GB 25466-2010 PDF in English
GB 25466-2010 (GB25466-2010) PDF English
| Standard ID | Contents [version] | USD | STEP2 | [PDF] delivered in | Name of Chinese Standard | Status |
| GB 25466-2010 | English | 120 |
Add to Cart
|
0-9 seconds. Auto-delivery.
|
Emission standard of pollutants for lead and zinc industry
| Valid |
Standards related to (historical): GB 25466-2010
PDF Preview
GB 25466-2010: PDF in English GB 25466-2010
GB
NATIONAL STANDARD OF THE
PEOPLE’S REPUBLIC OF CHINA
Emission standard of pollutants
for lead and zinc industry
[Including Modification List 2013XG1]
ISSUED ON. SEPTEMBER 27, 2010
IMPLEMENTED ON. OCTOBER 01, 2010
Issued by. Ministry of Environmental Protection;
General Administration of Quality Supervision, Inspection and
Quarantine.
Table of Contents
Announcement of Ministry of Environmental Protection of PRC ... 2
Foreword ... 5
1 Scope ... 7
2 Normative references ... 7
3 Terms and definitions ... 10
4 Pollutant emission control requirements ... 11
5 Pollutant monitoring requirements ... 17
6 Implementation and supervision ... 21
Modification List 2013XG1 ... 22
Foreword
To implement the Environmental Protection Law of the People's Republic of
China, the Law of the People's Republic of China on Prevention and Control of
Water Pollution, the Law of the People's Republic of China on Prevention and
Control of Atmospheric Pollution, the Law of the People's Republic of China on
Marine Environmental Protection, and the State Council on Strengthening the
Environment Laws and Regulations on Protection and other "Opinions of the
State Council on the Preparation of National Main Functional Area Planning",
to protect the environment, to prevent pollution, to promote the progress of lead
and zinc industrial production processes and pollution control technologies, this
Standard was formulated.
This Standard specifies the emission limits, monitoring and monitoring
requirements for water pollutants and atmospheric pollutants in the production
process of lead and zinc industrial enterprises. It is applicable to water pollution
and air pollution prevention and management in lead and zinc industrial
enterprises. In order to promote the coordinated development of regional
economy and environment, promote the adjustment of economic structure and
the transformation of economic growth mode, and guide the development
direction of lead and zinc industrial production processes and pollution control
technologies, this Standard specifies particular emission limits for water
pollutants.
The pollutant discharge concentration in this Standard is the mass
concentration.
Lead and zinc industrial enterprises emit odorous pollutants and environmental
noises. The identification, treatment and disposal of solid wastes are applicable
to national solid waste pollution control standards.
This Standard shall be issued for the first time.
From the date of implementation of this Standard, the discharge of water and
atmospheric pollutants from lead and zinc industrial enterprises shall comply
with this Standard. It shall not comply with relevant provisions in "Integrated
Wastewater Discharge Standard" (GB 8978-1996), "Comprehensive emission
standard of atmospheric pollutants" (GB 16297-1996) and "Standard of smoke
and dust emission for industrial kiln and furnace" (GB 9078-1996).
Local provincial people's governments may formulate local pollutant discharge
standards for pollutants not specified in this Standard. For pollutants that have
been stipulated in this Standard, local pollutant discharge standards that are
stricter than this Standard may be formulated.
Emission standard of pollutants
for lead and zinc industry
1 Scope
This Standard specifies the emission limits, surveillance and monitoring
requirements for water pollutants and atmospheric pollutants in lead and zinc
industrial enterprises, as well as relevant provisions on implementation and
supervision of standard.
This Standard is applicable to the management of water pollutants and
atmospheric pollutants in lead and zinc industrial enterprises, as well as
environmental impact assessment, environmental protection facilities design,
and environmental protection acceptance of lead and zinc industrial enterprises
construction projects as well as the management of water pollutants and
atmospheric pollutants after they are put into production.
This Standard does not apply to industries such as calendering of recycled lead,
recycled zinc and lead timber, zinc timber. It is not applicable to non-
characteristic production processes and devices affiliated with lead and zinc
industrial enterprises.
This Standard applies to the discharge of pollutants permitted by law. For site
selection of newly established pollution sources and management of existing
pollution sources in special protection areas, in addition to this Standard, it shall
also comply with the relevant provisions of laws, regulations and rules such as
the Law of the People's Republic of China on Prevention and Control of
Atmospheric Pollution, the Law of the People's Republic of China on Prevention
and Control of Water Pollution, the Law of the People's Republic of China on
Marine Environmental Protection, the Law of the People's Republic of China on
the Prevention and Control of Environmental Pollution of Solid Wastes, the
Environmental Impact Assessment Law of the People's Republic of China.
