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In accordance with the decision of the Government, the Environmental Protection Act (2006) And waste law (166/2011) Pursuant to:
This Regulation shall apply to the drawing up and implementation of the waste management plan for extractive waste, the establishment, management, withdrawal and treatment of waste from extractive waste, the recovery of extractive waste in an empty quarry, and Monitoring, monitoring and control of waste from extractive waste.
Article 5, Article 6 (1), Articles 9 to 11 and Article 14 of this Regulation shall not apply to extractive waste, which is permanent waste or unpolluted soil, or which has arisen in connection with peat production, if the waste is destined for a non-major accident Waste from extractive extractive waste.
For the purposes of this Regulation:
(1) Searching for The sampling, causation and excavation of the research oers and other forms of preparation for the recovery of rock or soil material;
(2) Enrichment The mechanical, physical, biological, thermal or chemical treatment of mineral resources, or a combination of these methods for the separation of minerals, including the modification, classification, separation and extraction of the size and the reprocessing of waste; However, the enrichment process does not include smelting processes, other thermal processes other than the burning of limestone or metallurgical functions;
(3) Tailings waste Solid or slurry residues remaining in the mineral enrichment where the value separates are separated from the less valuable stone material in crushing, milling, assembly, foaming, other physico-chemical treatment Or any other separation process;
(4) Permanent waste Extractive waste meeting the criteria in Annex 1;
(5) With unpolluted soil Organic or inorganic material extracted from the surface of the rock or soil, which is natural or does not contain any harmful substances which may result in environmental pollution or its risk;
(6) Swallow water A liquid that performs through the deposited waste and leaves the waste area or remains in the area, including contaminated lighting, which, without proper treatment, can have harmful effects on the environment;
(7) On waste from extractive waste An area in the context of a production site with solid, slurry or liquid extractive waste generated in it;
(8) In the area of waste from extractive waste resulting from a major accident The waste facility for extractive waste meeting the criteria set out in Annex 2.
The waste from the extractive waste referred to in paragraph 1 (7) shall not be regarded as an area in the context of a land and water-building activity to which extractive waste generated in the mineral extraction and crushing waste associated with the activity is located. Furthermore, the waste from extractive waste shall not be regarded as an empty quarry, which shall be used to restore the extractive waste generated in operation for the purpose of rehabilitation or construction. In the absence of a major accident hazard area, an area where the waste from extractive waste is located shall not be considered as a waste facility:
(a) non-contaminated soil, permanent waste, or extractive waste generated in the search or production of peat, which is not hazardous waste, less than three years;
(b) extractive waste, other than those referred to in point (a), which is not hazardous waste, for less than one year.
When drawing up the waste management plan for extractive waste, account shall be taken of:
(1) at the planning stage of the activity and the methods of extraction and enrichment, the impact of the action on waste management is explained;
(2) the physico-chemical changes of extractive waste during operations are assessed under different conditions;
(3) extractive waste is returned to the mine, quarry or any other place where the materials are taken, where technically and economically feasible and not otherwise prohibited;
(4) the surface country is returned to the sampling area or is recovered at the end of the operation;
(5) mineral enrichment is used to treat the environment as harmless as possible;
(6) the potential for the recovery of extractive waste is explained;
(7) the future disposal needs of extractive waste are explained in the planning of waste facilities;
(8) the waste facility for extractive waste is designed and implemented in such a way as to require minimum monitoring, monitoring, control and treatment at the end of operations;
(9) adverse environmental impacts arising from activities in the short and long term are prevented as effectively as possible;
(10) Geotechnical stability of the stocks of extractive waste in excess of the natural height of the surface area associated with the operation shall be ensured.
The waste management plan for the extractive waste shall include:
(1) a report on the extractive waste and its properties in accordance with Annex 3;
(2) an estimate of the total amount of extractive waste, a description of the recovery and disposal of waste, and information on the recovery of extractive waste in an empty mine or quarry;
(3) a report on the waste facility and its environment in the extractive waste sector, as well as the classification of the waste facility as a major accident hazard or waste facility for extractive waste;
(4) according to the classification of the waste facility for extractive waste, either information on the operating principles for the control of the major accident, the safety management system and the internal emergency plan or any other explanation of the accident hazards;
(5) a report on the state of the soil, water and groundwater in the waste facility of the extractive waste and in a neighbouring region to which the waste may be caused;
(6) information on the environmental impact of waste from extractive waste and waste from extractive waste;
(7) information on measures to be taken to prevent soil, water, groundwater and air pollution and other effects during and after operation;
(8) a report on monitoring and surveillance during and after the operation;
(9) information on the cessation of activities, the use of the waste facility for extractive waste and after-treatment, and related monitoring and surveillance.
