Description of content-set
The data set "Emissions of the most common polluting atmosphere of substances departing from stationary sources" contains information on the number of emissions of the most common pollutants in the city of Moscow. Data is given on the basis of an annual statistical collection "The state of atmospheric air of the city of Moscow", published by the territorial body of the Federal State Statistics Service in Moscow (Mosgorostat). Indicators are given on legal entities that have inpatient sources of emissions of pollutants into atmospheric air.
Basic concepts:
source of emission - construction, technical device, equipment that are isolated in atmospheric air harmful (pollutants) substances
stationary source - a source of emission, the location of which is determined using a unified state coordinate system or which can be moved by means of a mobile source
Modern situation in Russia.
Today in Russia there is a decrease in emissions of pollutants. Dynamics and a change in the overall structure of emissions of harmful substances is represented in the Russian statistical annudent of the Federal Service of the State.
According to regular observations of Roshydromet for the period 2011 - 2015. The average concentration of suspended substances, nitrogen dioxide, nitrogen oxide, sulfur dioxide and carbon oxide decreased by 8-15%.
Modern situation in Moscow.
According to the Moscow City Court of Moscow, 457 enterprises operate on which less than 30 thousand inpatient sources of pollutant emissions into atmospheric air are registered. At the moment, in the territory of the city of Moscow, there is a negative dynamics of numerical indicators that characterize the emissions of the most common pollutants of substances from stationary sources of 6.9% from 2014 to 2016.
Table. "Emissions of the most common polluting atmospheric substances departing from stationary sources" Moscow. (thousand tons).
Years |
Total |
including: |
||||||
emissions |
solid |
gaseous and liquid |
of them |
|||||
sulfur dioxide |
azota oxides |
oxide carbon |
hydrocarbon (without volatile organic compounds) |
volatile organic compounds |
||||
2011 |
61,2 |
59,6 |
13,2 |
35,4 |
||||
2012 |
71,6 |
70,3 |
17,3 |
36,5 |
||||
2013 |
66,0 |
64,7 |
12,9 |
33,1 |
||||
2014 |
67,7 |
66,1 |
10,7 |
33,0 |
10,0 |
|||
2015 |
63,2 |
61,6 |
29,7 |
|||||
2016 |
63,0 |
61,5 |
31,5 |
10,3 |
Do you know what?
In Moscow, the Law "On Environmental Monitoring in the city of Moscow" and the Decree of the Government of Moscow of 08.11.2005 No. 866-PP "On the functioning of a unified environmental monitoring system and the practical use of environmental monitoring data" is the most significant from the point of view of anthropogenic environmental impact. Industrial enterprises are required to create automated systems for direct instrumental measurements of pollutant emissions into the atmosphere on organized sources.
Equipment tools for automated control are subject to sources of pollutants emissions, in which, with the greatest probability, supernormative emissions of pollutants can occur into the atmosphere, as well as sources used in measures to reduce pollutant emissions, with adverse meteorological conditions.
Automated systems of local environmental monitoring provide continuous automatic control of the main characteristics of emissions of pollutants - the magnitude of emissions of dioxide and nitrogen oxide, hydrogen oxide, hydrogen chloride, sulfur dioxide, amount of suspended substances, mixtures of limit hydrocarbons C1-C5, hydrogen sulfide, flow rate, linear velocity and temperature Exhaust flue gases. The list of controlled parameters is determined individually taking into account the composition of the emissions of the industrial enterprise. The measurement results are transmitted in real time to the information and analytical center of the unified state system of environmental monitoring of the city of Moscow, whose functions performs the GPBU "Mosekomonitoring".
At the moment, the systems of local environmental monitoring are equipped with 55 industrial enterprises of the city of Moscow: 51 enterprise of the heat and energy complex (11 Moscow CHP, 40 regional heat stations), 3 Gazpromneft-MNPR JSC oil-influence plant.
