Source: https://www.global-regulation.com/translation/sweden/2987621/regulation-%25282013%253a319%2529-of-extractive-waste.html
Timestamp: 2019-11-18 09:02:18
Document Index: 224478033

Matched Legal Cases: ['§ 70', '§ 1', '§ 52', '§ 15', '§ 40', '§ 2', '§ 53', '§ 74', '§ 57', '§ 77']

Machine Translation of "Regulation (2013:319) Of Extractive Waste" (Sweden)
Regulation (2013:319) Of Extractive Waste
Original Language Title: Förordning (2013:319) om utvinningsavfall
Article 1 this regulation lays down provisions on
precautions to prevent or, as far as possible
limit the harmful effects on human health and the environment
may arise as a result of the management of waste from the industrial
that extracts topics and materials by breaking or at
otherwise remove them from the Earth's crust or processing or
otherwise handles quarried materials
(extractive industries). The regulation is notified
1. with the support of the 15 Cape. section 9 of the Environment Act in respect of sections 14 to 22,
paragraph 30, 55, 56, 65, 67 to 69, § § § 70 2 and 74, 77
and paragraphs 78,
2. with the support of the 15 Cape. section 28 of the environmental code in terms of 14 and 20,
22-27, 29-81, 85 and 86 § §,
3. with the support of 26 kap. section 19 of the environmental code in the case of 23-27 and
29 sections, section 30 of the second and third subparagraphs, 31-54 and 57-64 § §,
70, § 1 and 73, 76, 85, and 86 § §,
4. with the support of 27 Cape. section 2 of the environmental code in respect of section 88, and
5. Moreover, pursuant to Chapter 8. section 7 of the Constitution.
Discovery: natural occurrence of mineral in the Earth's crust,
energy raw materials, soil or rock, or other substance that does not
mining: activities that involve breaking, drilling
or blow up in the Earth's crust, or otherwise disconnect
material from the Earth's crust in order to charge a deposit
or substances or material from a deposit of the
the Earth's crust,
extracted material: material that has been released
through extraction,
exploration: activities involving that
sampling, drilling, trenching, or otherwise
systematic searches for a discovery that has an economic
value, but not activities needed to prepare
the extraction of such deposit and not activities that have
directly related to the ongoing recovery, and
processing: activities aimed at by a mechanical
process, a chemical process, a biological process or a
thermal or other physical process, or a combination
of such processes are separate or concentrate substances or
material from the quarried materials or from previous
bortskaffat extractive waste, but not smelting or other
heating processes than lime-burning and no metallurgical
paragraph 3 of the waste referred to in this regulation is the same as for 15
Cape. section 1 of the Swedish environmental code, with chemical product is the same as for 14
Cape. section 2 of the Swedish environmental code and with recycling and disposal
the same as in the waste regulation (2011:927).
4 section With extractive waste as referred to in this regulation waste
have been incurred as a direct result of prospecting, extraction
or processing or as a direct result of the storage of
quarried materials before processing of the material has
paragraph 5 of this regulation,
"hazardous waste" means any substance or object which is waste that is
marked with an asterisk (*) in annex IV to the
Waste Regulation (2011:927) or according to regulations
announced pursuant to section 12 of the hazardous waste regulation
dangerous chemical product "means a chemical product that meets
the criteria for classification as dangerous according to
European Parliament and Council Regulation (EC) no 1272/2008 of the
16 december 2008 on classification, labelling and
packaging of substances and mixtures, amending and repealing
by directives 67/548/EEC and 1999/45/EC and amending
Regulation (EC) No 1907/2006 (Reach) or regulations if
the classification and labelling of chemical products
The Swedish Chemicals Agency has announced.
6 § with inert waste as referred to in this regulation
1. not in any significant degree may decay or be resolved
up or otherwise change in any significant way that can
cause damage to human health or the environment,
2. does not contain more than
(a)) 0.1% sulfidsvavel, or
b) 1% sulfidsvavel, if the
neutraliseringspotentialkvot is greater than 3,
the ratio between neutraliseringspotentialen and syrapotentialen,
When a static testing according to the standard EN 15875:2011,
3. not likely to ignite spontaneously and can not burn,
4. neither in its entirety or in its fine fraction contains a
higher levels of arsenic, cadmium, cobalt, chromium, copper,
Mercury, molybdenum, nickel, lead, vanadium, zinc or something
other substances that can be harmful to human health or the
environment than to the risk of such damage is insignificant and
content must not exceed the level that can be considered the
national natural background concentration, and
5. in essence, free from such substances used
When extracting or processing and may be harmful to human
7 § With unpolluted soil referred to in this regulation cover soil
in connection with the extraction has been removed from the upper
layers that are not contaminated.
