Hair care 

Waste disposal site monitoring program. Monitoring of the state of the environment at waste disposal sites. Requirements for reporting documentation on environmental monitoring

On June 23, 2016, the Procedure for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment came into force by the owners of waste disposal facilities, as well as persons who own or use waste disposal facilities, approved by the Order of the Ministry of Natural Resources of Russia dated March 4, 2016 No. 66.

In accordance with paragraph 3 of Article 12 of the Federal Law of June 24, 1998 No. 89-FZ, on the territories of waste disposal facilities and within the limits of their impact on the environment, the owners of waste disposal facilities, as well as persons in whose possession or use there are waste disposal facilities, required to monitor state of the environment in accordance with the procedure established by the federal executive authorities in the field of waste management in accordance with their competence.

Types of impact of the waste disposal facility on the environment

The effect of the Monitoring Procedure does not apply to monitoring the state and pollution of the environment at the following facilities:

  • waste disposal facilities decommissioned (including reclaimed or mothballed) in accordance with the established procedure;
  • waste disposal facilities located in territories whose use for waste disposal is prohibited by the legislation of the Russian Federation
  • special radioactive waste disposal facilities;
  • cattle burial grounds;
  • medical waste disposal facilities.

The monitoring order is intended to be used:

  • owners of waste disposal facilities;
  • persons who own or use waste disposal facilities;
  • Rosprirodnadzor and its territorial bodies;
  • other state authorities, local authorities, legal entities and individuals interested in obtaining data on the state and pollution of the environment in the areas where waste disposal facilities are located.

Monitoring carried out by owners, owners of objects waste disposal, in the event that they directly operate such facilities, or by persons in use, the operation of which are waste disposal facilities in accordance with the requirements in the field of hydrometeorology and related fields. To organize work to monitor the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment, assess and forecast changes in its state by persons operating waste disposal facilities, a monitoring program is being developed the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment.

The monitoring program is approved by the person operating the waste disposal facilities and sent on paper in a notifying manner to the territorial body of Rosprirodnadzor at the location of the waste disposal facility or sent by post with a list of attachments and with a return receipt.

The monitoring program can be submitted in the form of an electronic document signed with a simple electronic signature in accordance with the requirements of the Federal Law of April 6, 2011 No. 63-FZ "On Electronic Signature". The monitoring program is developed based on the available data on the state and pollution of the environment on territory of the waste disposal facility and within its impact on the environment.

At the same time, at the discretion of persons operating waste disposal facilities, the following can be used:

  • data of the section "List of measures for environmental protection", which is part of the design documentation of the facility associated with the disposal of waste of I-V hazard class, and materials for assessing the impact of the waste disposal facility on the environment;
  • stock data of observations of the state and pollution of the environment in the area of ​​the location of the waste disposal facility and within the limits of their impact on the environment;
  • data on the background state of the environment in the area where the waste disposal facility is located;
  • available to persons operating waste disposal facilities, observational data on the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment;
  • materials of previously conducted environmental surveys on the territory of the waste disposal facility and within its impact on the environment.

When developing a monitoring program, the following are taken into account:

  • design characteristics (technical features) of the waste disposal facility;
  • origin, types, quantity and hazard classes of the disposed waste;
  • physical and geographical conditions in the area where the waste disposal facility is located;
  • geological and hydrogeological conditions in the area of ​​the waste disposal facility.

Requirements for the composition and content of the monitoring program:

The results of monitoring the state and pollution of the environment in the territories of waste disposal facilities and within the limits of their impact on the environment are drawn up in the form of reports.

Reports on the results of monitoring in a notification procedure are submitted to the territorial body of Rosprirodnadzor at the location of the waste disposal facility annually until January 15 of the year following the reporting one. The monitoring results report is drawn up in two copies. One copy is kept by the person operating this waste disposal facility, and the second copy, together with the electronic version of the report on magnetic media, is sent by post to the territorial agency of Rosprirodnadzor at the location of the waste disposal facility (clause 6 of the Monitoring Procedure).

Requirements for the composition and content of the monitoring report:

According to paragraphs 6.6 - 6.8 of SP 2.1.7.1038-01 "Hygienic requirements for the arrangement and maintenance of landfills for municipal solid waste", the production control system should include devices and structures for monitoring the state of ground and surface water, atmospheric air, soil, levels noise in the zone of possible influence of the landfill.

In agreement with the authorized federal executive authorities and other regulatory bodies, control over the state of groundwater is carried out, depending on the depth of their occurrence, pits, wells or boreholes are designed in the green zone of the landfill and outside the sanitary protection zone of the landfill. The control facility is laid upstream of the landfill along the groundwater flow in order to take samples of water, which is not affected by the leachate from the landfill.

Above the landfill and below the landfill on drainage ditches, surface water sampling sites are also designed.

The content of ammonia, nitrites, nitrates, bicarbonates, calcium, chlorides, iron, sulfates, lithium, COD, BOD, organic carbon, pH, magnesium, cadmium, chromium, cyanides, lead, mercury, arsenic, copper, barium, dry residue, samples are also examined for helminthological and bacteriological indicators. If in the samples taken downstream a significant increase in the concentrations of analytes compared to the control is established, it is necessary, in agreement with the regulatory authorities, to expand the scope of the determined indicators, and in cases where the content of the analytes exceeds the MPC, it is necessary to take measures to limit the intake pollutants into groundwater up to the MPC level.

The production control system should include constant monitoring of the state of the air environment. To this end, it is necessary to quarterly analyze atmospheric air samples above the exhausted areas of the landfill and at the border of the sanitary protection zone for the content of compounds that characterize the process of biochemical decomposition of MSW and pose the greatest danger. The volume of indicators to be determined and the frequency of sampling are substantiated in the project for the production control of landfills and agreed with the regulatory authorities.

note

Order of the Ministry of Natural Resources of Russia dated 04.03.2016 No. 66
"On the procedure for the owners of waste disposal facilities, as well as persons in whose possession or use of the waste disposal facilities, to monitor the state and pollution of the environment on the territories of the waste disposal facilities and within the limits of their impact on the environment"
(Registered in the Ministry of Justice of Russia on June 10, 2016 No. 42512)

1. General Provisions

Clause 4. The monitoring procedure is intended for use by the owners of waste disposal facilities, as well as by persons who own or use waste disposal facilities, the Federal Service for Supervision of Natural Resources (hereinafter referred to as Rosprirodnadzor) and its territorial bodies, the Federal Service for Hydrometeorology and monitoring of the environment and its territorial bodies and subordinate organizations, other state authorities, local governments, legal entities and individuals interested in obtaining data on the state and pollution of the environment in the areas where waste disposal facilities are located.
Monitoring of the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment is carried out by the owners, owners of waste disposal facilities, in the event that they directly operate such facilities, or by persons who use and operate waste disposal facilities (hereinafter - persons operating waste disposal facilities) in accordance with the requirements in the field of hydrometeorology and related fields.