An analysis of the operation of control systems demonstrates their effectiveness to prevent unauthorized exhaust emissions. So in 2016, according to the results of the operation of the control systems, 3 cases of exceeding PDV norms on sources of emissions of enterprises, which is 15 times less than the same indicator in 2011. At the same time, the total total extensive release in 2016 decreased compared with 2011 more than 100 times (from 1317 kg to 13 kg).
The material is prepared on the basis of information:
http: // DATA. MOS. Ru /, http://moscow.gks.ru, state report "On the status and environmental protection of the Russian Federation in 2015".Industrial and economic development is accompanied, as a rule, an increase in environmental pollution. Most major cities are characterized by a significant concentration of industrial facilities in relatively minor territories, which represents the danger to people's health.
One of the environmental factors that have the most pronounced effect on human health is air quality. Special danger is currently emissions into the atmosphere of pollutants. This is due to the fact that the toxicants go into the human body mainly through the respiratory tract.
Emissions to the atmosphere: sources
There are natural and anthropogenic sources of contaminants entering the air. The main impurities that contain emissions into the atmosphere from natural sources are dust of cosmic, volcanic and vegetable origin, gases and smoke resulting from forest and steppe fires, products of destruction and weathering of rocks and soils, etc.
Air pollution levels with natural sources are background character. They change little enough with time. The main sources of contaminants in the air pool of pollutants at the present stage are anthropogenic, namely - industry (various industries), agriculture and motor vehicles.
Emissions of enterprises in the atmosphere
The largest "suppliers" of various pollutants in the air pool are metallurgical and energy enterprises, chemical production, construction industry, mechanical engineering.
In the process of burning fuel of various types of energy complexes, large quantities of sulfur arhydride, carbon and nitrogen oxides, soot are highlighted in the atmosphere. Also in emissions (in smaller quantities) there are a number of other substances, in particular hydrocarbons.
The main sources of dust-gas emissions in the metallurgical production are melting furnaces, casting plants, fragrances, agglomeration machines, crushing equipment, unloading-loading materials, etc. The largest share among the total amount of substances entering the atmosphere, carbon monoxide, dust, sulfur anhydride occupy, nitrogen oxide. In some smaller quantities, manganese, arsenic, lead, phosphorus, mercury pairs, etc. Also in the process of steel-smelting production emissions to the atmosphere contain vapor-gas mixtures. They include phenol, benzene, formaldehyde, ammonia and a number of other hazardous substances.
Harmful emissions into the atmosphere from the industry, despite small volumes, are of particular danger to the natural environment and humans, since they are characterized by high toxicity, concentration and considerable diversity. The mixtures arriving in the air depending on the type of products produced may be in their composition volatile organic compounds, fluorine compounds, nitrous gases, solids, chloride compounds, hydrogen sulfide, etc.
In the production of building materials and cement, emissions into the atmosphere contain significant amounts of different dust. The main technological processes leading to their formation are grinding, the processing of the charge, semi-finished products and products in hot gas streams, etc. Around factories producing various building materials, areas of contamination by a radius up to 2000 m are characterized by a high concentration in the air of dust containing Particles of plaster, cement, quartz, as well as a number of other pollutants.
Emissions of motor vehicles
In major cities, a huge number of pollutants in the atmosphere comes from motor vehicles. According to different estimates, they are from 80 to 95%. Consist of a large number of toxic compounds, in particular nitrogen and carbon, aldehydes, hydrocarbons, etc. (about 200 compounds).
The greatest volumes of emissions are noted in the location of traffic lights and intersections, where cars are moving at low speed and in idle mode. The calculation of emissions into the atmosphere shows that hydrocarbons are also the main components of the exhaust.
It should be noted that, unlike stationary emission sources, the operation of vehicles leads to air pollution on urban streets at the height of human growth. As a result of the harmful effects of pollutants, pedestrians, residents located at the roads of houses are subjected to, as well as growing vegetation in the surrounding territories.