section 8 of this regulation, '
waste tray: plant or naturally occurring
area where such fine-grained extractive waste generated
during processing or treatment or recycling of
process water is disposed of along with water, and
landfill: plant on the surface of the ground where the fixed
extractive waste is disposed of.
section 9 With extractive waste facility as referred to in this regulation
a waste tray, a waste disposal site or a different area
intended for collection or disposal of
extractive waste in solid or liquid form, with the
pond levees and other structures that are designed to keep
left, hold back, delimit or otherwise support the
An area designated for the accumulation of extractive waste, however, is
an extractive waste facility only if the area is a
risk system or used for collection for a longer
period than
1. six months in the case of hazardous waste generated
2. a year in the field of extractive waste is neither hazardous
waste or inert waste, or
3. three years in the case of waste which
a) is inert extractive waste or non-polluted soil,
(b)) is the extractive waste from prospecting which is not dangerous
c) is waste from the extraction, processing or storage of
With extractive waste facility referred to do not a cavity as
have arisen during the extraction and extractive waste where other than
hazardous wastes are added back for construction purposes or
as a avhjälpandeåtgärd.
10 § risk facility referred to in this regulation cover a
extractive waste facility
1. whose characteristics are such that the assessment under
44 § give reason to suspect that an error or a deficiency in the facility
or in the operation of it could cause a serious
2. containing hazardous waste in such quantity that the proportion of
hazardous waste in the plant at the assessment under section 51
means that the plant should be considered a risk facility,
3. whose aqueous phase or liquid has such a chemical
composition at a calculation or assessment
According to § 52, 53 or 54 shall be deemed to be a dangerous chemical
section 11 With leachate as referred to in this regulation fluid after
having been in contact with extractive waste in a
extractive waste facility leaves the plant or mass
up in the facility and that can have harmful effects on the environment
If it is not handled appropriately.
section 12 of this regulation,
waste prevention measures: measures taken before a
substance, material or product has become waste, and that
aim at reducing the amount of hazardous substances in materials
or products, reducing the amount of waste or a
reduction of the negative effects on human health and the
the environment as waste raises,
waste management plan: plan for how a business
taking waste prevention measures, recycle, dispose
or otherwise physically manage extractive waste as well as
handle the dangers and consequences of accidents so that a
sustainable development is promoted,
serious accident: event in a location where extractive waste
handled as is attributable to the handling and carrying
serious risk to human health or the environment in the short
or long term, and
extractive waste fixed structural integrity: a
utvinningsavfalls-fixed ability to retain
extractive waste within the facility.
section 13 with the supervisory authority referred to in this regulation the
authority under the environmental protection Decree (2011:13) has
the operational supervisory responsibilities to this regulation
section 14 of this Regulation shall apply to professional management
of extractive waste, subject to the provisions of §§ 15-21.
section 15 of the Ordinance shall not apply in the case of
extractive waste resulting from prospecting, extraction, or
processing carried out at sea or on the sea floor, about
the activities are carried out outside the low-water line for normal
or medium tides.
section 16 of the Ordinance shall not apply in the case of Grouting
of water in a geological formation from which hydrocarbons or
other substances have been extracted or into geological formations which
for natural reasons are permanently unsuitable for other purposes, if
the injection does not compromise the opportunities to achieve good
groundwater status pursuant to the Regulation (2004:660) if
management of the quality of the aquatic environment and
1. the water contains only substances from prospecting or
2. the injection is done for technical reasons and the water does not
contains other substances than those from
exploration or extraction, or necessary for such
section 17 of the regulation shall not apply to the reversal of
pumped groundwater in connection with mining or in
associated with the construction or maintenance of buildings or
plants, if the reversal does not compromise possibilities
to achieve good groundwater status, according to the Regulation (2004:660)
on the management of the quality of the aquatic environment.
section 18 in respect of inert waste and unpolluted
soil in an extractive waste facility, 69, 72, 74, 75 and
86 §§ apply only if the facility is a risk facility.
section 19 in respect of extractive waste in a
extractive waste facility which is neither hazardous waste
or inert waste, 69, 74, 75 and 86 §§
applicable only if the plant is a risk facility.
section 20 provisions of 57 to 63, 77-79 and 88 § § shall not
apply to holdings covered by the Act
(1999:381) on pollution prevention and control
the consequences of serious chemical accidents.
section 21 if during the application process under the environmental code, or
older regulations given conditions on safeguards
or other precautionary measures that are more stringent than
the provisions of this regulation, to the stricter requirements apply.