In addition to the provisions laid down in paragraph 1, the competent authority for the management plan of the extractive waste management plan may require that any other relevant information be provided in the waste management plan to assess that the quantity and harmfulness of extractive waste And the recovery and disposal of waste under the Environmental Protection Act (177/2014) And waste law (166/2011) And in accordance with this Regulation. (5 FEBRUARY 2015)
In establishing and implementing a policy document, the safety management system and the internal emergency plan causing the risk of a major accident, the safety management system and the internal rescue plan shall be respected The principles and requirements laid down in Annex 4. The internal rescue plan shall take into account the safety assessment of the safety of dams in the waste facility (494/2009) The risk of damage and other explanations. The rescue plan shall be updated as necessary, in such a way as to reflect changed situations and circumstances.
In the event of a major accident, the operator shall, in the event of a major accident, provide the Authority and the Authority with information to minimise the impact on human health and to assess and minimise The extent of the damage or potential environmental damage.
The Environmental Licence Authority shall request an internal emergency rescue plan and, where appropriate, the opinions of the Pathological Authority. The licensing authority shall submit to the Civil Protection Authority and the PatoSafety Authority the other documents relating to the authorisation decision and the application for a rescue plan to be taken into account for plans in the field of their activities. The Authority shall also submit the amendments to the internal emergency plan to the Civil Protection Authority and the PatoSafety Authority.
The environmental authorisation shall determine how the internal emergency plan shall be kept up to date and how the amendments to the plan shall be submitted to the Authority.
The operator shall monitor technical developments relating to the establishment and management of waste facilities in the extractive waste facilities and shall, as appropriate, ensure adequate training and certification of personnel in the waste facility.
The responsible person for the waste facility in the extractive waste facility is governed by Article 141 of the Waste Act and Article 115 (3) of the Environmental Protection Act. The responsible person shall be notified to the Authority. (5 FEBRUARY 2015)
The waste facility for extractive waste shall be established and managed in such a way as to:
(1) the waste facility is not caused by soil, water, groundwater or air pollution or any other environmental pollution, or its risk, taking into account the location of the site and geological, hydrological, hydrogeological and geotechnical characteristics of the site;
(2) the waste facility does not, within a long period of time, give rise to environmental pollution or its risk, taking into account the resulting protective water and other waste water and erosion;
(3) the physical stability of the waste facility is ensured, as well as environmental degradation and the prevention of landscape damage by appropriate structures and planned management and maintenance;
(4) the waste facility shall be monitored and monitored in a planned and competent manner and shall take the necessary measures if the waste facility is not stable enough or the area of the environment is caused by environmental pollution or risks;
(5) the soil of the waste facility and its environment, where necessary, is purified or otherwise remedied;
(6) appropriate measures are taken to eliminate the use of the waste facility and to organise its aftercare.
The operator of the extractive waste facility shall:
(1) assess the amount and contamination levels of leachate and other waste water from the extractive waste and determine the water balance of the waste facility during and after its operation;
(2) prevent the pollution of soil, water and groundwater from extractive waste, as well as the resulting pollution from leachate and other waste water and from waste water;
(3) collecting and addressing effectively waste water and other waste water from the waste facility;
(4) prevent dust and gas emissions from the waste facility in the air.
The environmental permit or notification decision may stipulate that the obligation laid down in paragraph 1 (3) does not have to be complied with if the operator reliably demonstrates, on the basis of the overall environmental hazard assessment, That waste from extractive waste cannot cause pollution of the soil, water or groundwater or any other environmental pollution or risk.
Solid, slurry or liquid extractive waste must not be placed or water-water or other waste water will lead to water in such a way as to result in the aquatic environment of the Council Regulation on dangerous and harmful substances (1022/2006) Of environmental quality standards. In certain plans and programmes, the environmental permit provides for the environmental authorisation to be taken into account in Article 51 (1) of the Environmental Protection Act. (5 FEBRUARY 2015)
Paragraph 1 shall not apply to extractive waste arising from unpolluted soil or in the context of peat production, nor from extractive waste generated in the search, which is not hazardous waste, if any In the waste management plan for the extractive waste management plan, it is reliably demonstrated that the waste facility for extractive waste cannot cause environmental pollution or its risks or accidents and that operations comply with Chapter 2 of the Waste Framework Obligations and principles. However, extractive waste from the prospecting of oil and evaporites other than gypsum and anhydrite shall be subject to the provisions of paragraph 1.