"GOST R 56059-2014. National standard of the Russian Federation. Industrial environmental monitoring. General provisions"
(approved and put into effect by the Order of Rosstandart dated July 9, 2014 No. 708-st)

p.4.8 Ecological and analytical measurements are included in the scope of state regulation of ensuring the uniformity of measurements and state regulation in the field of hydrometeorology and environmental monitoring, which determines the need to comply with the established requirements of the system for ensuring the uniformity of measurements in accordance with GOST R 8.589-2001, , and requirements in the field hydrometeorology and environmental monitoring.
Environmental analytical measurements can be carried out only own or involved laboratories accredited to carry out the necessary measurements in accordance with the current legislation of the Russian Federation and licensed to operate in the field of hydrometeorology and related areas (with the exception of the specified activities carried out in the course of engineering surveys performed for the preparation of project documentation, construction, reconstruction of capital construction).

contact us

TsLATI in the Omsk region, is one of the leading analytical laboratories offering a full range of environmental monitoring services at waste disposal sites, providing fast, comprehensive, accurate, affordable research for industrial, engineering/consulting and government clients throughout Omsk and the Omsk region.

For details or for Application for TsLATI services in the Omsk region, contact us by contact number in Omsk +7 (381-2) 23-77-86

On the Procedure for the owners of waste disposal facilities, as well as persons in possession or use of which the waste disposal facilities are located, to monitor the state and pollution of the environment on the territories of the disposal facilities ...

MINISTRY OF NATURAL RESOURCES AND ENVIRONMENT OF THE RUSSIAN FEDERATION

ORDER


In accordance with subparagraph 5.2.62 of the Regulations on the Ministry of Natural Resources and Ecology of the Russian Federation, approved by Decree of the Government of the Russian Federation of November 11, 2015 N 1219 (Collected Legislation of the Russian Federation, 2015, N 47, Art. 6586; 2016, N 2, Art. 325),

I order:

1. Approve the attached Procedure for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment by the owners of waste disposal facilities, as well as persons in possession or use of which the waste disposal facilities are located.

2. Paragraph 8 of the attached Procedure for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment by the owners of waste disposal facilities, as well as persons in possession or use of which the waste disposal facilities are located, shall enter into force from January 1, 2018.

Minister
S.E. Donskoy

Registered
at the Ministry of Justice
Russian Federation
June 10, 2016,
registration N 42512

The procedure for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment

I. General provisions

1. The procedure for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment (hereinafter referred to as the Monitoring Procedure) by the owners of waste disposal facilities, as well as persons in whose possession or use of which waste disposal facilities are located, establishes requirements for the organization and implementation of observations of the state and pollution of the environment in the territories of waste disposal facilities and within the limits of their impact on the environment, assessment and forecast of changes in its state, as well as requirements for formalizing and presenting the results obtained.

2. Monitoring of the state and pollution of the environment in the territories of waste disposal facilities and within the limits of their impact on the environment is part of the system for monitoring the state and pollution of the environment, assessing and forecasting changes in its state under the influence of waste disposal facilities and is carried out in order to prevent, reduction and elimination (reduction) of negative changes in the quality of the environment, informing public authorities, local governments, legal entities and individuals about the state and pollution of the environment in the areas where waste disposal facilities are located.

The territory within the limits of the impact of waste disposal facilities on the environment is determined on the basis of the standards of permissible environmental impact approved in accordance with the established procedure.

3. The effect of the Monitoring Procedure does not apply to the monitoring of the state and pollution of the environment at the following facilities:

waste disposal facilities decommissioned (including reclaimed or mothballed) in accordance with the established procedure;

waste disposal facilities located in territories whose use for waste disposal is prohibited by the legislation of the Russian Federation;

special radioactive waste disposal facilities;

cattle burial grounds;

medical waste disposal facilities.

4. The monitoring procedure is intended for use by the owners of waste disposal facilities, as well as by persons who own or use waste disposal facilities, the Federal Service for Supervision of Natural Resources (hereinafter referred to as Rosprirodnadzor) and its territorial bodies, the Federal Service for Hydrometeorology and Monitoring of the environment and its territorial bodies and subordinate organizations, other state authorities, local authorities, legal entities and individuals interested in obtaining data on the state and pollution of the environment in the areas where waste disposal facilities are located.

Monitoring of the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment is carried out by the owners, owners of waste disposal facilities, in the event that they directly operate such facilities, or by persons who use and operate waste disposal facilities (hereinafter - persons operating waste disposal facilities) in accordance with the requirements in the field of hydrometeorology and related fields.

5. In order to organize work to monitor the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment, to assess and predict changes in its state by persons operating waste disposal facilities, a program for monitoring the state and pollution of the environment on the territory waste disposal facility and within its impact on the environment (hereinafter referred to as the monitoring program).

The monitoring program is approved by the person operating the waste disposal facilities and sent on paper in a notifying manner to the territorial body of Rosprirodnadzor at the location of the waste disposal facility or sent by post with a list of attachments and with a return receipt.

The monitoring program can be submitted in the form of an electronic document signed with a simple electronic signature in accordance with the requirements ; 2013, N 14, item 1668; N 27, item 3463; item 3477; 2014, N 11, item 1098, N 26, item 3390; 2016, N 1, item 65).

6. The results of monitoring the state and pollution of the environment in the territories of waste disposal facilities and within the limits of their impact on the environment are drawn up in the form of reports that are compiled by persons operating these waste disposal facilities and submitted to the territorial body of Rosprirodnadzor at the location of the facility in a notification manner. waste disposal annually until January 15 of the year following the reporting year. The report on the results of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within the limits of their impact on the environment (hereinafter referred to as the report on the results of monitoring) is drawn up in two copies, one copy of which is kept by the person operating this waste disposal facility, and the second a copy, together with an electronic version of the report on magnetic media, is sent by post to the territorial body of Rosprirodnadzor at the location of the waste disposal facility in a notification manner.

The monitoring results report can be submitted in the form of an electronic document signed with a simple electronic signature in accordance with the requirements of Federal Law No. 63-FZ of April 6, 2011 "On Electronic Signature".

