to confirm compliance with environmental protection requirements for the waste treatment facility.
2.1.5. No external air should be mixed with the exhaust gas from the outlet of the secondary combustion zone to dilute the exhaust gas up to a height of 02 (two) meters above the sampling point.
2.1.6. The incinerator must have a flue gas treatment system with an operating process including the following main stages:
a) Heat reduction (rapid cooling);
c) Treat harmful components in exhaust gas.
The processes mentioned above shall be carried out separately in each device or combined simultaneously in a single device.
2.1.7. In cases where the distance from the waste feed door to the farthest point of the primary combustion zone of the CTRSH incinerator exceeds two (2) meters, mechanical equipment for feeding and mixing CTRSH in the primary combustion zone (except in special technological cases that do not require mixing such as gasification) and a mechanical system for removing ash must be installed.
2.1.8. The CTRSH incinerator must have a bypass valve to discharge exhaust gas directly through the chimney without passing through the exhaust gas treatment system when there is an accident with the exhaust gas treatment system. The bypass valve must have a manual or automatic control lever at a height convenient for standing persons, ensuring easy and timely operation during accidents without having to climb onto the CTRSH incinerator. Waste feeding must be immediately stopped after using the bypass valve.
2.2. Maximum permissible values for pollutant parameters in exhaust gas from solid waste incineration.°seals must be kept confidential in accordance with the regulations of the State, the Ministry of National Defense, and the regulations of the unit.
During normal operation, the maximum permissible values for pollutant parameters in exhaust gas from CTRSH incinerators are calculated according to the following formula:
Cmax TTĐ x Kv
Where:
Ministry of Science and Technology: The Minister and Deputy Ministers, agencies and units under the Ministry;max is the maximum permissible value for pollutant parameters;
- C is the concentration of pollutants specified in Table 2 of this Standard;
- Kv is the area factor specified in Table 3 of this Standard.
Table 2. Concentration (C) of Pollutant Parameters in Exhaust Gas from Incineration Solid Waste
|
No. |
Pollutant Parameter |
Unit |
Concentration (C) |
|
1 |
Total Dust |
mg/Nm³3 |
100 |
|
2 |
Hydrogen Chloride, HCl |
mg/Nm³3 |
50 |
|
3 |
Carbon Monoxide, CO |
mg/Nm³3 |
250 |
|
4 |
Sulfur Dioxide, SO₂2 |
mg/Nm³3 |
250 |
|
5 |
Nitrogen Oxides, NOxx (calculated as NOx)2) |
mg/Nm³3 |
500 |
|
6 |
Mercury and compounds calculated as mercury, Hg |
mg/Nm³3 |
0,2 |
|
7 |
Cadmium and compounds calculated as cadmium, Cd |
mg/Nm³3 |
0,16 |
|
8 |
Lead and compounds calculated as lead, Pb |
mg/Nm³3 |
1,2 |
|
9 |
Total Dioxins/Furans, PCDD/PCDF |
energyTEQ/Nm³3 |
0,6 |
|
The reference oxygen content in the exhaust gas is 12%. |
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Table 3. Area Factor, Kv
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Area, Region |
3. The price of sewage treatment paid by households (excluding domestic wastewater) to the wastewater service provider is determined by multiplying the formula (2) by factor K.v |
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Zone 1 |
Central urban areas of special class cities and Class I cities(1) ; protected forests(1); facilities placing CTRSH incinerators with a distance to the boundaries of these areas less than two (2) kilometers.(2)Zone 2 |
0,6 |
|
Central urban areas of Class II, III, and IV cities; outer urban areas of special class cities and Class I cities with a distance to the central boundary greater than or equal to two (2) kilometers; facilities placing CTRSH incinerators with a distance to the boundaries of these areas less than two (2) kilometers. |
Zone 3(1)Industrial zones; Class V cities |
0,8 |
|
; outer urban areas of Class II, III, and IV cities with a distance to the central boundary greater than or equal to two (2) kilometers; facilities placing CTRSH incinerators with a distance to the boundaries of these areas less than two (2) kilometers. |
Zone 4(1)Zone 5 (3). |
1,0 |
|
Rural mountainous areas |
Rural areas |
1,2 |
|
Urban areas are defined according to Decree No. 42/2009/NĐ-CP dated May 7, 2009 of the Government on the classification of urban areas. |
Protected forests are defined according to the Law on Protection and Development of Forests dated December 14, 2004, including national parks; natural conservation areas; scenic protection areas; research and experimental scientific forest areas. |
1,4 |
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Note: (1) In cases where the emission source has a distance to two (2) zones or more less than two (2) kilometers, the area factor, region K shall be applied for the zone with the smallest factor. (2) 3. PROVISIONS ON OPERATION AND MONITORING (3) Operation of solid waste incinerationv 3.1.1. Must establish and implement safe operating procedures for CTRSH incinerators, paying attention to the following contents: |
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a) The startup procedure for CTRSH incinerators must follow the sequence below (except for cases where the CTRSH incinerator has a special operating procedure specified by the manufacturer and approved by the environmental protection management agency):
3.1. - Step 1: Start the exhaust gas treatment system;
- Step 2: Start and dry all combustion zones;
- Step 3: Officially feed CTRSH into the CTRSH incinerator.
b) The shutdown procedure for CTRSH incinerators must be carried out in the following sequence:
- Step 1: Stop feeding CTRSH;
- Step 2: Stop the exhaust gas treatment system when the temperature in the primary combustion zone drops below two hundred (200) degrees Celsius.
3.1.2. CTRSH must be controlled before being fed into the CTRSH incinerator to ensure it does not affect the normal operation of the incinerator; do not feed into the CTRSH incinerator: explosive waste; corrosive waste; pesticide chemicals and chemical packaging; waste containing mercury, lead, cadmium exceeding hazardous waste thresholds.