Paragraphs 1 to 3 shall also apply in the event of an investment from extractive waste to an empty quarry which is allowed to be filled with water after cessation of activity.
Using the best available techniques, the operator shall ensure that cyanide-soluble cyanide accumulates in the waste area of extractive waste as little as possible.
The concentration of cyanide soluble in acid in tailings shall not exceed 0,001 % by weight in the place where the waste is disposed of and derived from the waste from the extractive waste.
The environmental authorisation shall provide for more stringent requirements for the concentration of cyanide in low-acid acid, as provided for in paragraph 2, if the activity may result in environmental pollution or its risk. However, it is not necessary to give an order if, on the basis of the overall environmental hazard assessment, the operator reliably demonstrates that there are no such consequences.
In addition, the assessment of the amount of the security for the waste facility for extractive waste is, in addition to Article 60 of the Environmental Protection Act, taking into account the classification of the waste facility, the characteristics of the waste deposited, the future use of the land and other Annex 5. The above facts. Account must also be taken of the fact that the actions to be covered by the guarantee are assessed or carried out by an operator or a public authority.
The operator shall inform the Authority without delay and at the latest within 48 hours of the circumstances likely to affect the stability of the waste facility in the extractive waste facility and the monitoring and monitoring of the activities Factors which may result in environmental pollution or its risks or accidents.
The operator shall, where appropriate, take action in accordance with the internal emergency plan to prevent accidents or pollution.
The operator's obligation to draw up a plan for the monitoring and monitoring of waste from the extractive waste facility, to monitor and monitor the operation and to keep records of waste as provided for in Articles 118 to 120 of the Waste Act. The monitoring and monitoring data shall be kept together with the authorisation documents.
The monitoring and surveillance data of the extractive waste facility shall be provided to the Authority as provided for in the environmental permit. However, the data shall be transmitted at least once a year.
The obligation to notify the operator of the waste facility of the extractive waste facility is provided for in Article 81 of the Environmental Protection Act. The operator shall disclose the accounting records to the new operator.
In order to monitor compliance with the permit requirements, the Authority shall carry out an inspection in the area of waste from extractive waste from the extractive waste facility prior to the commencement of the deposit and on a regular basis of operation or use of the waste facility. After removal.
The provisions relating to the monitoring and monitoring plan for the area of waste from the extractive waste from the environmental permit and the provision of monitoring and monitoring results to the Authority are laid down in Article 62 of the Environmental Protection Act. (5 FEBRUARY 2015)
In order to ensure the reliability of monitoring and surveillance data, measurements and other studies shall be carried out by an independent expert on the operator.
The removal of the waste facility from the extractive waste facility and subsequent aftertreatment shall be laid down in the environmental permit or in a decision adopted pursuant to Article 94 (3) of the Environmental Protection Act. The waste facility shall be considered to be withdrawn when the waste facility has been inspected and approved by the Authority after verifying that the waste facility and the land area affected have been returned to a satisfactory state and that the The authorisation rules have been complied with. (5 FEBRUARY 2015)
The operator shall ensure that the structures necessary for the management of waste from the extractive extractive waste and its environmental load are maintained and monitored, monitoring is possible and, where appropriate, overflow channels and The floodholes are kept in operation and clean. The operator shall also inform the Authority without delay and take action to prevent accidents or environmental pollution, in accordance with Article 11 and Article 12 (2).
The operator shall be responsible for the aftercare activities after the decommissioning of the extractive waste facility and the associated monitoring and surveillance as long as this is necessary to ensure that the area does not: Environmental degradation or hazard, the area is stable and permanently landscaped, the area does not present any risk of an accident and the resulting environmental load or the area of surface or groundwater in the affected area is no longer needed.
The Food, Transport and Environment Agency shall, in the context of the environmental protection information system, provide information on the discarded or discarded serious environmental pollution or on waste from extractive waste resulting from its risk. The information on the waste facility shall be regularly updated. The information shall be published by electronic means.