Agriculture
Influence on man
According to various sources, there is a direct link between air pollution and a number of diseases. For example, the duration of the flow of respiratory diseases in children who live in relatively polluted areas, 2-2.5 times more than those who live in other areas.
In addition, in cities characterized by an unfavorable environmental situation, in children there are functional deviations in the system of immunity and blood formation, violations of compensatory adaptation mechanisms to the conditions of the external environment. Many studies also identified the relationship between air pollution and mortality.
The main components of emissions entering the air from various sources are suspended substances, nitrogen oxides, carbon and sulfur. It was revealed that zones with an exceedment of PDC on NO 2 and CO cover up to 90% of urban area. The above emissions are capable of cause serious diseases. The accumulation of these pollution leads to damage to the mucous membranes of the upper respiratory tract, the development of pulmonary diseases. In addition, the elevated concentrations of SO 2 may cause dystrophic changes in the kidneys, liver and heart, and NO 2 - toxicosis, congenital anomalies, heart failure, nerve disorders, etc. Some studies have identified the relationship between the incidence of lung cancer and concentrations of SO 2 and NO 2 in the air.
conclusions
Pollution of the environment and, in particular, the atmosphere, has adverse effects of health not only of this, but also subsequent generations. Therefore, it can be safely argued that the development of measures aimed at reducing emissions of harmful substances into the atmosphere is one of the most relevant problems of humanity.
GOST R 56167-2014
National Standard of the Russian Federation
Emissions of pollutants in the atmosphere
Method for calculating damage from an industrial enterprise environmental objects
Air Pollution Emissions. Method of Prejudice Calculation from Industrial Enterprise Environment Objects
OX 13.020.01
13.040.01
Date of introduction 2015-07-01
Preface
Preface
1 Developed by an open joint-stock company "Research Institute for Protection of Atmospheric Air"
2 Submitted by the Technical Committee on Standardization of TC 409 "Protection of the Environmental Environment"
3 approved and commissioned by the Order of the Federal Agency for Technical Regulation and Metrology of October 14, 2014 N 1325-ST
4 introduced for the first time
5 reprint. October 2019
The rules for applying this standard are established inarticle 26 of the Federal Law of June 29, 2015 N 162-FZ "On Standardization in the Russian Federation" . Information on the changes to this standard is published in the annual (as of January 1 of the current year) the information indicator "National Standards", and the official text of the amendments and amendments - in the monthly information indicator "National Standards". In case of revision (replacement) or the cancellation of this standard, the appropriate notification will be published in the nearest issue of the monthly information indicator "National Standards". Relevant information, notification and texts are also posted in the public information system - on the official website of the Federal Agency for Technical Regulation and Metrology on the Internet (www.gost.ru)
1 area of \u200b\u200buse
This standard establishes the method of calculating the damage caused by emissions of pollutants of a particular industrial enterprise with environmental facilities, environmental systems, building structures, monuments and agricultural crops.
This standard is intended for employees of enterprises environmental protection units, specialists of research, design and other organizations dealing with environmental air protection issues, as well as bodies and services for the protection of the Environment of cities and regions of Russia.
2 Regulatory references
This standard uses regulatory references to the following standards:
GOST ISO / IEC 17025 General requirements for the competence of test and calibration laboratories
________________
GOST ISO / IEC operates 17025-2019.
GOST R 8.563 State system for ensuring unity of measurements. Methods (methods) measurements
Note - When using this standard, it is advisable to check the action of reference standards in the public information system - on the official website of the Federal Agency for Technical Regulation and Metrology on the Internet or on the National Standards Annual Information Signal, which is published as of January 1 of the current year, and on issues of the monthly information pointer "National Standards" for the current year. If the reference standard is replaced, to which the undated link is given, it is recommended to use the current version of this standard, taking into account all changes made to this version. If the reference standard is replaced by a dated reference, it is recommended to use the version of this standard with the above-mentioned approval (adoption). If, after approval of this standard in the reference standard, to which the dated reference is given, the change has been made affecting the provider to which the link is given, this provision is recommended to be applied without taking into account this change. If the reference standard is canceled without replacement, the position in which the reference is given to it is recommended to be applied in a portion that does not affect this link.