7. In the cases provided for by paragraph 7 of Article 23 of Federal Law No. 89-FZ of June 24, 1998 "On Production and Consumption Waste" (Sobraniye Zakonodatelstva Rossiyskoy Federatsii, 1998, No. 26, Art. 3009; 2001, No. 1, Art. 21 ; 2003, N 2, item 167; 2004, N 35, item 3607; 2005, N 19, item 1752; 2006, N 1, item 10; N 52, item 5498; 2007, N 46, item .5554; 2008, N 30, item 3616; N 45, item 5142; 2009, N 1, item 17; 2011, N 30, item 4590, item 4596, N 45, item 6333, N 48 , Art. 6732; 2012, N 26, Art. 3446, N 27, Art. 3587, N 31, Art. 4317; 2013, N 30, Art. 4059, N 43, Art. ; 2014, N 30, article 4220, article 4262; 2015, N 1, article 11, article 38, N 27, article 3994, N 29, article 4350, 2016, N 1, article 12, 24), reports on the results of monitoring the state and pollution of the environment in the territories of waste disposal facilities and within the limits of their impact on the environment are used to confirm the exclusion of the negative impact of waste disposal facilities on the environment.

8. In relation to waste disposal facilities equipped with automatic means for measuring and recording the volume or mass of pollutant emissions, pollutant discharges and concentrations of pollutants, as well as technical means for recording and transmitting information on the volume and (or) mass of pollutant emissions, discharges pollutants and on the concentration of pollutants in the state data fund of state environmental monitoring (state environmental monitoring) in accordance with the requirements of Article 67 of the Federal Law of 10.01.2002 N 7-FZ "On Environmental Protection" (Collected Legislation of the Russian Federation, 2002, No. 2, item 133; 2004, N 35, item 3607; 2005, N 1, item 25; N 19, item 1752; 2006, N 1, item 10; N 52, item 5498; 2007, No. 7, article 834; No. 27, article 3213; 2008, No. 26, article 3012; No. 29, article 3418; No. 30, article 3616; 2009, No. 1, article 17; No. 11, article .1261; N 52, art. 6450; 2011, N 1, art. 54; N 29, art. 4281; N 30, art. 4590, art. 4591, art. 4596; N 48, art. 6732 ; N 50, art. 7359; 2012, N 26, article 3446; 2013, N 11, article 1164; N 27, art. 3477; N 30, art. 4059; N 52, art. 6971, art. 6974; 2014, N 11, article 1092; N 30, art. 4220; N 48, art. 6642; 2015, N 27, article 3994; N 29, art. 4359; N 48, art. 6723; 2016, N 1, art. 24), by the person operating the waste disposal facility, in the section "Information on indicators characterizing the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment" of the monitoring results report, the data indicated in paragraphs 2 and 3 of clause 25 of this Monitoring Procedure are not included.

9. If, based on the results of monitoring, negative changes in the quality of the environment that have arisen in connection with the operation of waste disposal facilities are identified, the persons operating these waste disposal facilities, in cases provided for by the legislation of the Russian Federation, immediately provide this information to the authorized state authorities, bodies local self-government and measures are taken to prevent, reduce and eliminate such changes in the manner prescribed by the legislation of the Russian Federation.

II. Development of a program for monitoring the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment

10. The monitoring program is developed on the basis of available data on the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment.

At the same time, at the discretion of persons operating waste disposal facilities, the following can be used:

data of the section "List of measures for environmental protection", which is part of the design documentation of the facility associated with the disposal of waste of I-V hazard class, and materials for assessing the impact of the waste disposal facility on the environment;

stock data of observations of the state and pollution of the environment in the area of ​​the location of the waste disposal facility and within the limits of their impact on the environment;

data on the background state of the environment in the area where the waste disposal facility is located;

available to persons operating waste disposal facilities, observational data on the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment;

materials of previously conducted environmental surveys on the territory of the waste disposal facility and within its impact on the environment.

11. When developing a monitoring program, the following are taken into account:

design characteristics (technical features) of the waste disposal facility;

origin, types, quantity and hazard classes of the disposed waste;

physical and geographical conditions in the area where the waste disposal facility is located;

geological and hydrogeological conditions in the area of ​​the waste disposal facility.

III. Composition and content of the program for monitoring the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment

12. The monitoring program includes the following sections:

general information about the waste disposal facility;

goals and objectives of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment;

information about the sources of information used in the development of the monitoring program;

substantiation of the choice of components of the natural environment and natural objects subject to observation on the territory of the waste disposal facility and within the limits of its impact on the environment;

substantiation of the choice of observed indicators of the components of the natural environment and natural objects that characterize the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment, the frequency of observations;

substantiation of the choice of sampling sites, points of instrumental measurements, determinations and observations;

composition of the report on the results of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment;



applications.

13. The section "General Information about the Waste Disposal Facility" contains the details of the letter by which the characteristics of the waste disposal facility were sent to the territorial body of Rosprirodnadzor, compiled based on the results of the inventory of waste disposal facilities in accordance with the approved ones (registered with the Ministry of Justice of Russia on 06/08/2010, registration N 17520), as amended by the order of the Ministry of Natural Resources of Russia dated 09.12.2010 N 541 (registered in the Ministry of Justice of Russia on 03.02.2011, registration N 19685).

14. In the section "Goals and objectives of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment", the goals and objectives of monitoring the state and pollution of the environment on the territory of this waste disposal facility and within its limits are given. impact on the environment.

15. The section "Information on the sources of information used in the development of the monitoring program" indicates the sources of information (in accordance with paragraph 10 of this Procedure) used in the development of the monitoring program, as well as data from these sources of information necessary for the organization and conduct of work on monitoring the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment.

16. In the section "Justification for the choice of components of the natural environment and natural objects to be monitored on the territory of the waste disposal facility and within the limits of its impact on the environment" are given:

data on the background state and pollution of atmospheric air, surface and ground waters, soils, flora and fauna (if necessary), as well as natural objects in the area of ​​the waste disposal facility;

data characterizing the potential and direct impact of waste disposal facilities on atmospheric air, surface and ground waters, soils, flora and fauna (if necessary), as well as individual ecological systems and natural landscapes in the area of ​​the waste disposal facility.

Based on a comparative assessment of the above data, a conclusion is made about conducting observations of specific components of the natural environment and natural objects on the territory of the waste disposal facility and within the limits of its impact on the environment.

The decision on the need to conduct observations of flora objects is made based on the results of the analysis of geochemical data on the state of groundwater and/or soil cover in the presence of evidence of their pollution.

The decision on the need to conduct observations of the objects of the animal world is made based on the results of the analysis of geochemical data on the state of the vegetation cover in the presence of evidence of its pollution and / or on the basis of the results of the analysis of physiognomic data on the state of the vegetation cover in the presence of evidence of its suppression.