Where extractive waste generated in operation is returned to an empty quarry for rehabilitation or construction purposes, the operator shall ensure that:
(1) the waste shall be disposed of in a geologically stable manner, as provided for in Article 7;
(2) the disposal of waste does not result in pollution of the soil, water or groundwater, and that the operation complies with the provisions of Article 8 (1);
(3) the activities are monitored and monitored in accordance with Article 14 (2) and (3).
In accordance with Article 18 (1) of Directive 2006 /21/EC of the European Parliament and of the Council of the European Parliament and of the Council on the management of waste from extractive industries and amending Directive 2004 /35/EC, the Finnish Environment Agency shall: Report on the implementation of the Directive in Finland. In addition, in accordance with Article 18 (2) and Article 22 (1) (a) of that Directive, the Finnish Environment Agency shall provide the Commission with information on the events reported by the operators pursuant to Article 11 and Article 14 (2). In accordance with
The Authority shall, without delay, provide the information communicated by the operator referred to in paragraph 1 to the Finnish Environment Agency.
This Regulation shall enter into force on 1 May 2013.
This Regulation repeals the Council Regulation on extractive waste (190/2008) .
This Regulation shall not apply if the waste facility for extractive waste has been withdrawn in accordance with the law before 13 June 2008.
Articles 3 to 6 and Articles 9 and 10 of this Regulation shall not apply where the environmental permit or equivalent authorisation for a waste facility has, before 13 June 2008, suspended or submitted an application not later than 1 In the case of waste from extractive waste from 30 April 2006 and the waste facility has effectively been withdrawn by 31 December 2010 at the latest.
Paragraph 9 (2) of Article 9 (2) on the concentration of soluble cyanide in tailings shall apply from 1 May 2018. However, that concentration shall not exceed 0,0025 % by weight of this Regulation.
Article 10 of this Regulation shall apply from 1 May 2014. Where an environmental permit is applied for before the above date, this Regulation shall apply to the authorisation procedure.
Directive 2006 /21/EC of the European Parliament and of the Council (32006L0021); OJ L 102, 11.4.2006, p. 15, Commission Decision 2009 /335/EC (32009D0335); OJ L 101, 21.4.2009, p. 25, Commission Decision 2009 /337/EC (32009D0337); OJ L 102, 22.4.2009, p. 7, Commission Decision 2009 /358/EC (2009D0358); OJ L 110, 1.5.2009, p. 39, Commission Decision 2009 /359/EC (32009D0359); OJ L 110, 1.5.2009, p. Commission Decision 2009 /360/EC (32009D0360); OJ L 110, 1.5.2009, p. 48Annex 1
Classification of extractive waste as permanent waste
1. This Annex defines the criteria for the classification of extractive waste as permanent waste. Classification shall be carried out in the context of the determination of the characteristics of the waste in accordance with Annex 3 to this Regulation using the data sources required therein.
2. The waste is considered a permanent waste within the meaning of Article 2 (1) (4) if the following criteria are met in both the short and the long term:
(a) the waste does not disperse or dissolve, or otherwise significantly change in such a way as to pose a risk to the environment or to human health;
(b) Sulphide sulphur content of waste
-not more than 0,1 %, or
-it is not more than 1 % and the neutralising potential ratio, defined as the ratio between the neutralising potential and the output potential based on the test method EN 15875 static test, is greater than 3;
(c) the waste does not present a risk of self-ignition or a burn;
(d) the concentrations of substances which may be harmful to the environment or to human health (in particular arsenic, cadmium, cobalt, chromium, copper, mercury, molybdenum, nickel, lead, vanadium and zinc) The waste is sufficiently low in such a way that the resulting risk to the environment and health is negligible in both the short and the long term;
-the concentrations of such substances are considered to be sufficiently low and, if they do not exceed the risk to the environment or health, if they do not exceed the Regulation (14/2007) The thresholds necessary for the assessment to be carried out or the background concentrations of the soil in the area;
(e) in practice, waste does not contain substances used in mining or treatment which may pose a risk or harm to the environment or to human health.
3. The waste may be considered as permanent waste without specific testing if, on the basis of the information available to the competent authority or the procedures or systems in place, it is reliably demonstrated that: The criteria have been sufficiently taken into account and the criteria are met.
Annex 2
Classification as a waste facility for mining waste from a major accident
This Annex defines the procedures and limit values to be followed in the classification of a waste facility as a waste facility for extractive waste from a major accident based on the following factors:
-the risk to the environment or to human health related to the structural stability or incorrect operation of the waste facility;
-the amount of hazardous waste disposed of in the waste facility; or
-the amount of chemicals that are hazardous to the environment or health of the waste facility.