3 General provisions
3.1 This standard applies to the following main types of damage caused by the environment:
- contamination of atmospheric air with organized emissions of pollutants from stationary sources of pollution;
- Pollution of atmospheric air by unorganized emissions of pollutants from stationary contamination sources.
3.2 Collecting the data necessary to determine the calculation of damage caused by emissions of pollutants of a particular enterprise to environmental facilities, environmental systems, building structures, monuments and agricultural cultures and design results are carried out in conjunction with specialized organizations, certified and (or) accredited in the prescribed manner, and Also recent research institutes.
3.3 Exceeding established pollutant emission standards are set by the following methods:
- by the instrumental method based on measurements of the parameters of emissions of pollutants performed by the analytical laboratory, the technical competence of which meets the requirements of GOST ISO / IEC 17025 according to the methods that have passed the metrological certification in accordance with the requirements of GOST R 8.563;
- settlement method on the basis of methods for calculating emissions of pollutants into the atmosphere recommended for use during the rationing and determining the amount of emissions of pollutants into atmospheric air.
3.4 The fact of exceeding the norm of one-time emission of the pollutant at the source of contamination is considered established if the difference between the actual power of one-time emissions of this pollutant, taking into account the error of its measurement exceeds the maximum allowable value.
3.5 The costs needed to determine the amount of damage are determined on the basis of data on the value of the main types of work and (or) on the basis of data on actually produced costs to determine the amount of damage caused.
The expenditures necessary to assess the damage include the costs of the following work:
- sampling and conducting laboratory tests of the content of components in samples;
- assessment of the propagation of pollutants in atmospheric air;
- Drawing up for the fulfillment of work to eliminate damages and its consequences;
- Conduct damage and loss counting;
- Conducting other types of work, the execution of which is associated with damage assessment and account counting.
4 Procedure for calculating damage
4.1 Determination of the amount of emissions of pollutants into atmospheric air
4.1.1 In the presence of permission for emissions of pollutants into atmospheric air in a stationary source of contamination, the amount of emission of a pollutant in tons is calculated by the formula
where - the value of the emission of the pollutant, established at the time of control over compliance with the established emission standards; Determine the instrumental method, g / s;
- the magnitude of the value of the permissible emission of the pollutant established in the permission for the emission of pollutants of the enterprise [maximum allowable emission, the release limit (temporarily consistent emission)], g / s;
- the duration of the emission of a pollutant from the moment of detection and to the discontinuation of the emission, h;
An example of calculation is given in Appendix A.
4.1.2 In the absence of permission for emissions of pollutants into atmospheric air, the amount of emission of a pollutant in tons is calculated by the formula
where - the value of one-time emission of the pollutant, established at the time of control over compliance with the established emission standards, g / s;
- the duration of the emission of the pollutant since the emission is detected and before its termination, h;
278 - Coefficient of recalculation of grams in tons and seconds in hours.
4.1.3 In case of malfunction or non-use (disconnection) of the sewage settings, the calculation of the emission values \u200b\u200bof the pollutants is carried out according to 6.1 or in the input characteristics specified in the passport to a particular gas cleaning. The fault of the cleaning settings is equal to their non-working state.
4.1.4 In case of emergency emissions of pollutants (emissions carried out by emergency situations), the amount of pollutant is determined as the value of the pollutant emission by formula (2) or as a value of the pollutant emission set by the calculated way based on the characteristics of the technological equipment and the situation of the situation settings In the accounting documentation of the nature user in case of its maintenance, as well as taking into account the duration of emissions.
4.1.5 The duration of the pollutant emission, including the emergency, is determined from the moment of detection until the end of the emission.