Management of extractive waste
section 22 of The who in their business generates or handles
extractive waste shall take the waste prevention measures,
promote the recovery of the waste which is suitable from
the point of view of the environment and dispose of waste in a way that is
safe for human health and the environment in the short and long term
1. manage the waste according to the waste management plan
applies to the handling of waste,
2. take into account waste already in the design
of the business and, if the business involves the extraction or
processing, in the selection of methods for the extraction and
3. take into account the changes introduced by the waste may be
undergo in terms of increased surface size or because of
exposure to conditions above ground;
4. put back the waste in the cavity arising
during the extraction, if technically and economically
5. dispose of the waste in a way that, as far as possible
ensures the extractive waste facility's long-term
physical and chemical stability and prevents serious
6. after the closing of an extractive waste facility post
back topsoil, if possible, and otherwise,
7. when machining choose to, in accordance with Chapter 2. 4 §
the environmental code, use of hazardous chemical products
less dangerous if there are multiple products to choose from,
8. take the waste prevention measures and
measures that promote recycling law or
other regulation as well as ensure that disposal of waste
in a manner which is safe for human health and the
the environment in the short and long term.
section 23 of the operator of an activity which gives rise to
extractive waste or operating an extractive waste facility
must have a waste management plan.
section 24 of the waste management plan shall contain
1. a description of the activities and measures
that gives rise to the extractive waste and all subsequent
management of the waste;
2. a description of how its harmfulness are prevented
or reduced by reference to waste management are
the design of the business,
3. a description of how the chosen methods of extraction and
processing prevents the formation of waste and waste
harmfulness of the business means the extraction or
4. documentation of characterization in accordance with section 30 of the
extractive waste resulting or handled in the activities
and an explanation of how the disposal of such waste can
impair human health and the environment,
5. data on the estimated total amount of
extractive waste that will occur or be managed in
6. a description of the measures that will be taken to
avoid pollution of air, surface water and groundwater as well as
ground handling of the extractive waste, and
7. a description of how the business in General will
follow 22, 51-56, 67 – 71 and 74 sections.
section 25 where a business is a
extractive waste facility, waste management plan
1. an assessment of whether the property is or will be
become a risk facility,
2. a description of the area that will be affected by
3. information on how the plant continuously monitored
4. an explanation of how the facility will be closed with
(a)) details of how the area affected by the installation
to be used after shutdown,
(b)) the data on the plant's physical stability, highest
values for emissions of polluting substances, applicable
environmental quality standards and other environmental quality objectives that have
relevant to the assessment of what is required to
ensure that the area affected by the plant can
restored to a satisfactory condition and use
without causing harm or inconvenience to human health
or the environment and without compromising the possibilities to follow
environmental quality standards,
c) information on the measures for ensuring
the resort's stability, restoration, monitoring,
restoration of biodiversity and other
measures need to be taken during and after the closure of
to comply with the environmental quality standards and meet the environmental quality objectives
and the goal of rehabilitation referred to in (b), and
d) information on the estimated time for the resort's
impact on human health and the environment and for the
reparation measures will be needed, and
5. a description of how the business in General will
follow 55, 56, 67 – 71 and 74 sections.
If the plan relates to an extractive waste facility that does not
is deemed to be or become a risk facility, should the plan contain
an account of the circumstances which are the basis for
assessment and data on the identified hazards for
accidents as the facility is associated with.
section 26 Of the risk in a business establishment or a
facility that has been judged to be a risk facility,
the waste management plan, moreover, contain the particulars of the
strategy for prevention of major accidents, the
security management system for the implementation of the strategy and the
internal emergency plan referred to in section 57.
section 27 of the waste management plan shall be sent to
section 28 Of a waste management plan have not been tried in the framework
for a procedure, the supervisory authority shall examine whether
the plan meets the requirements of this regulation. If the plan is
deficient, it shall submit to the operator
to remedy the deficiency.
section 29 the operator shall review the waste management plan
as soon as there is reason to do so, and at least every five
year. Changes to the plan shall, as soon as possible be notified to
Characterization of extractive waste
section 30 of The program according to section 23 shall have a waste management plan shall
characterize the extractive waste resulting or
handled in the activities so that waste can be handled in the
meaning of section 22.
Characterization should be documented and include the
information set out in paragraphs 31 to 36 and, if necessary, include
the information is relevant for assessing whether
extractive waste is inert.
The collection and evaluation of information shall be carried out on the
as indicated in paragraphs 38 to 43.
31 § documentation shall contain a general description of the
the background to and objectives of the extraction with the overall
1. the exploration, extraction and processing,
2. the methods of extraction and processing to be used
and a description of the methods, and
3. the intended final product characteristics.
