In India, Central Pollution Control Board (CPCB) and respective state pollution control boards are responsible for the formulation, publishing and regulating the dust suppression standards in India. The CPCB sets guidelines and standards for dust emissions from various industries and activities, and state pollution control boards are responsible for enforcing these regulations.
The Air (Prevention and Control of Pollution) Act, 1981 and the Water (Prevention and Control of Pollution) Act, 1974 are the main legislation that govern dust suppression in India. These acts give the CPCB and state pollution control boards the authority to set standards for dust emissions and to enforce compliance with these standards.
The CPCB has set guidelines for the control of dust emissions from construction and demolition activities, roads, and thermal power plants. These guidelines include measures such as regular water sprinkling, use of dust suppressant chemicals, and proper management of waste materials.
Dust suppression regulations in India are often not strictly enforced and there is a lack of monitoring and enforcement mechanism in many cases. Non-compliance with regulations is a common issue and it's important to raise awareness and create a culture of compliance with the regulations.
Below are the few important dust suppression regulation and Standards in India for M 10 and PM 2.5 type of respirable dust.
2.Sample Scheme to be executed
3.Methodology of checking
4.Scope of work
Also please include the following items
- What is the CPCB norms for dust emission (for belt conveyor and other emissions)
- what is the methodology to give Performance Guarantee. Mechanism to measure the dust norms
(24 hours period and other norms)
- Detailed scope of work
1.1 Continuous Emissions Monitoring – Systems and Benefits Emission measurement and
monitoring by Continuous Emissions Monitoring Systems (CEMS) has been in practice across the
globe for a long time. The CEMS is basically an electronic device, which is capable of capturing
electronic signals, e.g. in milliamps (mA), and they are collected and stored in a data logger. CEMS
have been used for pollutants other than particulate matter in the first major emissions trading
program, the acid rain program in US, and CEMS for PM have been used for monitoring of
concentration based requirements in other settings. However this specification focuses on the use of
PM CEMS with reference to the use of this data as the basis for an emissions trading scheme. Thus
attempts have been made to document issues and aspects of Particulate Matter CEMS (PM-CEMS) in
stationary industrial sources.
Introduction to PM CEMS
The technology behind continuous emissions monitoring systems for particulate matter (PM CEMS)
has been developed since the 1960s when PM CEMS were first used in Germany. In the 1970s, the
use of PM CEMS became a federal requirement in Germany, and particulate matter concentrations
began to be correlated to opacity meter readings in the United States. Since that time, various
regulatory standards for PM CEMS have been developed in different countries, each of which has
been designed for the specific needs and objectives of the regulator. Nevertheless all these standards
share a common broad protocol designed to ensure that the underlying objective of reliable
emissions monitoring is achieved. Some of these standards include the US EPA performance
specification (PS-11), various European specifications including the BS-EN 14181 and BS-EN 14182,
and country standards by the TUV (Germany) and MCERTS (United Kingdom).
PM CEMS Technology
Concurrent with their increasing use in various regulatory and industrial contexts, different
technologies have been developed to make quantitative measurements of particulate matter
concentrations or load in smoke stacks. Different physical principles are commonly used as the basis
of measurement today and these include (i) light scattering, (ii) probe electrification, (iii) light
extinction and (iv) optical scintillation. A less common technology that is sometimes used in special
conditions is (v) beta attenuation.
Light scattering, extinction and scintillation based devices rely on changes in the optical properties of
stack gas as the concentration of particles increases. Probe electrification relies on changes in
generated charge in a probe due to moving particles in the gas stream. Over the years, multiple
studies have been carried out on the performance and characteristics of all these technologies and
some of this history is available from the references to this document (USEPA, 2000).
A characteristic that is common to all of these technologies (with the exception of beta attenuation)
is that they are based on indirect measurement principles and therefore require calibration to smoke
stack conditions before use. Thus calibration of a particulate CEMS device is a central part of all
performance specifications including this one. This calibration in 2 all cases involves a comparison of
the continuous emissions monitoring device to standard gravimetric sampling techniques that are in
use all over the world today. For this same reason, the process of calibration is largely technology
independent. In a sense therefore, PM CEMS can be viewed as an extension of existing manual
sampling techniques where technology is used to move from a one-time measurement of particulate
matter pollutants in the stack, to a continuous measure.
Benefits of PM CEMS
There are many clear benefits to continuous recording of particulate emissions as opposed to manual
stack sampling at specified intervals. These include:
Real Time Information
Manual stack sampling provides no information on particulate emissions in the intervals between
monthly monitoring. However actual emissions may vary quite widely in real time as a function of
operating processes, the operational status of air pollution control devices (APCD), fuel type and
quality, and so on. For this reason it is impossible to accurately estimate total emissions from any
given industry (or group of industries) in a region from occasional stack sampling. This is a major
drawback especially in critically and severely polluted areas where even small increases in pollutant
load can be a major health concern.