17. In the section "Substantiation of the choice of observed indicators of the components of the natural environment and natural objects that characterize the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment, the frequency of observations" shall indicate such indicators (physical, chemical, biological, other) conditions and pollution of the environment, the change of which is possible as a result of waste disposal at this facility, as well as the frequency of their observation depending on the properties of the components of the natural environment and the accuracy of measurements (determinations).

Herb-shrub, woody and other plants can be used as test samples of flora objects that characterize the impact of a waste disposal facility on a given component of the natural environment. Observations of the condition of the vegetation cover are carried out during the growing season.

Fish, amphibians, mammals (rodents) can be used as test samples of wildlife objects that characterize the impact of a waste disposal facility on a given component of the natural environment.

18. In the section "Justification of the choice of sampling sites, points for instrumental measurements, determinations and observations", data are provided that make it possible to conclude that the optimal location and sufficiency of sampling sites, points for instrumental measurements, determinations and observations of atmospheric air, surface and groundwater , soil, flora and fauna (if necessary).

The decision on the location and number of sampling sites, points for instrumental measurements of atmospheric air, soils is made taking into account the directions of the prevailing winds and taking into account the types of permitted land use in the areas adjacent to the waste disposal sites.

The decision on the location of sampling sites, points for instrumental measurements of groundwater is made taking into account:

prevalence and conditions of occurrence of aquifers and water-resistant rocks;

the location of the boundaries of the recharge areas of aquifers (within the territory of the waste disposal facility) and the boundaries of the areas of their discharge (within the territory of the waste disposal facility or within its impact on groundwater).

Monitoring of the state and pollution of groundwater in the zone of impact of waste disposal facilities is carried out on the first aquifer from the earth's surface. In case of detection of pollution of the first aquifer from the earth's surface and a high probability of spreading this pollution further inland, observations are also made on the underlying aquifer. In case of detection of pollution of the second aquifer from the earth's surface and a high probability of spreading this pollution further inland, observations are carried out on the underlying aquifer.

19. In the section "Composition of the report on the results of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within the limits of their impact on the environment":

requirements are given for the composition, completeness and detail of information that should be contained in the report on the results of monitoring the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment, including taking into account the provisions of Chapter IV of this Monitoring Procedure;

Based on the generalization of the information presented in the previous sections of the monitoring program, the minimum appropriate time intervals for conducting observations of the state and pollution of the environment are proposed.

20. The "List of sources used" section indicates the list of normative legal acts, normative-technical and instructive-methodical documents, publications used in the preparation of the monitoring program, indicating their authors, titles, sources, publishers and dates of publication.

21. The section "Appendices" includes:

scheme of the territory of the waste disposal facility and adjacent territories;

layout of sampling sites, points of instrumental measurements, determinations and observations;



IV. Composition and content of the report on the results of monitoring the state and pollution of the environment in the territories of the accommodation facilities and within the limits of their impact on the environment

22. The report on the monitoring results must comply with the approved monitoring program and include the following sections:

information about the waste disposal facility;

information on monitoring the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment;

information on indicators (physical, chemical, biological, others) characterizing the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment;

processing and documentation of observational data on the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment;

assessment and forecast of changes in the state of the environment;

list of sources used;

applications.

23. The section "Information about the waste disposal facility" contains the details of the last letter, which sent to the territorial body of Rosprirodnadzor the characteristics of the waste disposal facility, compiled on the basis of the results of the inventory of waste disposal facilities in accordance with the Rules for the inventory of waste disposal facilities, approved by order of the Ministry of Natural Resources of Russia dated February 25 .2010 N 49 .

24. In the section "Information on ensuring observations of the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment", the following information is provided:

on organizations involved in monitoring the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment;

on the means of sampling, instrumental measurements, determinations and observations used and their compliance with the requirements of the legislation;

about the methods (methods) used for sampling, instrumental measurements, definitions and their compliance with the requirements of the legislation;

copies of documents on accreditation of the testing laboratory (center) and the scope of its (its) accreditation in accordance with the Federal Law of December 28, 2013 N 412-FZ "On accreditation in the national accreditation system" (Collected Legislation of the Russian Federation, 2013, N 52, art. 6977, 2014, N 26, art. 3366), which (s) carried out instrumental measurements, certified by the seal and signature of an authorized official of the testing laboratory (center);

copies of acts of sampling.

25. In the section "Information on indicators characterizing the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment" the results of observations of the state of physical, chemical, biological and other indicators are given:

atmospheric air;

surface waters;

groundwater;

soils (in the year of work on assessing the state of soils);

flora and fauna (if necessary).

26. In the section "Processing and documentation of observational data on the state and pollution of the environment on the territory of the waste disposal facility and within the limits of its impact on the environment" are given:

results of assessment and dynamics of changes in the environment under the influence of the waste disposal facility (compared to background data on the state and pollution of the environment in the area of ​​the waste disposal facility and data from previous observations) and data on the forecast of such changes;

ongoing and planned measures to prevent, reduce and eliminate negative changes in the quality of the environment;

information on informing public authorities, local authorities, legal entities and individuals about the state and pollution of the environment in the area where the waste disposal facility is located.

27. The section "Assessment and forecast of changes in the state of the environment" provides comparative data on the indicators of the components of the natural environment and natural objects that characterize the state and pollution of the environment on the territory of the waste disposal facility and within its impact on the environment, for the reporting period and for previous reporting periods, as well as data on the expected values ​​of indicators of the components of the natural environment and natural objects for the upcoming reporting period.

When submitting the first report on the results of monitoring, the assessment of changes in the environment is carried out in comparison with the background values ​​of indicators of the components of the natural environment and natural objects in the area of ​​the waste disposal facility.

28. The "List of used sources" section indicates the list of normative legal acts, normative-technical and instructive-methodical documents, publications used in the preparation of the report on the results of environmental monitoring, indicating their authors, titles, sources, publishers and dates of publication.

29. The section "Appendices" includes:

calendar plan for the implementation of work to monitor the state and pollution of the components of the natural environment and natural objects;

copies of documents and materials on the compliance of the used sampling equipment, instrumental measurements, definitions with the requirements of the legislation of the Russian Federation;

copies of documents and materials on the compliance of the used methods (methods) of sampling, instrumental measurements, definitions with the requirements of the legislation of the Russian Federation;

other materials at the discretion of the person operating the waste disposal facility.