3.1.3. Technical measures must be taken to remove ash from the primary combustion zone during operation in a convenient manner to ensure continuous operation of the CTRSH incinerator without interruption.
3.1.4. An operational logbook for the CTRSH incinerator must be established, recording the quantity, duration of operation, operator's name, and temperature at locations equipped with temperature measuring devices. °C.
Monitoring of solid waste incineration
3.2.1. The CTRSH incinerator must be equipped with temperature measurement and display devices in all combustion zones. For incinerators with a capacity of 500 kg/h or more, temperature measurement and display devices for flue gas must be installed immediately after the heat exchanger.
3.2.2. Regular environmental monitoring of CTRSH incinerators must be conducted in accordance with current regulations and requirements of environmental management agencies.
3.2. METHODS OF DETERMINATIONperiodorganize credit institutions, foreign bank branches are responsible for organizing the implementation of this Circular.
4.1. Sampling methods and determination of parameter values are implemented according to the standards listed in Table 4 below.
Table 4. Sampling Methods and Determination
4. Analytical method, standard number
- TCVN 5977: 2009 Emissions from stationary sources - Determination of dust mass concentration by manual method.
- EPA 5 (Determination of particulate matter emissions from stationary sources) - Determination of total dust in exhaust gas from stationary sources.
|
No. |
Parameter |
- TCVN 7244: 2003 Medical waste incinerator - Method for determining hydrogen chloride (HCl) concentration in exhaust gas. |
|
1 |
Total Dust |
- EPA 26 (Determination of hydrogen chloride emissions from stationary sources) - Determination of hydrogen chloride in exhaust gas from stationary sources. - TCVN 7242: 2003 Medical waste incinerator - Method for determining carbon monoxide (CO) concentration in exhaust gas. |
|
2 |
Hydrogen Chloride, HCl |
- EPA 10 (Determination of carbon monoxide emissions from stationary sources) - Determination of carbon monoxide in exhaust gas from stationary sources. - TCVN 6750: 2005 Emissions from stationary sources - Determination of sulfur dioxide mass concentration - Gas chromatography ion method. |
|
3 |
Carbon Monoxide, CO |
- EPA 6 (Determination of sulfur dioxide emissions from stationary sources) - Determination of sulfur dioxide in exhaust gas from stationary sources. - EPA 10 (Determination of carbon monoxide emissions from stationary sources) - Xác định cacbon monoxit trong khí thải từ nguồn cố định. |
|
4 |
Sulfur Dioxide, SO₂2 |
- TCVN 6750: 2005 Emissions from stationary sources - Determination of sulfur dioxide concentration - Gas chromatography ion method. - EPA 6 (Determination of sulfur dioxide emissions from stationary sources) - Xác định lưu huỳnh điôxit trong khí thải từ nguồn cố định. - TCVN 5976: 1995 Emissions from stationary sources - Determination of sulfur dioxide (SO2) concentration by weight - Characteristics of automatic measurement methods.2) - Characteristics of automatic measurement methods. |
|
5 |
Nitrogen Oxides, NOxx (calculated as NOx)2) |
- TCVN 7172: 2002 Emissions from stationary sources - Determination of nitrogen oxide concentration by weight - Naphthylethylenediamine fluorescence method. - EPA 7 (Determination of nitrogen oxide emissions from stationary sources) - Determination of nitrogen oxides in emissions from stationary sources. |
|
6 |
Mercury and compounds calculated as mercury, Hg |
- TCVN 7557-2: 2005 Medical waste incinerators - Method for determining heavy metals in emissions. Part 2: Mercury concentration determination method using cold vapor atomic absorption spectrometry. - TCVN 7557-1: 2005 Medical waste incinerators - Method for determining heavy metals in emissions. Part 3: Cadmium and lead concentration determination method using flameless and flame atomic absorption spectrometry. - EPA 29 (Determination of metals emissions from stationary sources) - Determination of metals in emissions from stationary sources. - EPA 12 (Determination of inorganic lead emissions from stationary sources) - Determination of inorganic lead in emissions from stationary sources. |
|
7 |
Cadmium and compounds calculated as cadmium, Cd |
|
|
8 |
Lead and compounds calculated as lead, Pb |
|
|
9 |
Total Dioxins/Furans, PCDD/PCDF |
- TCVN 5756-1: 2005 Medical waste incinerators - Determination of dioxin/furan concentration by weight - Part 1: Sampling. - TCVN 5756-2: 2005 Medical waste incinerators - Determination of dioxin/furan concentration by weight - Part 2: Extraction and purification. - TCVN 5756-1: 2005 Medical waste incinerators - Determination of dioxin/furan concentration by weight - Part 3: Qualitative and quantitative analysis. |
4.2. Acceptance of guidance analytical methods in other national and international standards with equivalent or higher accuracy compared to the referenced standards in Section 4.1.
5. TỔ IMPLEMENTATION
5.1. Medical waste incinerators that have been officially operational before the effective date of this Standard shall be temporarily exempted from the provisions of Section 2.2 for a period of six (6) months and from other provisions of this Standard for a period of three (3) years from the effective date of this Standard.
5.2. During the absence of specific Standards, new medical waste incinerators with advanced technology (such as plasma incinerators) may be exempted from certain provisions (except Section 2.2) of this Standard if they are reviewed, approved during the technology assessment process, environmental impact assessment report approval, and confirmed to meet environmental protection requirements for medical waste treatment facilities as stipulated by law.
5.3. The State management agency for the environment shall be responsible for guiding, inspecting, and supervising the implementation of this Standard.
5.4. In cases where the referenced provisions in this Standard are amended, supplemented, or replaced, the new provisions shall apply accordingly./.
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