32 § documentation shall contain such information on
geological conditions at the site of the discovery to be
be extracted that are of significance for identifying the
extractive waste extraction and processing produce
1. the surrounding mountain's chemical, mineralogical and other
characteristics and possible hydrothermal quartz transformation of both
mineralized as other parts of the surrounding rock,
2. type of deposit and full size and geometry,
3. type of mineralization and Northern chemical and
mineralogical characteristics and density, porosity,
particle size distribution, moisture content and other physical
4. chemical and mineralogical properties and density,
porosity, particle size distribution, moisture content and other
physical properties of occurring gaits and
hydrotermalt newly created mineral, and
5. weathering and near-surface conversion in chemical and mineralogical
33 § documentation shall include a description of the
extractive waste arising from the exploration,
the extraction and processing of information for each
1. where on the extraction site waste comes from and the
or the activities which will give rise to
2. the total quantity of waste which may arise,
3. the transport system for the waste;
4. the chemical products used in the processing and
product stability,
5. any hazardous characteristics listed in annex 1 to
Waste Regulation (2011:927) and if the waste is hazardous
6. type of intended extractive waste facility, final
exposure form of waste and method of disposal of
34 § documentation shall contain, for each of the types of waste
information is relevant for assessing the
physical properties. The assessment shall take into account
type of extractive waste facility and its
granulometry, plasticity, density, moisture content,
compaction ratio, shear strength, friction angle,
permeability, portal, compressibility and consolidation.
35 § documentation shall contain, for each waste type
information on the chemical and mineralogical characteristics
in the short and long term, and any additives and residues in
36 § documentation shall for each waste type, and with
taking into account the intended handling, contain
information about the chemical composition of the scheme over time in the
leachate as waste. This documentation
should include information on
1. leaching of metals, oxyanjoner and its salts, as determined
by pH-dependent, time-dependent percolation leaching,
release or other appropriate test methods, and
2. the onset of acidic leachate and leaching of metals in
the sulphide bearing wastes, defined by static or kinetic
In the case of inert waste needs documentation
referred to in the first subparagraph include only information from
applicable geochemical testing.
The collection and evaluation of information for
37 § the information necessary for characterization of
extractive waste pursuant to sections 31 to 36 should be collected and evaluated
According to sections 38 to 43.
section 38 as a basis for characterization of extractive waste
such information shall be used that meet the requirements of 31-36
sections and see
1. geological surveys,
2. studies on similar sites,
3. lists of inert waste,
4. appropriate certification system or European or
national standards for similar material,
5. previously granted permission, or
6. other surveys or studies.
39 § an evaluation should be made of the quality of information
and whether or not it is representative. Any missing
information should be identified.
40 section if it is missing information necessary for
characterization of the waste, a sampling plan
be established in accordance with the standard EN 14899:2005 and samples
According to the plan of sampling and testing shall be carried out.
41 according to § 40 of the sampling plan shall be based on the
information for the plan's effectiveness has
identified in the case of
1. purpose of data collection,
2. inspection programs, and sampling requirements,
3. samples from drill cores, break fronts, conveyor belts,
landfill, the waste tray or other relevant
sampling sites, and
4. procedures and recommendations for the number of samples and
the size, weight, description, and management.
42 § Sampling validity and quality
43 § the results of characterization to evaluate. If the
further information is required for characterization, the
be collected in the manner provided in sections 38 to 42, and then
Assessment of an extractive waste facility shall be deemed to be
a risk plant
section 44 in determining whether an extractive waste facility,
considered to be a risk facility under section 10 first paragraph 1 shall
taking into account the whole life cycle of the plant, including the time
After the closure, as well as the size, location and
environmental impact at every point in its lifecycle. Plant
shall be deemed to be a risk facility if the deficiency
1. is attributable to the plant's structural integrity
or operation, and
2. could cause
a) a non-negligible probability of death,
(b)) a serious danger to human health, or
c) a serious danger to the environment.
45 § assessment of consequences and seriousness under section 44 shall
1. the immediate impact of materials as a result of a
a deficiency in the structural integrity of the plant can be
be discharged from the plant and the subsequent short-and
long-term effects of such emissions, and
2. emissions of pollutants caused by poorly functioning
protection measures, faulty or inadequate design or
other incorrect operation of the facility, taking into account
(a)) the effects of both short-term as lasting emissions of
b) facility operating time and the time after closing, and
(c)) the danger that reactive wastes in the plant, regardless of
If it is a hazardous waste or not.
section 46 The likelihood of death and danger to human
44 health referred to in § 2 shall be considered as negligible or not
serious about no other persons than those who manage the operation of the
the plant can be expected to be present permanently or
for long periods in the area that may be affected by
the shortage. Damage that can lead to disability or
longer periods of poor health must be regarded as a serious
danger to human health.