Electronic text of the document
prepared by Kodeks JSC and verified against:
Official Internet portal
legal information
www.pravo.gov.ru, 06/15/2016,
N 0001201606150049

On the Procedure for the owners of waste disposal facilities, as well as persons in whose possession or use of which waste disposal facilities are located, to monitor the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment

Document's name: On the Procedure for the owners of waste disposal facilities, as well as persons in whose possession or use of which waste disposal facilities are located, to monitor the state and pollution of the environment on the territories of waste disposal facilities and within the limits of their impact on the environment
Document Number: 66
Type of document: Order of the Ministry of Natural Resources of Russia (Ministry of Natural Resources and Ecology of the Russian Federation)
Host body: Ministry of Natural Resources of Russia (Ministry of Natural Resources and Ecology of the Russian Federation)
Status: current
Published: Official Internet portal of legal information www.pravo.gov.ru, 06/15/2016, N 0001201606150049

Bulletin of normative acts of federal executive authorities, N 30, 07/25/2016
Acceptance date: March 04, 2016
Effective start date: June 26, 2016

Monitoring of the state of the environment at the facilities (places) of storage and disposal of waste should be carried out taking into account:

· Assessment of the impact of waste accumulated in storage areas and stored at the waste disposal site;

organization of waste storage sites;

· physical and chemical properties of the waste (solubility, volatility, reactivity, explosion and fire hazard of the state of aggregation).

Monitoring aims to reduce or completely eliminate the harmful effects of waste on the environment.

Control over the state of objects of centralized waste disposal is assigned to representatives of the enterprise.

Monitoring of the state of the soil is carried out in accordance with the requirements of SaNPiN 2.1.7.1287-03 Sanitary and epidemiological requirements for soil quality.

The standard list of chemical indicators includes the determination of the content:

Heavy metals: lead, cadmium, zinc, copper, nickel, arsenic, mercury;

3,4-benzpyrene and petroleum products;

The total indicator of pollution.

Monitoring of the state of the soil is carried out in residential areas, including high-risk areas, in the zone of influence of vehicles, buried industrial waste (the soil of the territories adjacent to landfills), in places of temporary storage of industrial and domestic waste, on the territory of agricultural land, sanitary protection zones. The scope of research and the list of indicators studied during monitoring is determined in each specific case, taking into account the goals and objectives in agreement with the bodies and institutions that carry out state sanitary and epidemiological surveillance.

6.8. Monitoring is carried out taking into account the results of studies at all previous stages of design, construction, as well as upon completion of the construction of the facility, when it is put into operation and throughout its entire operational period.

6.9. Soil sampling is regulated by state standards for general requirements for sampling, methods for taking and preparing soil samples for chemical, bacteriological and helminthological analysis, and guidelines for hygienic assessment of soil quality in populated areas.

6.10. All soil quality assessment studies must be carried out in duly accredited laboratories.

6.11. Determination of the content of chemical pollutants in soils is carried out by methods used in the justification of MPC (APC) or other methods, metrologically certified, included in the state register of methods.

6.13. The number of sampling points depends on the area of ​​the construction site, the depth of the construction of the facility or the laying of engineering communications, the stages of design and construction work.

6.14. Radiation control is carried out in full at any construction and engineering structures for compliance with the requirements of the Radiation Safety Standards - NRB-99 (They do not need state registration, letter of the Ministry of Justice of Russia dated 29.07.99 N 6014-ER).

Previous materials:
  • Global and regional forecasts of the state of the natural environment. Forecast of pollution of natural waters, soils. Forecast of the quality of water resources.

In accordance with paragraph 6.4 of SP 2.1.7.1038-01 "Hygienic requirements for the arrangement and maintenance of landfills for municipal solid waste" (hereinafter - SP 2.1.7.1038-01), a special program (plan) for the production control (monitoring), which should include information on monitoring the state of underground and surface water bodies, atmospheric air, soils, noise levels in the zone of possible adverse impact of solid waste landfills.

Monitoring of solid waste landfills must be carried out taking into account the requirements of the following documents:

  • SP 2.1.7.1038-01;
  • Instructions for the design, operation and reclamation of landfills for municipal solid waste, approved by the Ministry of Construction of Russia on November 2, 1996 (hereinafter referred to as the Instruction);
  • SanPiN 2.2.1/2.1.1.1200-03 "Sanitary protection zones and sanitary classification of enterprises, structures and other objects" (as amended on April 25, 2014);
  • GOST 17.1.5.05-85 “Nature protection. Hydrosphere. General requirements for sampling surface and sea waters, ice and atmospheric precipitation”;
  • SanPiN 2.1.5.980-00 "Hygienic requirements for the protection of surface waters" (as amended on 04.02.2011 and 25.09.2014);
  • SanPiN 2.1.7.1287-03 "Sanitary and epidemiological requirements for soil quality" (as amended on April 25, 2007).

NOTE

According to paragraph 7 of Art. 12 of the Federal Law of June 24, 1998 No. 89-FZ “On Production and Consumption Wastes” (as amended on December 29, 2014) prohibited waste disposal at MSW landfills not included in the state register of waste disposal facilities (GRRO).
At present, all solid waste landfills must be brought into line with the current environmental legislation of the Russian Federation, as well as an inventory of these objects and apply in writing to the territorial body of Rosprirodnadzor for registration of landfills in the GRRO .
Information on whether the landfill is included in the GRRO can be found on the website of Rosprirodnadzor in the subsection “State Register of Waste Disposal Facilities”http://rpn.gov.ru/node/853located in the Waste Cadastre section.

According to clause 1.30 of the Instruction special monitoring project(i.e. the previously mentioned special program (plan) of production control (monitoring)) should include the following sections:

  • monitoring the state of underground and surface water bodies, atmospheric air, soils and plants, noise pollution in the zone of possible adverse impact of the landfill;
  • a system for managing technological processes at the landfill, which ensures the prevention of pollution of underground and surface water bodies, atmospheric air, soils and plants, noise pollution above the permissible limits in cases where the polluting effect of landfills is detected.

Based on clause 6.6 of SP 2.1.7.1038-01 and clause 1.31 of the Instruction, the production control system should include devices and facilities for monitoring the state of ground and surface water, atmospheric air, soil and plants, as well as noise pollution in the zone of possible influence of the solid waste landfill.

The monitoring system serves as an information basis for determining the effectiveness of environmental measures taken at the landfill, as well as a database for developing technical and technological solutions to improve the operation of the landfill.

According to paragraph 6.5 of SP 2.1.7.1038-01, the program (plan) for the production control of the MSW landfill is being developed landfill owner(based on clause 1.30 of the Instruction - according to the terms of reference of the landfill owner) in accordance with the sanitary rules for production control over compliance with sanitary and epidemiological requirements. Paragraph 1.30 of the Instruction states that such a program should be agreed with the competent authorities.