PM CEMS data enables the use of load standards instead of concentration standards as the basis for
regulating stationary source emissions. In many situations, load standards have a number of
important advantages over concentration standards, especially because health and environmental
concerns are normally influenced by the mass or volume (in the case of effluents) of pollutants
emitted and not directly by the concentration. A higher pollution load will normally translate into
higher ambient concentrations while a limit on concentration of emissions may still allow for a high
total load to be emitted (through an increase in operating hours, stack volume or the number of
stacks in an area). In addition, while load standards often make more environmental sense than
concentration standards, they also increase the number of options industry has available in order to
comply with regulation. For instance, total load can be reduced by decreasing operating hours.
However this is not a helpful option for an industry attempting to comply with concentration
Transparency and Openness
The use of PM CEMS technologies presents industries, regulators and potentially the public with high
quality, on-going information on emissions from each source so equipped. In turn, this means that
regulation based on this data is also transparent and clear, industries can predict and be aware of the
costs of compliance and plan accordingly, and the public at large obtains the best possible
information on environmental performance of regulated units and the total emissions load in an area
(from regulated stationary sources).
3Market Based Regulatory Mechanisms
PM CEMS can enable implementation of market based regulation, by providing an accurate record of
emissions over time.
Market based regulatory mechanisms such as emissions trading provide a number of benefits to
industry. The principal advantage is that emission reductions can be made at lower cost. Under cap
and trade for instance (a form of emissions trading), only the total emissions load from a number of
industries is fixed but individual units are free to trade emission permits amongst each other such
that reductions are undertaken by those units for whom it is cheapest to do so. This flexibility can
significantly reduce overall costs. In addition, since a cap and trade is based on a load standard the
benefits of regulating load vs. concentration also carry over to industry. Perhaps the most important
of these advantages is the ability of PM CEMS to enable the accurate measurement of total mass
load of emissions which is the critical quantity involved in emissions trading schemes. Indeed, it
would be reasonable to argue that to use PM CEMS only as a support to concentration standards is
to severely underutilize the information content of time series data. An important opportunity that is
opened up for regulators using PM CEMS is the ability to measure and therefore regulate total mass
emitted over a period of time, a quantity that cannot be reliably estimated using one time stack
sampling. This document primarily describes how to use PM CEMS in order to support a market
based regulatory mechanism (emissions trading scheme) targeting total particulate load.
Nevertheless the guidelines and specifications provided here will also enable the use of PM CEMS to
strengthen existing systems of monitoring concentration standards.
1.2 Pilot Emissions Trading Scheme for Particulate Matter
Introduction to Emissions Trading Emissions trading schemes (ETS) have been applied to a variety of
pollutants around the world in order to guarantee environmental outcomes while minimizing
compliance costs. In an ETS, the regulator sets the overall quantity of emissions for a specified area
but does not decide what any particular source will emit. Industrial plants and other polluters, rather
than being prescribed a fixed emissions limit or concentration standard as an individual unit, face a
price for their emissions and choose how much to emit, subject to the overall limit set by the
regulator, taking this price into account. Under ETS, firms have the flexibility to design their own
compliance strategy—emissions reduction through technology adoption or upgradation, or
allowance purchases/sales—to minimize their compliance costs.
The five main areas for the successful implementation of ETS are:
- Setting the Cap. The target for aggregate emissions from the sector where trading is
introduced must be set to produce reasonable prices and emissions reductions.
- Allocating Permits. The permits to emit must be distributed in an equitable way to build
support for the scheme.
- Trading. Permits are based on the total quantity of emissions rather than concentrations
and have a time duration that is set by the regulator. 4
- Monitoring. The quantity of emissions from each industrial plant must be reliably and
continuously monitored with high integrity recognized by all sides.
- Compliance. The regulatory framework must make industries confident that buying
permits is the only reliable way to meet environmental obligations.
Global Experience with ETS
The US EPA pioneered such trading under the Clean Air Act to limit a variety of common air
pollutants beginning in 1974 (Stavins, 2003). The landmark Acid Rain program applied the cap-and-
trade model to sulphur dioxide pollution, achieving sharp reductions in emissions at lower than
expected costs. In recent decades, environmental trading programs have proliferated in the
European Union, Canada and increasingly in developing Asia. China has a nascent sulphur dioxide
market as well as a trading market in CO2 and has been testing market-based policies jointly with the
US EPA since 1999 (Yang and Schreifels, 2003; Schreifels, Fu and Wilson, 2012). Indian industries
trade in Renewable Energy Certificates and, via the Clean Development Mechanism, Certified
Emissions Reductions (CER) for Carbon Dioxide. In 2012, the Indian government’s Bureau of Energy
Efficiency (BEE) launched a trading scheme based on energy consumption to encourage greater
efficiency in energy-intensive industrial sectors.