47 § The danger for the environment as referred to in paragraph 2 of section 44 shall not be deemed to
serious, about 1. the potential contamination greatly diminishes in strength
within a short period of time,
2. scarcity does not lead to any lasting or long-term
environmental damage, and
3. the impact on the environment can be restored with small
48 § in the assessment of the likelihood of death and danger
to human health or the environment as referred to in section 44, the
potential effects should be assessed taking into account both
pollution source and pollutant dispersal route that the
humans and the environment to be protected. Flaws in a
fixed operational or structural stability to bring
the plant is considered to be a risk only if it
There is a propagation path between the source of contamination and the
humans and the environment to be protected.
49 § assessment of the likelihood of death or danger to
human health as a result of such a deficiency in a
waste tray structural integrity referred to in section 45 1
should include 1. the size, shape and other characteristics,
2. the volume of extractive waste in the facility and its
physical, chemical and other qualitative characteristics,
3. damping and other topographic features in and around
the area of the holding,
4. estimated time before a potential tidal wave reaches the areas where
people find themselves and such a flood routing
propagation speed,
5. estimated level and pitch rate for water or
the mixture of water and fine-grained extractive waste in
areas where the people are, and
6. other circumstances that are typical of the place where the
the plant is located, and that affects the likelihood of
death or danger to human health.
Deficiencies in the structural integrity of the waste tray must
always be considered a non-negligible probability for
death, if the level of the water or the mixture of water
and fine-grained extractive waste is at least 0.7 metres above the
ground level or if the speed of the water or mixture
of water and fine-grained extractive waste exceeds 0.5
section 50 of the assessment of the likelihood of death or danger
for human health referred to in paragraph 2 of section 44 on the grounds of racial or
landslides in a landfill shall cover
1. upplagets the size, shape and other characteristics,
2. the volume of extractive waste into the pile and its
3. upplagets släntlutning,
4. the possibility of a local ground water area can occur in
5. stability during the plea,
6. the topography,
7. proximity to surface water, plants and buildings,
8. access to current or previous extraction, and
9. other circumstances that are typical of the place where the
warehouse exists and contributes significantly to the danger.
Landslides at a landfill shall always be considered to confer a
non-negligible probability of death, if people can
come to reside within the reach of the waste loads
that may be in motion.
51 § extractive waste facility as at the end of the
the planned operation is expected to contain hazardous waste into a
certain share, determined on the basis of an estimate of the weight ratio
between the dry matter of the hazardous waste and
dry weight of all waste that is expected to be in
the plant at the end of the planned operation, shall be deemed to
be a risk facility, if
1. the proportion of hazardous waste exceeding 50 per cent, or
2. the proportion of hazardous waste amounts to 5% or more but
not more than 50% and the other judgement cannot be justified by
a) content of hazardous waste,
b) circumstances which is typical of the place where the
the plant is located, and
(c)) that there is no need to fear that an error or a
deficiency in the plant or in the operation of it would get
An extractive waste facility shall not be deemed to be a
risk facility due to the proportion of hazardous waste, if the amount of
hazardous waste is below 5 percent.
52 section On assessing whether a planned waste tray is a
risk facility to calculate the danger posed by aqueous phase
1. take an inventory of the chemical products that will be used when
processing and then be discharged into the waste tray
tillsamamans with the fine-grained extractive waste,
2. for each year that the plant is planned to be in operation
make an estimate of the amount of chemical products
to be used in the processing,
3. for each chemical product to use when
processing determine whether the product is a dangerous chemical
4. for each year that the plant is planned to be in operation
calculate the annual increase in the number of cubic metres of stored water
in the waste tray for stationary conditions by
a) determine the number that indicates the number of tons of fine grained
extractive waste (dry weight) which are placed in
waste tray,
b) determine the number indicating it disposed of fine-grained
extractive waste's average dry bulk density in tonnes
c) divide the number referred to in point (a) of the number referred to in point (b);
d) multiply the result of (c) with the number indicating the
the sedimented fine-grained extractive waste's average
porosity, defined as the ratio of håligheternas
volume i number of cubic meters and it remained fine
the total volume of the extractive waste, in number of cubic meters, and
5. for each hazardous chemical product as determined in accordance
with 3 estimate the maximum annual concentration in the aqueous phase
a) determine the number that indicates the number of tons of the chemical
the product placed in the waste tray, and
b) divide the number referred to in point (a) of the number
the result of the calculation according to the 4.