The moment of the start of the emission is determined by the establishment of the fact of supernorumative emissions in the following documents:
- in the act of inspection check;
- in the protocol of analytical survey of air samples.
Note - In the act of inspection, the inspection indicates information on the observance of environmental requirements in the field of environmental protection during placement, construction, reconstruction, commissioning, operation, conservation and liquidation of buildings, structures and other objects.
The moment of the end of the emission is considered to be the registration date in the executive authority, carrying out public administration in the field of environmental protection, the report on the elimination of violations that led to damage, with the provision of the results of an analytical study of the air ambulance air conducted at the same points where previously identified Facts of violations listed in 4.1.
In the case of re-establishing the fact of damage (detecting excessive emissions), the end of the emission is established according to the laboratory attracted by the executive authority exercising public administration in the field of environmental protection, and the emission duration is determined since its initial detection.
5 Calculation of damage caused by emissions of pollutants of the industrial enterprise
5.1 Calculation of damage, in rubles caused by emissions of pollutants of a particular enterprise with environmental objects, environmental systems, building structures, monuments and agricultural crops, are calculated by the formula
where - the specific gravity costs and (or) neutralization of the substance is calculated by formula (4), rubles / t;
- pollutant;
- the number of pollutants contained in emissions of pollutants into atmospheric air;
- the amount of the pollutant determined by formulas (1) and (2) for each polluting substance, T;
- The costs needed to determine the amount of damage, rub.
5.2 Calculation of specific gravity costs and (or) neutralization -o substance, in rubles per ton, calculated by the formula
where - the cost of purchasing and installing equipment for catching and (or) the disposal of the pollutant, determined at market prices for similar cleaning equipment, which is used or should be used on the source, and installation of equipment, RUB;
- the mass of the pollutant, captured by the sewage equipment for the year, t.
5.3 In the presence of sewage equipment intended for cleaning air from several pollutants at the same time, the calculation of the specific costs of capturing and (or) the neutralization of the substance contained in emissions in rubles per ton is calculated by the formula
where - the cost of acquiring and installing equipment intended for air purification from several pollutants at the same time, determined at market prices to similar cleaning equipment, which is used or should be used on the source, and installation of equipment, rub.;
- the number of pollutants captured by the cleaning equipment simultaneously;
- the mass of the pollutant substance captured by the sewage equipment intended for cleaning air from several pollutants at the same time, T;
- coefficient of bringing the mass of pollutant to conventional tons, taking into account its relative danger, calculated by the formula
where is the maximum permissible concentration of the pollutant.
5.4 In the absence of data on market prices on similar cleaning equipment, which is used or should be used at the source, the calculation of damage caused by the pollution of atmospheric air by stationary sources of pollution, in rubles, calculated by the formula
where is the coefficient to calculate the amount of damage caused by emissions of pollutants depending on the industry to which the industrial enterprise belongs to the table B.1 of the application b, rubles / t;
- the mass of the pollutant, determined by formulas (1) and (2) for each polluting substance, T;
- an indicator that takes into account inflation calculated by formula (8);
- the cost of establishing the fact of damage and assess the size of the negative impact, calculated by the formula (9), rubles;
- pollutant;
- the number of pollutants contained in emissions of pollutants into atmospheric air.
An example of calculating the damage caused by the pollution of atmospheric air by stationary sources of contamination, is given in Appendix A.
where is the inflation rate set at the federal level for the year of the calculus of damage.
where - the cost of sampling and carrying out laboratory tests of the content of components in samples, taking into account overhead, rubles;
- costs associated with determining the amount of damage, rubles;
- costs of assessing the spread of pollutants in atmospheric air and their subsequent effect on the population, the main funds, related industries, rubles;
- costs associated with the calculations, rubles;
- Other costs, rub.
Appendix A (Reference). An example of calculating the extensive hydrocarbon emission and determining the amount of damage caused by a stationary source of pollution
Appendix A.