OBSERVATION OF THE STATE OF ATMOSPHERIC AIR

The monitoring system of the MSW landfill should include constant monitoring of the state of the air environment. For this purpose, air samples are analyzed quarterly in the surface layer above the exhausted areas of the landfill and at the border of the sanitary protection zone for the content of compounds in it that characterize the process of biochemical decomposition of MSW and pose the greatest danger.

In accordance with paragraph 6.8 of SP 2.1.7.1038-01 and paragraph 1.36 of the Instructions, the volume of indicators to be determined and the frequency of sampling are substantiated in the program for the production control of the solid waste landfill and agreed with the regulatory authorities. Usually, when analyzing samples of atmospheric air, the content of methane, hydrogen sulfide, ammonia, carbon monoxide, benzene, trichloromethane, carbon tetrachloride, chlorobenzene is determined.

When establishing the degree of air pollution above the MPC at the border of the sanitary protection zone and above the MPC r.z. in the working area (Tables 1.3 and 1.4 of the Instructions), appropriate measures should be taken, taking into account the nature and level of pollution and aimed at reducing this level.

extraction
from the Instructions

Table 1.3

MACS FOR THE MAIN POLLUTANTS RELEASED INTO THE AIR AT SMW POLYGONS

Table 1.4

MACS OF THE MAIN POLLUTANTS (WORKING AREA) RELEASED TO THE ATMOSPHERIC AIR AT MSW POLYGONS IN THE AREA OF STAFF WORK

SOIL OBSERVATION

The production control of the MSW landfill should include constant monitoring of the soil condition in the zone of possible influence of the landfill.

According to paragraph 6.9 of SP 2.1.7.1038-01, soil quality is controlled by chemical (content of heavy metals, nitrites, nitrates, bicarbonates, organic carbon, pH, cyanides, lead, mercury, arsenic), microbiological (total bacterial count, coli-titer, proteus titer, helminth eggs) and radiological parameters. The number of chemical and microbiological indicators can be expanded only at the request of the territorial center of state sanitary and epidemiological supervision(hereinafter - TsGSEN).

On the basis of paragraph 1.38 of the Instruction, the quality of soil and plants is controlled for the content of exogenous chemicals (ECS), which should not exceed the MPC in the soil and, accordingly, not exceed the residual amounts of harmful ECS in the vegetable marketable mass above the permissible limits. The volume of ECM to be determined and the frequency of control are determined in the landfill monitoring project (i.e., in the production control program) and are agreed with specially authorized environmental protection authorities.

MONITORING THE STATE OF SURFACE AND GROUND WATER

The monitoring program also includes analyzes of surface and ground waters.

In accordance with paragraph 6.7 of SP 2.1.7.1038-01, in agreement with the territorial TsGSEN and other regulatory authorities (according to paragraph 1.32 of the Instructions - in agreement with the hydrogeological service, local sanitary and epidemiological supervision and nature protection authorities), the state of ground water- depending on the depth of their occurrence, control pits, wells or wells are designed in the green zone of the landfill and outside the sanitary protection zone of the landfill. The control facility is laid upstream of the landfill along the groundwater flow in order to take samples of water, which is not affected by the leachate from the landfill.

Based on paragraph 1.32 of the Instructions, water samples from control pits, wells and wells laid upstream of the landfill along the groundwater flow characterize their initial state. Below the landfill along the groundwater flow (at a distance of 50-100 m, if there is no danger of groundwater pollution from other sources), 1-2 wells (pits, wells) are laid for water sampling in order to identify the impact of landfill effluents on it. Wells with a depth of 2-6 m are made of reinforced concrete pipes with a diameter of 700-900 mm up to a mark of 0.2 m below the groundwater level. The filtering bottom consists of a layer of crushed stone 200 mm thick. They descend into the well by a fixed ladder. With a deeper occurrence of groundwater, their control is carried out using wells. The design of the facilities should ensure the protection of groundwater from ingress of accidental pollution, the possibility of drainage and pumping, as well as the convenience of taking water samples. The volume of indicators to be determined and the frequency of sampling are substantiated in the monitoring program for landfills.

According to clause 6.7 of SP 2.1.7.1038-01 and clause 1.34 of the Instructions, sampling sites are designed above the landfill on surface water sources and below the landfill on drainage ditches surface water.

The content of ammonia, nitrites, nitrates, bicarbonates, calcium, chlorides, iron, sulfates, lithium, COD, BOD, organic carbon, pH, magnesium, cadmium, chromium, cyanides, lead, mercury, arsenic, copper, barium, dry residue. Samples are also examined for helminthological and bacteriological indicators. If in the samples taken downstream a significant increase in the concentrations of analytes compared to the control is established, it is necessary, in agreement with the regulatory authorities, to expand the scope of the determined indicators, and in cases where the content of the analytes exceeds the MPC, measures should be taken to limit the intake of pollutants into groundwater up to MPC level.

"Handbook of Ecologist" No. 2, 2015.

UDC 631.47

ORGANIZATION OF MONITORING OF WASTE DISPOSAL FACILITIES (BY THE EXAMPLE OF THE POLYGON OF SOLID HOUSEHOLD WASTE IN THE MOSCOW REGION)

© 2012 E.I. Kovaleva1, A.S. Yakovlev2, S.A. Yakovlev1, E.A. Duvalina2

1 ANO Ecoterra 2 Lomonosov Moscow State University M.V. Lomonosov

Received May 14, 2012

The results of long-term monitoring of a landfill for municipal solid waste (MSW) are presented. The main source of pollution of soils, natural waters, bottom sediments of the water body adjacent to the landfill is the leachate released from the body of the landfill. Long-term control in the area of ​​the landfill location revealed unregulated sources of pollution that increase the burden on the environment in the area of ​​the landfill location. The accumulation of pollutants inherent in the composition of the leachate and wastewater from unregulated sources was established in the bottom sediments of water bodies and soils in the area of ​​the solid waste landfill. The basic principles of organizing monitoring are proposed, which allow obtaining representative results and identifying the features of the negative impact on the components of the environment.