If exact information is missing for the values in the first paragraph 4,
the default value of 1.4 tons per cubic meter can be used to
determine the dry bulk density as referred to in the first subparagraph 4 (b)
and the default value 0.5 cubic meters per cubic metre be used
to determine the porosity within the meaning of the first subparagraph 4 (d).
If the aqueous phase in the light of the estimate in 5 groups
dangerous chemical product, the waste tray is considered to be a
risk facility.
§ 53 when assessing whether a waste tray into operation shall
considered to be a danger hazard of aqueous phase installation shall
calculated in the same manner as under section 52 or based on a
direct chemical analysis of the water and fine-grained
extractive waste found in the plant. If the aqueous phase and
its content is a dangerous chemical product, complex
considered to be a risk facility.
54 section When a facility where metals are separated out or
concentrates from ore stockpile by percolation of
lakningslösningar (leaching) is closed to a
inventory is made by using the lakningskemikalier and
the amount of residue in drainage systems after
finished rinsing. If the liquid in the drainage systems is a
dangerous chemical product, the plant is considered a
The location and design of a
55 § location of an extractive waste facility shall be
appropriate in light of
1. the geological, hydrological, seismic, geotechnical and
hydrogeological conditions on and around the site, and
to the danger of flooding, subsidence, landslides,
avalanches and erosion,
2. the presence of groundwater, surface waters and coastal waters, and
3. the protection of the cultural and natural values and the existence of
56 section On who operates or intends to operate a
extractive waste facility shall ensure that the facility
be designed so that
1. it is appropriate to take account of the possibilities for
operation of the plant, and after it has been shut down to comply with the
waste management requirements imposed by the Swedish environmental code and
regulations issued on the basis of the beam,
2. the adverse effects on human health and the environment are avoided
3. it is and will continue to be stable, geotekniskt
4. after closing requires a minimum degree of
monitoring, maintenance and control.
Strategy for preventing major accidents and
security management system and internal emergency plan
57 § if there is a risk in a business establishment, the
the responsible party shall ensure that for the
strategy to prevent serious accidents, a
security management system for the implementation of the strategy and a
internal emergency plan specifying the measures to be
taken at the facility in the event of a serious accident.
Strategy, the security management system and the internal
the contingency plan should be tailored to the risk of
serious accidents as the facility is associated with under
the operation and after closure.
58 § Strategy should be documented and include
overall aims and principles of action for the management of
dangers of serious accidents and a description of how
security management system is structured.
59 § the operator shall ensure that the supervisory authority
get a copy of the strategy and the internal emergency plan.
60 § security management system shall relate to the governance of
operations in terms of organization and responsibilities,
methods, procedures and other procedures and resources to
design and implementation of the strategy.
The safety management system should include the procedures and
instructions that need to be determined and applied
1. tasks and responsibilities to the staff at all
levels of the organization involved in the effort to manage
dangers of serious accidents, identification of
training needs and implementation of training
needed, as well as other employees and any contractors '
2. to systematically identify dangers of serious
accidents arising from normal and abnormal
operational conditions and to evaluate such farors probability
3. the maintenance of the complex, the processes, the
equipment, the measures in case of temporary interruption or the like
otherwise needed for a safe operation,
4. to plan and implement new construction or other
changes in the plant,
5. that with systematic analysis to identify foreseeable
emergency situations and to prepare, test and review
contingency plans designed for such situations,
6. to report the discovery of the security measures that are not
works, incidents, and serious accidents,
7. to examine, monitor and learn from the experience acquired,
continuously assess how security management system consistent
with the objectives and principles referred to in paragraph 58 and to explore
and correct non-compliance,
8. to regularly and systematically make a revision and
review of the strategy and security management system
efficiency and convenience, and
9. to inform the operator's senior management about
the results of the audit and review and, if necessary,
decide on updates as well as to document the highest
management's review of the strategy and
the security management system.
61 section in the operator's organization, a person in
supervisors are appointed to have the operational responsibility to
the strategy is implemented and continuously supervised.