The report on the classification of a waste facility in the event of an accident hazard shall be included in the waste management plan for the extractive waste. The classification shall be reviewed if the activity changes materially. The classification shall also always be reviewed at the end of the waste facility.
Points B and C of Annex B shall not apply to a waste facility with only permanent waste or unpolluted soil.
For the purposes of this Annex:
(1) Structural stability of the waste facility The ability of the region to keep waste within its borders as planned, taking into account the damage which may arise in the waste area in question; the assessment of the consequences of a deterioration of stability must take account of the damage caused by the area The immediate effects and the short-and long-term effects of the accompanying materials;
(2) Incorrect operation of Measures which may result in a major accident, including the disturbance or incorrect or inadequate design of environmental protection measures; the assessment of emissions of pollutants due to erroneous activity shall take into account short-term and The impact of long-term emissions during the operation and after-treatment phases of the waste facility; it shall include an assessment of the risk posed by waste facilities containing reactive waste, whether or not classified as hazardous waste Or other waste.
A. Risk of structural stability or incorrect operation of the waste facility
1. The waste facility is to be classified as a waste facility for mining waste resulting from a major accident, if the predicted loss of structural stability of the waste facility or damage caused by the misconduct of the waste facility is short or The long-term consequences, the whole life cycle of the waste facility and also taking into account the aftercare phase, may lead to the following situations:
-the loss of human life is very possible;
-a significant risk to human health;
-significant risk to the environment.
2. The consequences of the deterioration in the structural stability of the waste facility or of the damage resulting from the misconduct of the site shall be assessed as follows:
(a) The loss of human life and the risk to human health shall be considered negligible or not considered to be significant if the persons who are exposed to other effects are not expected to be present For periods of permanent or longer duration. A significant risk to human health is to treat personal injuries which cause disability or long-term health degradation.
(b) The risk to the environment is not considered to be significant if:
-a significant reduction in emissions of any pollutant source within a short period of time;
-there is no permanent or long-term hazard or damage to the environment in the waste facility;
-the environment exposed to the effects can be restored by means of minor rehabilitation and restoration measures.
(c) When determining the risk of loss of human life or of human health or the environment, account shall be taken of any specific estimates of the extent of the potential impact on the route-transit route-in the case of the recipient chain. If there is no route between the source and the consignee, the waste facility shall not be classified as an area of waste from the extractive waste posing a risk of a major accident from a deterioration in structural stability or damage resulting from incorrect operation. Based on.
3. The deterioration of the structural stability of the waste facility in the waste facility shall be considered a threat to human life in the case of water or slurry in the area rising at least 70 cm above the ground, or if the flow rate of the water or sludge erupting Exceeding 0,5 m/s.
The assessment of any loss of human life or of human health shall take into account at least the following factors:
-size and characteristics of the waste facility, including its structure;
-the quantity and quality of waste disposed of in the waste facility, including its physical and chemical properties;
-topography of the waste facility, including structures to prevent the spread of water or sludge;
-the transition period for a possible flood wave to areas where people are staying;
-the speed of the flood wave;
-the estimated level of water or slurry surface and climb speed;
-relevant regional factors, such as the climate and the annual variation in the crop, which may affect the extent of the loss of human life or the danger to human health.
4. In the case of the collapse of a waste mass, a landslide must always be regarded as a likely threat to human life if people are staying in the area of the avalanche.
The assessment of any loss of human life or of human health shall take into account at least the following factors:
-size and characteristics of the waste facility, including its structure;
-the quantity and quality of waste disposed of in the waste facility, including its physical and chemical properties;
-angle of inclination;
-the possibility of creating groundwater in the pile;
-underground stability;
-topography of the environment;
-proximity to water, structures and buildings;
-quarry facilities;
-other regional factors which could have a significant impact on the risk posed by the structure.
B. Amounting of hazardous waste disposed of in the waste facility
In accordance with paragraphs 2 and 3 below, the assessment of the classification of a waste facility based on the quantity of hazardous waste to be disposed of in the waste facility shall be carried out in accordance with paragraphs 2 and 3. On the basis of the total quantity of hazardous waste and waste. The amount of waste to be invested shall be assessed as dry weight.