Keywords: monitoring, bottom sediments, waste disposal sites, landfill, pollution

Irrational use of natural resources, pollution and degradation of environmental components as a result of economic activity, make the problem of protecting soils and water bodies one of the main ones, since without maintaining the quality of soils and waters, it is impossible to ensure the implementation of the state strategy of the Russian Federation to ensure the sustainable development of the country. Waste disposal sites are one of the most significant factors of anthropogenic impact on the environment. Waste disposal sites (ORF) are complex technogenic formations within which substances of various genesis and composition are concentrated. For a long time, the choice of the location of the ODP took place without taking into account the environmental sustainability of the territory and the implementation of environmental protection measures. These objects are both objects of land littering and a source of pollutants entering the environment: atmospheric air, soils, surface and ground waters, plant

Kovaleva Ekaterina Igorevna, Candidate of Biological Sciences, Deputy Head of the Department. Email: [email protected] en

Yakovlev Alexander Sergeevich, Doctor of Biological Sciences, Professor, Head of the Department of Land Resources and Soil Assessment. E-mail: [email protected] Yakovlev Sergey Alexandrovich, leading specialist

Duvalina Ekaterina Anatolyevna, cover specialist. The composition and volume of waste entering landfills is extremely diverse, increasing and changing from year to year. When storing waste in the body of the landfill, complex chemical and biochemical processes take place, including the formation of new substances characterized by high danger. The present and newly formed substances of the stored waste under the influence of atmospheric precipitation form a filtrate that flows out of the landfill body, migrates, polluting the adjacent environments: surface water, ground water, soil, vegetation. In the absence of control over ODP, a moment may come when negative changes in natural complexes become irreversible, which may lead to an ecological crisis. In this regard, it is important to organize a monitoring system in the ODP zone, assess the state of the environment and predict changes under the influence of anthropogenic factors. The monitoring of the state of the environment on the territory of the ODP is carried out in pursuance of Article 12 of Chapter III of the Federal Law No. 89-ФЗ “On Production and Consumption Waste” .

Components of the OS, due to the buffering and tolerance properties of biotic components, are able to withstand the negative impact, while maintaining their structures.

tour and functional properties. However, certain levels of anthropogenic impact can lead to an irreversible deterioration of the ecological state of the environment. In accordance with this, the results of monitoring should record the state of the OS components and not allow the permissible anthropogenic load on the OS to be exceeded when its components cannot perform their environmental functions.

The organization of environmental monitoring at waste disposal sites is based on scientifically based methodological approaches to the selection of a set of controlled parameters and points of their control. The choice of parameters, methods of observation, methods of assessing the components of the environment is determined by the nature of the anthropogenic impact on adjacent territories by economic entities. When monitoring the state of the natural environment, a necessary step is the assessment and establishment of environmental quality standards based on the natural features of the study area, its functional and economic purpose.

Purpose of the work: development of principles for organizing monitoring of RDP and assessment of changes in the state of soils and water bodies in the zone of its location (on the example of a solid waste landfill in the Moscow region).

Objects and methods. The object of the study was the MSW landfill in the Moscow region and the territory adjacent to it. During the monitoring, the soil cover and water bodies were studied for 6 years. The entry of pollutants into soils and water bodies comes from a point source - a solid waste landfill, which has been accepting waste of 4-5 hazard classes for disposal for more than 30 years. At the time of the survey, the thickness of the landfill body reached about 20 m. Seepage water (leachate) is released from the landfill body, which enters the bypass ditch around the landfill, which localizes the spread of the leachate in the radial direction. The leachate is discharged from the bypass ditch into the river, which originates at the border of the landfill. There is a network of drainage ditches in the area around the landfill, which serves to divert water from wetland areas to the aforementioned river. The study of the area around the landfill and the evaluation of monitoring results in the first years made it possible to identify unregulated sources of pollutant discharges from nearby enterprises located higher in relief from the landfill. In accordance with the soil zoning of the Moscow region, the studied territory is included in the district of soddy-podzolic soils of loamy mechanical composition of the Smolensk-Moscow Upland. soil

the cover of the territory is represented by variations of soddy-podzolic and soddy-podzolic gleyic soils with a slight distribution of marsh-podzolic and marsh soils.

To assess the possible impact of the solid waste landfill, control sites have been laid out that characterize: 1) sources of pollutants entering the environment; 2) the quality of the environment in the zone of possible impact of sources of pollutants, along the gradient of removal from it in the direction of the general slope of the area; 3) background natural objects, not affected by anthropogenic activity, near the solid waste landfill. The choice of indicators for monitoring was made taking into account the set of pollutants contained in the leachate released from the landfill body and wastewater from unregulated sources of pollution.

As part of long-term monitoring, a study was made of the composition of the leachate flowing from the body of the landfill, an assessment of the nature and level of possible contamination of soils, surface waters and bottom sediments of the stream, drainage ditches in the zone of the proposed impact of the landfill. To assess the level of anthropogenic impact, background areas were surveyed, where samples of soils, natural waters and bottom sediments were taken. In the selected samples of the filtrate and natural media, the following was determined annually: pH - potentiometrically, metals - by atomic emission spectrometry with inductively coupled plasma in the liquid phase, X-ray spectral method - in the solid phase; anions - by ion chromatography and spectrophotometry, oil products - by fluorometry on a Fluorate device with preliminary extraction into hexane.

The discussion of the results. To assess the changes occurring in the state of natural environments under the influence of anthropogenic load, samples of soils, bottom sediments and natural water of the stream, taken in the background area not subject to anthropogenic impact, were studied. The results of the chemical analysis of the samples showed that the content of pollutants characteristic of the composition of the filtrate does not exceed the established maximum permissible concentrations (MPC) for these substances. The obtained results can be used as background values ​​in interpreting the data obtained for soils selected at monitoring control plots. According to the literature data, the anthropogenic impact on the components of the environment is reliably manifested when the content of pollutants (heavy metals) exceeds the background by 1.5-2 times.

The released leachate is a source of pollution of environmental components: natural waters, bottom sediments, soils in the zone of influence of the solid waste landfill. The filtrate is a saturated multicomponent aqueous solution, the chemical composition of which, according to the results of the analysis, is not uniform in different years and periods. The main pollutants coming with the leachate from the solid waste landfill, according to long-term monitoring data, are chromium (24 MPC), manganese (14 MPC), copper (18 MPC), lead (b MPC), ammonium (140 MPC), chlorides (6 MPC), nitrates (3 MPC), phosphates (3 MPC), sulfates (4 MPC). On fig. 1-4 shows histograms of changes in the content of some pollutants in the filtrate over time.

Rice. 1. Change in the concentration of chromium, manganese in the filtrate over the years

Rice. 2. Change in the concentration of lead in the leachate over the years

Rice. 4. Change in the concentration of the ammonium ion in

leachate by years of waste in the body of the landfill with the establishment of stable temperatures below + 3-5 ° C and a decrease in precipitation

The analysis of data on the content of pollutants in the leachate did not reveal any direction in the change in the concentration of pollutants over the years, there is a significant variation in the level of their content. Probably to a greater extent, the composition of the stored waste determines the spectrum of contaminants in the leachate.