62 § the operator shall consult with the municipality and the
employees and other personnel who could affect the dangers of
serious accidents when the internal emergency plan
63 § internal emergency plan should always include
1. the names or positions of persons authorized
to start an internal emergency response as well as on the people
its task is to ensure coordination of immediate
2. indication of who or what is responsible for the contact with
the municipality in the case of such an emergency plan which
the municipality establishes under Chapter 3. section 6 of the Regulation (2003:789)
on protection against accidents,
3. a description of the measures to be taken to
prevent and mitigate severe damage to human health and the
the environment for any situation or the kind of event that can
foreseen and which operations can play a crucial role
for the emergence of a serious accident and other incidents,
with an account of available equipment and
the resources available to deal with such situations and
4. a description of the warning system and the measures to be
taken at the alert as well as the measures in General aimed at
to limit damage to human health,
5. a description of procedures for alerting of the municipality
Organization of emergency assistance in the event of a serious accident and
the information to be provided in case of alarm,
6. a description of procedures for cooperation with the municipality's
Organization of emergency assistance in the event of a serious accident, with
procedures for how support should be provided for interventions outside
7. a description of how the staff are trained and exercised,
8. a description of how the samövning with the municipality's organization
for civil protection is implemented, if such a samövning is needed,
9. a description of the plans for how the environment can be
cleaned up and restored after a serious accident in order to
Information on applying for a licence
64 § it as in the case of activities covered by this
Regulation applies for a licence referred to in 9
or Chapter 11. the environmental code, in connection with the application, inform
the licensing authority if
1. who operates or intends to operate,
2. the location where business is conducted or to be conducted on
by describing the location and possible alternative sites,
3. content of the waste management plan as required by
4. the security in case of an extractive waste facility
According to an independent qualified appraisal required by 15
Cape. 34 § environmental code and the attention that has been given to a
any unplanned or early closure of
the plant and the additional costs that such a closure,
5. how the otherwise ensure that the provisions of this
Control before disposal started
65 § the operator of an extractive waste facility shall see
to disposal of extractive waste does not start
before the supervisory authority has verified that the facility
meets the requirements placed on it
State, announced regulations and decided
section 66 if the supervisor determines that the requirements referred to in
section 65 are fulfilled, it shall notify the
the operator that the disposal operations may commence.
Operation of an extractive waste facility
67 § the operator of an extractive waste facility shall see
the facility is consistent with the municipality's waste plan
According to chapter 15. section 11 of the environmental code.
68 § the operator of an extractive waste facility shall operate
and maintain the facility in a way that in the short and long
term ensures its physical stability and to prevent
accidents, pollution of soil, air, surface water and groundwater
and as far as possible, minimize the damage on
69 § the operator of a waste tray, shall ensure that
the concentration of cyanide or cyanide compounds as
are dissociated with a weak acid at a specified asset value
(pH) is as low as possible in the tray.
The concentration may not exceed 0.001% by weight (10
weight-ppm) the point where extractive waste discharged to
the waste tray.
70 § the operator of an extractive waste facility,
1. understanding of the characteristics of the waste
to be disposed of has in regards to produce leachate,
If the pollutants which the leachate may contain and
If the plant's water balance, and
2. ensure that the leachate and other polluted water from
the plant is taken care of and if necessary cleaned so that the water
can be discharged from the facility without the spill battles
on environmental quality standards for water or other provisions
for the protection of human health or the environment or against
terms and conditions that apply to your business.
The closing of an extractive waste facility
71 § the operator or close a
extractive waste facility, in conjunction with the
the plant is closed, make sure that the area has been affected
of the facility will be restored to a satisfactory condition
by performing or pay the reparation measures that
necessary and paying particular attention to the protection of land and
water quality, wild life, natural habitats,
the landscape, future land use and other health-
and environmental aspects.
72 § extractive waste facility may be considered to be closed first
When the reparation measures and other measures necessary for
to close the facility has been inspected and approved by
73 section Before an extractive waste facility is closed,
operator to determine whether the facility is a
risk facility. The operator shall inform
the supervisory authority if the conditions on which it is based
for the assessment. The system may be considered closed only when
the regulator has approved the assessment.
§ 74 after an extractive waste facility has been closed
the operator shall, to the extent necessary with
account of the danger of accidents and the protection of human
health and the environment during the time the supervisory authority
Decides to ensure that
1. utskov, overflow and utskovskanaler are kept clean and
2. measuring and control equipment works,
3. the facility in General maintained, monitored and
4. shortcomings are remedied, and
5. follow 70 § if the closed plant still
would be in operation.
75 section Supervisor may take over the responsibilities of
the operator has under section 74.
Back filling of cavities
76 § whoever lays back extractive waste in a cavity
incurred during the extraction shall, whether the cavity
have arisen through extraction above or below ground, perform
controls and have a responsibility that corresponds to the responsibilities of a
operators are under 22, 56, 70, 71 and 74 sections.