2. The waste facility shall be classified as a waste from the extractive waste into a major accident on the basis of the amount of hazardous waste to be disposed of, if the ratio referred to in paragraph 1:
(a) exceeding 50 %;
(b) is between 5 and 50 %.
However, the waste facility referred to in point 2b shall not be classified as a major accident hazard on the basis of the quantity of hazardous waste disposed of as a waste facility if the classification is found to be unjustified in the region Risk assessment. The risk assessment shall be carried out as part of a classification based on the consequences of the deterioration of the structural stability of the waste facility or damage resulting from incorrect operation and shall pay particular attention to the The effects of waste.
3. The waste facility shall not be classified as a waste facility for the disposal of a major-accident waste facility on the basis of the amount of hazardous waste to be disposed of if the ratio referred to in paragraph 1 is less than 5 %.
C. Amount of chemical hazardous to the environment or health of the waste facility (5 FEBRUARY 2015)
In accordance with paragraphs 2 to 4 below, an assessment of the classification of a waste facility based on the amount of a chemical hazardous to the environment or to health that is to be deployed in the waste facility is to be assessed in accordance with paragraphs 2 to 4 below.
With a dangerous substance or mixture (dangerous chemical) Means the substance or mixture, the classification, labelling and packaging of substances and mixtures, and amending and repealing Directives 67 /548/EEC and 1999 /45/EC and amending Regulation (EC) No 1907/2006 In accordance with Council Regulation (EC) No 1272/2008, classify as a hazardous substance or mixture. Until 31 May 2015, it is also considered a dangerous mixture to be considered as a mixture of the Regulation of the Ministry of Social Affairs and Health on the classification and labelling of chemicals (2006) Is classified as a dangerous mixture.
2. As regards the waste facility for enrichment waste, the following procedure shall apply:
(a) Inventing the substances and mixtures used in such activities that are discharged after processing into the waste facility for tailings waste;
(b) Evaluate the amount of each substance and mixture used in the process for each scheduled year of operation;
(c) Determine whether a substance or mixture is a dangerous chemical;
(d) Calculate the increase in the volume of water in the waste facility for each scheduled year (ΔQ I ) In stable conditions using the following formula:
ΔQ I = (ΔM I *P, where:
-WHAT'S UP? I = annual increase in the volume of water in the waste facility in the waste facility (m 3 Year) in 'i',
-EAR. I = quantity of enrichment waste in the area per year (dry weight in tonnes/year) in the year 'i',
-D = average specific weight of the deposited dry enrichment waste (tonnes/m 3 ) And
-P = average porosity of the layer enrichment waste (m 3 /m 3 ) As a ratio between the number of sinuses and the total quantity of enrichment waste.
If accurate information on the specific weight and porosity is not available, the default values of D = 1,4 tonnes/m 3 And P = 0,5 m 3 /m 3 .
(e) Evaluate the maximum annual concentration (C) of each hazardous chemical identified in accordance with point 2c Maks ) In the water phase of enrichment waste by means of the following formula:
C Maks = ratio S I /ΔQ the maximum value of
-S I = the annual mass of the dangerous chemical identified in accordance with each 2c and in the year 'i'.
The waste facility is to be classified as a waste from extractive waste as a major accident if the aqueous phase of the enrichment waste is considered to be the maximum annual concentration (C Maks ) The presence of a dangerous chemical.
3. The classification of a waste facility which was operational on 13 June 2008 may also be based on the direct chemical analysis of the water and the solids in the waste facility. The waste facility is to be classified as a waste facility for extractive waste from a major accident, where the water phase of the enrichment waste and its contents are considered to be a dangerous chemical.
4. In the case of castration areas where the metals are separated from malt by means of a liquid solution, the presence of hazardous solute chemicals shall be determined at the sealing stage of the site. The report shall be based on the information on the solubility chemicals used and their residual concentration in the swamp water at the end of the reconstitution process. The waste facility is to be classified as a waste from extractive waste from a major accident if it is considered to be a dangerous chemical.
Annex 3
Definition of extractive waste characteristics
The definition and compilation of the characteristics of extractive waste shall be carried out in accordance with this Annex.
The relevant information on the waste shall be included in the waste management plan for the activities of the extractive waste.
A. Definition of the characteristics of waste
The determination of the characteristics of waste shall be based on the following information:
(a) Background:
-Description and objectives of the planned extractive activities.
-General information on the following:
-prospecting, extraction and enrichment activities;
-the type and description of the mining method and the enrichment process;
-final products.