(Reference)
A.1 At the enterprise, over 30 days, an excessive emission of hydrocarbons (benzene, toluene, xylol, ethylbenzene and phenol) was carried out in a stationary source.
In accordance with 4.1, the calculation of the extensive emission of hydrocarbons according to formula (1) is calculated as follows:
Thus, in 30 days in atmospheric air, 6,9045 tons of pollutants were released.
A.2 In accordance with 5.4, the calculation of the calculation of the amount of damage caused by a stationary source of contamination by formula (7) is performed as follows, while the costs are taken equal to zero
Thus, the amount of damage caused by emissions of pollutants of a particular enterprise with environmental facilities, environmental systems, building structures, monuments and agricultural crops, excluding costs is equal to 1191026.2 rubles.
Appendix B (mandatory). Coefficients for calculating the amount of damage caused by emissions of pollutants depending on the industry
Appendix B.
(mandatory)
Table B.1 - the coefficient for calculating the amount of damage caused by emissions of pollutants depending on the industry to which the industrial enterprise belongs, in thousands of rubles for 1 t
Industries, production | Weighted | Group of pollutants |
|||||
Carbohydrated | Hazard I grade | Other substitute |
|||||
Ferrous metallurgy | |||||||
Non-ferrous metallurgy | |||||||
Machinery, metalworking production | |||||||
Autostructuring (including enterprises for repair and maintenance of motor vehicles) | |||||||
Radio electronic production | |||||||
Oil refining production (including gas station) | |||||||
Chemical and petrochemical production | |||||||
Production of rubber products | |||||||
Chemical and Pharmaceutical and Perfume Production | |||||||
Glass and ceramic production | |||||||
Production of synthetic resins and products from them | |||||||
Food industry | |||||||
Production of tobacco products | |||||||
Textile and weaving production | |||||||
Ferrous metallurgy | |||||||
Woodworking and pulp and paper production | |||||||
Furniture manufacture | |||||||
Printing production | |||||||
Production of building materials and asphalt | |||||||
Burning garbage | |||||||
Energy facilities (boiler rooms, CHP, thermal stations, etc.) | |||||||
Other industries | |||||||
* Other substances include the remaining contaminants for which the maximum permissible concentration values \u200b\u200bor indicative safe levels of influences (shoes) in the atmospheric air of populated areas are installed. |
Bibliography
UDC 504.054: 504.3.054: 006.354 | OX 13.020.01 |
Keywords: emissions of pollutants, atmosphere, damage, industrial enterprises, environment |
Electronic document text
prepared Codex JSC and drilled by:
official edition
M.: Standinform, 2019
In the overwhelming majority of modern technological processes, various contaminants are emitted into atmospheric air. At the same time, the sources of contamination of the atmosphere (IZA) can be organized or unorganized. According to the Federal Law "On Environmental Protection", environmental standards for atmospheric air quality are established - maximum permissible concentrations of polluting air substances.
Organized sources of pollutant emissions (pipes, ventilation mines, aeration lights) are contributed to the main contribution to the pollution of the atmosphere, so we pay major attention.
The problem of normalizing emission emissions is to establish for each source of the atmosphere pollution such a limit emission value so that in the surface layer of the atmosphere, the concentration of any substance that emitted to them has not exceeded the MPC values.
Consider one organized source of pollution of the atmosphere - the smoke tube of the boiler room. It is known that when burning organic fuels (natural gas, coal, firewood, fuel oil, etc.) in the composition of flue gases contain various SL:
1. Natural gas: carbon monoxide, nitrogen oxides.
2. Coal: solid particles (ash), carbon monoxide, nitrogen oxide, benzapine, sulfuric anhydride.
3. Mazut: solid particles (fuel oil oola), carbon monoxide, nitrogen oxides, sulfuric anhydride.
The chimney is characterized by a number of parameters: a height, a diameter of the mouth, the volumetric flow rate of flue gases, their temperature. All these parameters affect the dispersion of emissions in the atmosphere.