A study of the chemical composition of leachate samples by season showed that the content of all pollutants did not exceed the MPC values ​​established for them in the autumn-winter period. This confirms the hypothesis of slowing down the biochemical processes of transformation

The study of the composition of wastewater from unregulated sources of pollutants entering the environment and their migration routes showed that they increase the load on the components of the environment in the area where the solid waste landfill is located. Wastewater from unregulated sources through drainage ditches enters the bypass ditch with leachate, then into the river. Consequently, the composition of wastewater from unauthorized sources to some extent determined the set of pollutants and their concentrations in the leachate and the river.

Rice. 3. Change in the concentration of chlorides in the filtrate over the years

On fig. As an example, Tables 5 and 6 give the content of typical pollutants in the leachate and wastewater in 2010. The identification of unregulated sources of pollutants with their subsequent elimination made it possible to reduce the set and level of pollutants in the leachate and in the water body in subsequent years.

The results of the study of selected samples of natural environments at sites that characterize the quality of the environment in the area of ​​impact of the landfill showed that surface water and bottom sediments of the stream and drainage ditches of adjacent areas are contaminated with substances typical for leachate and wastewater (copper, nickel, lead, manganese , zinc, chromium). The level of their content exceeds both the background values ​​and the MPC values ​​established for them. On fig. Figures 8 and 9 show data on changes in the concentration of chromium in samples of water and bottom sediments from the stream, taken along the gradient of removal from the solid waste landfill over time.

The results of soil monitoring in the zone of influence of the MSW landfill revealed contamination of bog soils developing in flooded areas. Having a high sorption capacity, these soils accumulate heavy metals, nitrates, phosphates, sulfates in the surface peat layer, the content of which exceeds the background values ​​by 10-1000 times. Soddy-podzolic soils are less susceptible to pollution. It has been established that the area of ​​distribution of pollution can reach several kilometers.

Rice. Fig. 7. Change in the concentration of chromium in the water from the stream along the gradient of removal from the MSW landfill over time

Rice. Fig. 8. Change in the concentration of chromium in bottom sediments from the stream along the gradient of removal from the MSW landfill in time

Conclusions: the study of the state of the OS components, the establishment of the presence (absence) of the impact of the leachate emitted from the body of the solid waste landfill, showed the need for long-term environmental monitoring of RDO using the principles of regulation and scientifically based approaches, since such objects are dynamic systems. This will make it possible to timely identify changes in the state of the OS, give an assessment, forecast and develop recommendations for the prevention and elimination of the consequences of negative processes. The work on organizing monitoring of the MSW landfill showed that in order to obtain representative data for assessing the state of the OS components, the following requirements must be met:

Sites for sampling soils and associated media - waters and bottom sediments are laid taking into account the landscape and terrain, the general slope of the territory, the direction of water migration of pollutants from the waste disposal facility;

Sampling of background and contaminated sites should be carried out simultaneously in the same period of time, which will allow them to be compared correctly;

Sampling by years is carried out at the same time, taking into account seasonality and weather conditions;

An obligatory element of monitoring is the control of the content of pollutants in the bottom sediments of water bodies, since they are an informative object of research and an indicator of the ecological state of the territory.

Science-based design and organization of monitoring makes it possible to identify the features of the negative impact of ODP on OS components. The present work shows the possibility of establishing unregulated sources against the background of the functioning of a point, regulated ODP - a solid waste landfill, which increase the anthropogenic load on the components of the environment. Properly organized monitoring in identifying unregulated sources of pollutants entering the environment makes it possible to identify them.

host by type of pollutant and economic activity of enterprises located near the identified source. This may contribute to the development of the practice of establishing and delimiting the environmental liability of enterprises for damage caused to the environment. four.

BIBLIOGRAPHY:

1. Zyrin, N.G. Impact pollution of soils by metals and fluorides / N.G. Zyrin, A.I. Obukhov, 5. L.K. Sadovnikova and others - L.: Gidrometeoizdat, 1986. 123 p.

2. Gorlenko, A.S. Issues of assessing the negative impact of waste disposal facilities on soils

/ A.S. Gorlenko, E.I. Kovaleva, T.O. 6. Poputnikova // Proceedings of the III Congress of the Society of Soil Scientists

them. V.V., Dokuchaeva. Rostov-on-Don, 2008. S. 3538.

Kovaleva, E.I. Monitoring of solid household waste disposal facilities / E.I. Kovaleva, T. O. Poputnikova // VIII International Ecological Forum, 2008. P. 176-178. Poputnikova, T. O. Ecological assessment of soils and individual components of the environment in the area of ​​solid domestic waste landfill. Abstract for the competition uch. Art. cand. biol. Sciences. 2010. 24 p.

Assessment of the ecological state of soil and land resources and the environment of the Moscow region / Ed. ed. G.V. Dobrovolsky, S.A. Shoby. - M.: Publishing House of Moscow State University, 2000. 221 p.

Federal Law "On Environmental Protection" dated January 10, 2002 N 7-FZ

ORGANIZATION THE MONITORING OF WASTAGE OBJECTS PLACEMENT (ON EXAMPLE OF SOLID HOUSEHOLD WASTAGE POLYGON IN MOSCOW OBLAST)

© 2012 E.I. Kovaleva1, A.S. Yakovlev2, S.A. Yakovlev1, E.A. Duvalina2

1 ANO "Ecoterra" 2 Moscow State University named after M.V. Lomonosov

Results of long-term monitoring of solid household waste (SHW) polygon are presented. The main source of pollution the soils, natural waters, ground deposits of water object of the adjacent territory to the polygon is the filtrate which is allocating from the body of the polygon. Long-term monitoring in a zone of placement of the polygon of SHW revealed the noncontrollable polluters strengthening load on the surrounding environment in a zone of placement of SHW polygon. Accumulation the pollutants inherent in structure of filtrate and sewage of noncontrollable sources, in ground deposits of water objects and soils in zone of placement of SHW polygon is established. Philosophy of the organization the monitoring are offered, allowing to receive representative results and to reveal features of negative impact on components of surrounding environment.

Key words: monitoring, ground deposits, objects of waste placement, polygon, pollution

Ekaterina Kovaleva, Candidate of Biology, Deputy Chief of the Department. Email: [email protected] Alexander Yakovlev, Doctor of Biology, Professor, Head of the Land Resources and Soils Estimation Department. E-mail: [email protected] Sergey Yakovlev, Leading Specialist Ekaterina Duvalina, Specialist

Have questions?

Report a typo

Text to be sent to our editors:

Send