(b) Geological data of the occurrence of the occurrence:
-Identification of the waste generated in the quarrying and enrichment by providing relevant information on the following:
-the nature of the surrounding bedrock, its chemical and mineralogical properties, including the transformation of mineral and non-mineral rock material;
-the nature of the deposit, including mineral material;
-in the case of mineral, mineral and hydrothermal-formed minerals, mineralisation typology, their chemical and mineralogical data, including physical properties such as density, porosity, granular distribution, and Water content;
-size and shape of the deposit;
-erosion and alteration of surface layers from a chemical and mineralogical perspective.
(c) Type of waste and its intended recovery or disposal:
-Description of waste from exploration, extraction and enrichment activities, including irtomas, side stones and tailings, by providing information on the following:
-the origin of the waste in the mining area and the process of producing waste, such as exploration, extraction, crushing and enrichment;
-the amount of waste;
-a description of the waste transport system;
-a description of the chemicals used for enrichment;
-classification of waste in the Council Regulation on waste (179/2012) , including the hazard characteristics of the waste in accordance with Article 3 of that Regulation;
-the type of waste facility planned, the final form of the waste to be disposed of and the method of placing the waste in the area.
(d) Geotechnical behaviour of waste:
-Identification of appropriate parameters to assess the essential physical characteristics of the waste, taking into account the type of waste facility.
-Suitable parameters can include: size distribution, plasticity, density and water content, degree of condensation, surgical strength and friction angle, permeability ratio, compression and consolidation.
(e) Geochemical properties and behaviour of waste:
-Specification of the chemical and mineralogical properties of the waste and its chemical and mineral residues.
-Estimate over time of variable leachate chemical properties by type of waste, taking into account the intended uses of waste, in particular:
-detection of leaching from metals, oxanions and salts over time by the pH of the solubility test, the flow-through test, the time-dependent solubility test and/or any other appropriate test;
-waste, static and kinetic tests containing sulphide in order to determine the formation of acidic leachate and the leaching of metals by time.
2. Waste classified as permanent waste in accordance with Annex 1 to this Regulation shall only apply to the relevant part of the geochemical testing referred to in paragraph 1e.
B. Data collection and evaluation
1. For the determination of the characteristics of the waste, existing studies and studies, including the information, geological surveys, relevant areas, shall be used in accordance with the technical requirements referred to in point A, European or national standards for waste catalogues, appropriate certification schemes and similar materials.
2. Data quality and representativeness shall be assessed and any missing information shall be identified.
3. If the data necessary for the definition of waste is missing, the sampling plan in accordance with EN 14899 shall be drawn up and samples taken in accordance with the plan. The sampling plan shall be based on the necessary identified information, such as:
-purpose of data collection;
-test programme and sampling requirements;
-the sampling points, such as the borehole, the wall of the quarry, the conveyor belt, the waste pile, waste facility or any other relevant location;
-the procedures and recommendations for the number, size, mass, description and treatment of samples.
The reliability and quality of the sampling results shall be assessed.
4. The results of the regulatory process shall be evaluated. Where necessary, additional data shall be collected using the same procedure.
Annex 4
Principles of action to combat major accidents, content of the internal emergency plan and information
A. Policy and Safety Management System
In the preparation and implementation of a major accident prevention policy and safety management system for the management of waste from extractive waste, account shall be taken of the following:
1. The operating principles for the fight against major accidents shall be set out in writing and included in the general objectives and policies to limit the risk of major accidents established by the operator.
2. The safety management system shall include a part of the general management system, including the organisational structure, responsibilities, practices, procedures, methods and resources for the prevention of major accidents The definition and implementation of policies. The description shall include the name of the responsible person in the extractive waste facility and the names and responsibilities of the persons involved.