In addition, it is necessary to know the value of the mass ejection of each SN, g / s.
The smoke jet, falling out of the pipe into the atmosphere, is demolished in the wind, and at the same time, it dissipates, in horizontal and vertical directions. The dispersion process is highly dependent on the nature of atmospheric diffusion, and it, in turn, from currently currently meteorological conditions. The process of dispersion of impurities is influenced by wind speed, its distribution with a height, vertical temperature, the nature of the underlying surface, the nature of the terrain.
There are also regional peculiarities of atmospheric diffusion processes, all these and other factors are taken into account in the mathematical model of impurities.
If you depict the process of surface concentration on the chart as it removes from the pipe, then the characteristic curve shown in Fig.3.1.
GK "Effective Safety"- Conducting and registration of the calculation of standards for permissible emissions of pollutants in Moscow, Moscow Region, Kazan and the Republic of Tatarstan. The optimal price, optimal quality.
Cost: OT 20 000
rubles. Development time: from 20 working days. Duration: 7 years.
Calculation of permissible emission standards (NDV) - The document in which is calculated for a certain object of negative impact on the environment (onvos) permissible norms of emissions of a harmful (pollutant) substance into atmospheric air, which is defined as the volume or mass of chemical or a mixture of chemicals, microorganisms, other substances, as an indicator of activity Radioactive substances allowed to emissions into atmospheric air by a stationary source and (or) a set of stationary sources, and subject to compliance with the requirements of atmospheric air protection.
In accordance with paragraph 2 of Article 22 of the Federal Law of January 10, 2002 No. 7-FZ (as amended by 29.07.2018), "On Environmental Protection", the calculation of the standards of permissible emissions, permissible discharge standards is made by legal entities and individual entrepreneurs who are planning the construction of objects I and II categories of NVOS (when assessing environmental impact), as well as carrying out economic and (or) other activities at facilities of category II.
Also, paragraph 4 of Article 22 of the Federal Law of January 10, 2002 No. 7-FZ (as amended by 29.07.2018), "On Environmental Protection" establishes the obligation to calculate the standards of permissible emissions of substances 1 and 2 hazard classes for objects III NVOS categories.
Clause 1 of Article 30 of the Federal Law of 04.05.1999 No. 96-FZ (as amended by 29.07.2018), "On Protection of Atmospheric Air" obliges legal entities and individual entrepreneurs to ensure the development of extremely permissible emissions and maximum permissible standards of harmful physical Impact on atmospheric air.
Content of calculation of values \u200b\u200bof permissible emissions
Due to the lack of special requirements for the registration of the calculation of standards for permissible emissions of pollutants into the atmosphere, the requirements are taken as prescribed by "recommendations for the design and content of the draft standards for the maximum permissible emissions into the atmosphere", approved. Goskomgidromet of the USSR 28.08.1987. and a methodological manual for calculating, rationing and controlling emissions of pollutants into atmospheric air, the "atmosphere" of 2012. The volume and content of the calculation of emission standards in each individual case is determined by the activities of the enterprise and the characteristics of emission sources. The calculation of the NDV includes the following sections:
Section 1. Brief description of the enterprise;
Section 2. Characteristics of the enterprise as an atmosphere pollution source:
Brief description of technological equipment and technological processes;
A list of harmful substances emitted into the atmosphere;
Section 3. Calculations of air pollution and proposals for DV regulations for emission sources:
Determination of emission sources and harmful substances subject to rationing;
Preliminary analysis of the effect of emissions of pollutants on pollution of the surface layer of the atmosphere;
Detailed calculations of dissipating pollutants in atmospheric air using specialized programs (refrigeration);
Proposals for NDV to atmospheric air for the ONVOS object.