The water pollutant emission control requirements specified in this Standard
are applicable to the behavior of enterprises directly or indirectly discharging
water pollutants outside their legal boundaries.
2 Normative references
This Standard refers to the following documents or their terms.
HJ/T 195-2005, Water quality - Determination of ammonia-nitrogen Gas-
phase molecular absorption spectrometry
HJ/T 199-2005, Water quality - Determination of total-nitrogen Gas-phase
molecular absorption spectrometry
HJ/T 399-2007, Water quality - Determination of the chemical oxygen
demand - Fast digestion - Spectrophotometric method
HJ 482-2009, Ambient air - Determination of sulfur dioxide - Formaldehyde
absorbing-pararosaniline spectrophotometry
HJ 483-2009, Ambient air - Determination of sulfur dioxide in ambient air -
Tetrachloromercurate (TCM) - pararosiniline method
HJ 487-2009, Water quality - Determination of Fluoride - Visual colorimetry
zirconium alizarin sulfonate
HJ 488-2009, Water quality - Determination of Fluoride - Fluorine reagents
spectrophotometry
HJ 535-2009, Water Quality - Determination of Ammonia Nitrogen - Nesslers
Reagent Spectrophotometry
HJ 536-2009, Water quality - Determination of ammonia nitrogen - Salicylic
acid spectrophotometry
HJ 537-2009, Water quality - Determination of ammonia nitrogen - Distillation
- neutralization titration
HJ 538-2009, Stationary source emission - Determination of lead - Flame
atomic absorption spectrometry (on trial)
HJ 539-2009, Ambient air. Determination of lead. Graphite furnace atomic
absorption spectrometry (on trial)
HJ 542-2009, Ambient air - Determination of mercury and its compounds -
Cold atomic fluorescent (on trial)
HJ 543-2009, Stationary source emission - Determination of mercury - Cold
atomic absorption spectrophotometry (on trial)
HJ 544-2009, Stationary source emission - Determination of sulfuric acid
mist-Ion chromatography (on trial)
Measures for the Automatic Monitoring and Control of Pollution Sources
(Order No. 28 of the State Environmental Protection Administration)
Measures for the Administration of Environmental Monitoring (Order No. 39
3.8 standard condition
referring to the state when the temperature is 273.15 K and the pressure is 101
325 Pa; the atmospheric pollutant emission concentration limits specified in this
Standard are based on dry gas under standard conditions
3.9 excess air coefficient
referring to the ratio of actual air volume to theoretical air demand during
industrial furnace operation
3.10 enterprise boundary
referring to the legal boundary of lead and zinc industrial enterprises; if the
boundary cannot be determined, it means the actual boundary
3.11 public wastewater treatment system
referring to enterprises or institutions that collect wastewater through sewage
pipelines, provide wastewater treatment services to more than two pollutant
discharge units, and discharge to meet relevant emission standards, including
urban sewage treatment plants of various scales and types, regional (including
various industrial parks, development zones, industrial agglomerations, etc.)
wastewater treatment plants, etc., of which the degree of wastewater treatment
shall reach level two or more
3.12 direct discharge
referring to the behavior of pollutant discharge units directly discharging water
pollutants into the environment
3.13 indirect discharge
referring to the behavior of pollutant discharge units discharging water
pollutants into public sewage treatment systems
4 Pollutant emission control requirements
4.1 Control requirements for water pollutant emission
4.1.1 From January 1, 2011 to December 31, 2011, existing facility shall
implement the water pollutant emission limits specified in Table 1.
as the basis for determining whether the emission meets the standard
requirements. The product production and effluent volume statistics period is
one working day.
In the case of producing two or more products at the same time in the
production facilities of the enterprise, when it is applicable to different emission
control requirements or national pollutant emission standards of different
industries, and the sewage generated by the production facilities is mixed and
discharged, the most stringent concentration limits specified in the emission
standards shall be implemented. And the benchmark effluent volume emission
concentration of water pollutant shall be converted according to formula (1).
where,
ρbenchmark - the benchmark effluent volume emission concentration of water
pollutant, mg/L;
Qtotal - the total drainage, m3;
Yi - the yield of the ith kind of product, t;
Qi benchmark - the benchmark effluent volume per unit product of the ith kind of
product, m3/t;
ρmeasured - the measured concentration of water pollutant, mg/L.