3. The safety management system shall cover:
(a) organisation and staff: the tasks and responsibilities of personnel involved at all levels of the management of major-accident hazards, the identification of the training needs of staff and the organisation of training, and staff and, where appropriate, The participation of staff of subcontractors working in the waste facility;
(b) identification and evaluation of major-accident hazards: the establishment and implementation of procedures for the systematic identification of major-accident hazards occurring in normal or normal abnormal operations; And assess their probability and severity;
(c) operational control: the introduction of procedures for the safe use and maintenance of the waste facility and its processes and equipment, as well as the provision of instructions;
(d) changes management: the establishment of procedures and the introduction of changes in waste facilities or new waste facilities;
(e) planning for emergency situations: the establishment and implementation of procedures for the identification of foreseeable emergency situations through a systematic assessment and the establishment, practice and review of Emergency plans and thus manage such incidents;
(f) monitoring of implementation: the establishment and implementation of procedures for the continuous assessment of the operation of the operator's operational principles and safety management systems for the prevention of major accidents; As well as procedures for investigations and corrective actions, in the event that the principles and systems do not exist; the procedures must include operators' reporting systems for major accidents or near misses, in particular: Where there has been a lack of security, and Their investigation and monitoring procedures, taking into account past experience;
(g) evaluation and review: the establishment and implementation of procedures for systematic evaluation of major accident prevention policies at regular intervals; and The effectiveness and relevance of the safety management system; a written assessment of the level of senior management and the level of the safety management system and the updating thereof.
B. Contents of the internal emergency plan
The internal emergency plan shall include at least the following:
1. Names and tasks of persons responsible for:
(a) internal emergency measures for the waste facility in the extractive waste facility and which are authorised to initiate rescue operations;
(b) contacts with authorities responsible for external emergency plans.
2. Report on the Policy Document and the Safety Management System.
3. Description of the measures to be taken in foreseeable circumstances to control and limit the consequences of accidents and to correct the effects of accidents.
4. Actions aimed at limiting the risks to people in the region, including the alarm system and instructions for behaviour in the event of an alert.
5. Assessment of the impact of accidents outside the waste facility.
6. Procedures for notification to the rescue authority in the event of an accident and an explanation of what information will be provided immediately and how more detailed information will be provided as they are received.
7. Training and coordination of staff with external civil protection measures.
8. Support for rescue operations outside the waste facility.
C. Information (5 FEBRUARY 2015)
In the event of a major accident, the persons and entities referred to in Article 115 (4) of the Environmental Protection Act shall be given at least the following information free of charge:
1. Name of the operator and location and address of the waste facility in the extractive waste facility.
2. Name and status of the person providing information.
3. Confirmation that the activities of the waste facility have to comply with the Environmental Protection Act and this Regulation and the authorisation rules adopted pursuant thereto, and that the required information on the prevention of a major accident has been provided to the relevant authorities.
4. A clearly defined description of the activities or activities in the waste facility.
5. The commonly used names, group headings or general categories of hazard and information on the main hazardous properties of substances or waste disposed of in the waste area.
6. General information on the nature of the hazards of major accidents, including their potential impact on the population and the environment in the affected area.
7. Appropriate information on how to alert the affected population to the accident and how it will be kept up to date in major accidents.
8. Appropriate information on the action to be taken by the population in the affected area and how it should behave in the event of a major accident.
9. Confirmation that the operator has a duty to take appropriate action in the area and, in particular, to contact the rescue operation in order to be able to function properly and minimise the consequences thereof.
10. Advertising of the external emergency plan to manage the effects outside the affected area and the call for compliance with the rescue instructions or requirements in the event of an accident.
11. Information on where other relevant information may be obtained, in so far as they are not confidential under the law.
Annex 5
Assessment of the amount of the security of the extractive waste facility
The amount of the security for the waste facility shall be assessed on the basis of at least the following information or items:
1. The likely effects of the waste facility on the environment and human health
2. The need for rehabilitation of the waste facility, including its future use.
3. Applicable environmental standards and environmental objectives, including the physical stability of the waste facility, minimum standards for soil and water quality, and maximum pollutant emissions.
4. The technical measures necessary to achieve the environmental objectives, in particular to ensure the stability of the waste facility and to limit environmental damage.
5. The measures necessary to achieve these objectives during and after the closure of the waste facility, including, where appropriate, soil rehabilitation, aftercare and monitoring, as well as actions related to the restoration of biodiversity.
6. Duration of impacts and measures necessary to mitigate them.
7. An independent and competent estimate of the costs of the necessary measures for the rehabilitation of the soil and the disposal of the waste facility and for the organisation of after-care, including possible monitoring or contamination of the soil During the post-treatment period; the assessment shall take into account that the waste facility may have to be withdrawn in an unplanned or timely manner.
This Regulation shall enter into force on 20 February 2015.
Directive 2006 /21/EU of the European Parliament and of the Council (32006L0021); OJ L 102, 11.4.2006, p. 15, Commission Decision 2009 /337/EC (32009D0337); OJ L 102, 22.4.2009, p. 7