Stages of calculating the standards of permissible emissions
The main stages on the calculation of the standards of permissible emissions of pollutants into the atmosphere are:
- Assessment of the cost, drawing up a contract and payment of the account;
Primary consultation, in the course of which our specialist clarify information about your organization, namely: the scope of activities, the number of objects and sources, the location of them, the presence of permission for the emission of pollutants and the previous project, or the current inventory of sources and emissions of pollutants. If you have a previous project, you need to clarify what changes occurred during the action of this project;
Collection of information;
Departure of specialists in order to conduct if necessary;
Carrying out laboratory measurements of emissions (for organized emission sources);
Calculation of dispersion;
Evaluation of the information received;
Registration of calculation of standards of permissible emissions.
Legislation
- Federal Law of January 10, 2002 No. 7-FZ "On Environmental Protection";
- Federal Law of May 4, 1996 No. 96-FZ "On Protection of Atmospheric Air";
- GOST 17. 2. 3.02-78 "Nature Protection. Atmosphere";
- Letter of the Ministry of Environment of Russia dated 29.03.2012 N 05-12-47 / 4521 "Methodological manual for calculation, rationing and control of emissions of pollutants into the atmosphere" (Augmented and processed), OJSC "Nii atmosphere", C-PB , 2012;
- Recommendations for the design and content of the draft standards of maximum permissible emissions to the atmosphere (PDV) for the enterprise, approved. State Committee of the USSR 28.08.1987;
- Order of the Ministry of Extraction and Natural Resources of the Republic of Tatarstan of 20.04.2012 N 143-P "On approval of the administrative regulations of the Ministry of Ecology and Natural Resources of the Republic of Tatarstan providing a state service for issuing permits for emissions of harmful (pollutant) substances to atmospheric air in stationary sources"
- Decree of the Government of the Russian Federation of March 2, 2000 No. 183 "On the standards of emissions of harmful (pollutants) into atmospheric air and harmful physical impacts on it";
- Order of the Ministry of Natural Resources and Ecology of the Russian Federation of 29.09.2015 No. 414 "On approval of the Administrative Regulations of the Federal Service for Supervision of Nature Management on the provision of a state service to establish maximum allowable emissions and temporarily agreed emissions"
- Order of the Ministry of Environment of Russia dated December 26, 2016 No. 674 "On approval of methods for calculating the dispersion of emissions of harmful (polluting) substances in atmospheric air"
Questions and answers
Question number 1. Our company has an excess of the maximum permissible concentration (MPC) in two substances as part of emissions. How should we do in this situation?
In this situation, it is necessary to develop a similar project PDV, but there are some differences. First, in case of exceeding the MPC, permission to emissile pollutants into atmospheric air is issued for a period of no more than 1 year. Secondly, the prerequisite is the development and coordination of the plan of measures to reduce (reduce emissions) and the delivery of the report on the implementation of this plan. In case of non-fulfillment of the approved plan, there are raising coefficients for payments for the negative impact on the environment - 100 times.
Temporarily agreed emissions (VV) - temporary release limit, which is established for existing stationary emission sources, taking into account the quality of atmospheric air and the socio-economic conditions for the development of the relevant territory in order to step up achieving the established maximum permissible emission (Federal Law of 04.05.1999 N 96-FZ ).
Question number 2. Can we independently conduct an inventory of emissions?
If you have carcinogenic factors at the enterprise, then you need a passport.
Yes of course. But it should be noted that the final stage of the inventory is to perform measurements of emissions of harmful substances into the air. Measurements and emission analysis can only be carried out by an accredited laboratory.
Some time ago, we were faced with a problem in the development of the PDV project, namely, an inventory was carried out by the employees of the enterprise and a third-party laboratory, in the process of which the types of emission sources were not fully indicated (inorganized sources turned into organized) and their location. In this regard, we had to independently conduct an inventory and make changes to the developed draft PDV.
Tags:NDV, standards for permissible emissions, PDV, draft standards for maximum allowable emissions, standards for extreme-permissible emissions, emissions to atmospheric air, emissions of pollutants into atmospheric air, emission standards, calculation of emission standards, pollutants, atmospheric air