In this context, the Ministry of Environment & Forests, the Central Pollution Control Board and the
State Pollution Control Boards of the states of Gujarat, Maharashtra and Tamil Nadu have come
together to design and pilot an emissions trading scheme for particulate matter air pollution from
industrial point sources. Particulates are the most severe air pollution problem in India, with most
major cities and many industrial areas out of compliance with the National Ambient Air Quality
Standards for SPM (NAAQS) (CPCB, 2010; CPCB 2011). The model of industrial development in
tightly-clustered industrial estates results in industrial combustion being the key source of particulate
pollution in many areas, though transport emissions have also grown rapidly (CPCB, 2009; CPCB
2011). The emissions trading scheme (ETS) will be piloted in several such large industrial areas to
reduce emissions and to provide a working example of emissions trading in India for a critical local air
The Role of PM CEMS in the ETS pilot .
As noted above, a solid monitoring framework to provide reliable and high quality emissions data
forms the foundation of any successful trading program. It is worth noting that in an ETS there are
two aspects of data quality that are of key importance.
For emissions trading, it is important to have an accurate measurement of the quantity of interest, in
this scheme total load of PM emissions over a set period of time. Some existing ETS have utilised
input-based methods for estimating total emissions load for pollutants ranging from carbon dioxide
to particulate matter; however there are significant drawbacks to this method. For instance, input-
based methods of measurement are not reliable for particulates because PM emissions are a
complex function of combustion conditions and abatement technology. Accordingly, such estimation
methods would not reflect emissions reductions that occur after the inlet, such as improved
maintenance of abatement equipment, which can be a low-cost means of achieving reductions for
industry. Therefore it is critical for 5 a trading scheme in PM to measure the particulate emissions at
the outlet of a stack, necessitating the use of a monitoring technology such as CEMS. Measurement
frequency Although in theory it is possible to extrapolate total emissions from periodic manual
checks, the variations that exist in industry processes and conditions imply that these measures are
highly unreliable as a basis for trading. Therefore having the time series of emissions readings
provided by CEMS technology is necessary to form a more robust and complete measure of total
emissions load, the quantity required for ETS and that ultimately influences ambient air quality.
ETS schemes implemented to date have monitoring protocols that use some combination of input-
based methods of estimation, CEMS, and/or periodic site audits in order to determine compliance
with the scheme. However even in schemes where CEMS are used, they are often not mandated for
all regulated entities and the continuous emissions readings at the industry site are reported to the
regulator on a periodic basis (e.g. quarterly) rather than in real-time. Implementation difficulties in
early programs highlight the importance of having both accurate and high frequency data on
Building upon this experience, this document outlines a unique performance specification and set of
guidelines for the use of continuous emissions monitoring of particulate matter to support load
monitoring for an emissions trading scheme. In so doing, this document breaks new ground in the
use of modern monitoring technology to support innovative market based regulations. This
combination represents a significant advance not just in the Indian context, but globally.
1.3 The PM CEMS Monitoring Framework for ETS
The purpose of this document is to outline the technical and operational requirements of a PM
CEMS-based monitoring framework that provides reliable and accurate data as a foundation for the
pilot particulate matter emissions trading scheme.
The document is broadly divided into three sections that correspond to the key building blocks of
such a system:
∙ Section 2 discusses the technical components, referring to the hardware and software components
that form the basis of the monitoring framework. It also describes the technical specifications and
performance standards that apply to the same.
∙ Section 3 describes the various stakeholders and their roles and responsibilities within the
∙ Section 4 then outlines the standard operating procedures that underpin the functioning of the
whole system. These procedures form the linkages between responsibilities of the various
stakeholders and the specifications and standards required for smooth implementation of the
monitoring framework for ETS.
These components and linkages are illustrated in Figures 1 and 2 which follow.(Additional to be
STANDARDS APPLICABLE TO THE COAL MINES
1) Air Quality – (i) Work zone –Standards for Coal Mines issued by MoEF, GSR-742 E dt. 25.09.2000
(ii) Residential category – National Ambient Air Quality standards issued by CPCB, GSR 176 dt.
- STANDARDS FOR COAL MINES (Stipulated by Ministry of Environment and Forests (MoEF), Vide
Notification No. GSR 742(E), Dt: 25.09.2000)
- AIR QUALITY STANDARDS: (a) Standards
Note : -(i) Annual arithmatic mean of 24- hourly / 8- hourly values shall be met 92% of the time in a
year. However, 8% of the time it may exceed but not on two consecutive days.
(ii) In case of residential or commercial or industrial place falls within 500 metres of any dust
generating sources, the National Ambient Air Quality Standards shall be made applicable. (b)
(1) Air quality monitoring at a frequency of once in a fortnight (24 hourly sampling) at the identified
locations near the dust generating sources.
(2) As a result of monthly monitoring, if it is found that the concentration of the pollutants is less
than the 50% of the specified standards for three consecutive months, then the sampling frequency
may be shifted to two days in a quarter year.
(3) In case the value has exceeded the specified standards, the air quality sampling shall be done
twice in a week. If the results of four consecutive weeks indicate that the concentration of pollutants
is within the specified standards, then fortnightly monitoring may be reverted to.