If the ratio of Qtotal to ΣYi·Qi benchmark is less than 1, then use the measured
concentration of water pollutant as the basis for determining whether the
emission meets the standard requirements.
4.2 Control requirements for atmospheric pollutant emission
4.2.1 From January 1, 2011 to December 31, 2011, existing facility shall
implement the atmospheric pollutant emission limits specified in Table 4.
ρbenchmark Qtotal
ΣYi·Qi benchmark
ρmeasured
Table 6 -- Atmospheric pollutant concentration limits at enterprise
boundary of existing and new facilities
mg/m3
No. Pollutant item Maximum concentration limit
1 Particulates 0.5
2 Sulfur dioxide 1.0
3 Sulfuric acid mist 0.3
4 Lead and its compounds 0.006
5 Mercury and its compounds 0.0003
4.2.5 In the production process after the completion of environmental protection
acceptance of existing facility production and construction projects, the
environmental protection department in charge of supervision shall monitor the
environmental quality of sensitive areas around the residential, teaching,
medical and other uses. The specific monitoring scope of the construction
project is the surrounding sensitive area determined by the environmental
impact assessment. For existing facility that has not conducted environmental
impact assessment, the scope of monitoring shall be determined by the
competent environmental protection department in charge of supervision,
according to the characteristics and laws of the facility’s sewage discharge and
local natural and meteorological conditions, etc., with reference to the relevant
environmental impact assessment technical guidelines. The local government
shall be responsible for the environmental quality of its jurisdiction and take
measures to ensure that the environmental conditions meet the requirements
of environmental quality standards.
4.2.6 The production processes and devices that produce atmospheric
pollutants must establish local or integral gas collection systems and
centralized purification treatment devices. All stack height shall be no less than
15 m. When there are buildings within a radius of 200 m around the stack, the
stack height shall be higher than the maximum height by more than 3 m.
4.2.7 The lead and zinc smelting furnaces have an excess air ratio of 1.7. The
measured pollutant emission concentration of lead and zinc smelting furnaces
shall be converted into the benchmark excess air coefficient emission
concentration. Production facilities shall adopt reasonable ventilation measures.
Do not intentionally dilute emissions. Before the country does not stipulate the
benchmark exhaust volume of other production facilities, the actual measured
concentration shall be used as the basis for determining whether it meets the
standard.
5 Pollutant monitoring requirements
5.1 General requirements for pollutant monitoring
14 Total arsenic
Water quality - Determination of total arsenic
- Silver diethyldithiocarbamate
spectrophotometric method
GB/T 7485-1987
15 Total nickel
Water quality - Determination of nickel -
Flame atomic absorption spectrometric
method
GB/T 11912-1989
16 Total chromium Water quality. Determination of total chromium GB/T 7466-1987
5.3 Atmospheric pollutant monitoring requirements
5.3.1 The sampling point setting and sampling method are performed according
to GB/T 16157-1996.
5.3.2 Unorganized emission monitoring in the presence of sensitive buildings
and where necessary are monitored according to HJ/T 55-2000.
5.3.3 The measurement of the concentration of atmospheric pollutants emitted
by enterprises is based on the method standards listed in Table 8.
Table 8 -- Standards for determination methods of water pollutant
concentration
No. Pollutant item Standard name of method Reference to standard
1 Particulates
The determination of particulates and
sampling methods of gaseous pollutants
emitted from exhaust gas of stationary source
GB/T 16157-1996
Ambient air - Determination of total suspended
particulates - Gravimetric method GB/T 15432-1995
2 Sulfur dioxide
Determination of sulphur dioxide from
exhausted gas of stationary source Iodine
titration method
HJ/T 56-2000
Determination of Sulphur Dioxide from
Exhausted Gas of Stationary Source - Fixed-
potential Electrolysis Method
HJ/T 57-2000
Ambient air - Determination of sulfur dioxide -
Formaldehyde absorbing-pararosaniline
spectrophotometry
HJ 482-2009
Ambient air - Determination of sulfur dioxide in
ambient air -Tetrachloromercurate (TCM) -
pararosiniline method
HJ 483-2009
3 Sulfuric acid mist
Stationary source emission - Determination of
sulfuric acid mist-Ion chromatography (on trial) HJ 544-2009
......
Source: Above contents are excerpted from the PDF -- translated/reviewed by: www.chinesestandard.net / Wayne Zheng et al.
|