77 § if in a municipality there are people who may be affected by a
serious accident at a risk facility, should the municipality ensure
to the people on a website or other appropriate
get information about the danger of serious accidents and
actions taken at the facility. The information shall
1. name of operator and indication of where the plant
2. an indication of the municipality that is responsible for the content of
3. a statement that the plant is covered by
the provisions of §§ 57 to 63,
4. a statement that the municipality has received all relevant
information about the dangers of serious accidents
the plant is associated with, and of the measures
taken or to be taken to prevent, Suppress and
reduce damage to human health and the environment,
5. a clear and simple statement of
a) activities at the facility,
b) product description, alternative chemical name or General
risk classification for each chemical product which occurs in
the facility, and
(c)) the waste at the plant that can cause serious
accidents with information on its most important dangerous
6. a general description of the serious accidents
that could occur and their radiological effects on
human health and the environment,
7. an indication of how the public will be warned and
be informed if this happens a serious accident,
8. a report on the measures which the public should take about
It happens to a serious accident,
9. a statement that the operator is
required to take the necessary measures within the plant site
and interact with the municipal emergency services to
manage and limit the consequences of a serious accident,
10. an indication of the emergency plan that is
According to Chapter 3. section 6 of the Regulation (2003:789) on protection against
11. a statement as to where more information may be obtained.
section 78 the municipality shall, every three years, review the
the content of the communication referred to in section 77, and, if necessary,
79 section if there is a risk in a business establishment, the
the operator giving the municipality the information needed
to the municipality to meet their
List of closed extractive waste facilities
80 section environmental protection agency should maintain a list of closed
or abandoned extractive waste facilities carrying
or can pose serious hazards to human health or the
environment. The list shall be made available in an appropriate manner
to the public and regularly updated.
81 section supervisor shall identify such
extractive waste facilities as defined in section 80 and falling
under the regulator's remit and submit information
If the plants to the environmental protection agency.
82 section environmental protection agency may provide
1. regulations on what is an extractive waste
fine fraction, concentrations of pollutants and natural
background levels for determining whether the waste is inert
extractive waste, and
2. the provisions necessary for the implementation of section 81.
Before the environmental protection agency Announces rules referred to in the first
paragraph 1, the authority shall hear the geological
83 § provisions on supervision and control are found in chapter 26.
the environmental code, the environmental protection Decree (2011:13) and in
Ordinance (1998:901) if the operator's own control.
Provisions on the operational supervisory responsibilities associated
with this regulation can be found in chapter 26. section 3, third subparagraph
the environmental code and Chapter 2. 4, 29 and 30 § §
environmental protection regulation.
84 § for each extractive waste facility,
supervisor do regular on-site inspections.
85 § the operator shall ensure that the documentation
referred to in section 6 of the Ordinance (1998:901) if
operators ' self-checking is preserved along with the
regarding the authorisation documents.
86 § where for an extractive waste facility
occurs which may affect the stability of the plant
or that may involve a considerable inconvenience to people's
health or the environment, the operator shall
1. as soon as possible, and not later than 48 hours after
the event, inform the supervisory authority of the event,
2. If necessary, take action under the internal
the contingency plan, and
3. follow the instructions of the supervisory authority
87 § provisions on fees can be found in Chapter 27. the environmental code and
in the Ordinance (1998:940) if the fees for the examination and
supervision under the Environment Act.
88 § if there is a risk in a business establishment, the
the responsible party shall reimburse the costs been reasonable
of the municipality's public information according to § 77,
including keep the information up to date in accordance with section 78.
section 89 rules on penalties are provided in chapter 29. the environmental code.
90 § environmental protection agency shall carry out the
reporting obligations imposed by article 18(1) of
European Parliament and Council Directive 2006/21/EC of 15
March 2006 on the management of waste from extractive industries and
amending Directive 2004/35/EC, as amended by:
91 § the Swedish civil contingencies Agency shall carry out
the reporting obligations arising from article 18(2) of
Directive 2006/21/EC.
92 section in carrying out the obligations laid down in paragraphs 90 and 91
to the environmental protection agency and the Swedish civil
preparedness following the Commission decision 2009/358/EC of 29
April 2009 on the harmonisation and regular transmission of
information and the questionnaire referred to in articles 22 (1) (a)
and 18 of European Parliament and Council Directive 2006/21/EC
on the management of waste from the extractive industries.
2013:319
1. This Regulation shall enter into force on 1 July 2013, when
Regulation (2008:722) of extractive waste shall cease to
2. This Regulation shall not apply to
extractive waste facilities closed by 31
3. Despite paragraph 69 shall, for the period prior to 1 may
by 2018, the concentration of cyanide or cyanide compounds as
are dissociated with a weak acid amount to 0.0025% w/w (25
weight-ppm), if the waste tray on 1 september 2008, in
operation or were subject to a condition referred to in 9 or
11 kap. the environmental code.
2013 The State Council Regulation On The Management Of Waste From Extractive Waste
2010 The Planning (Management of Waste from Extractive Industries) Regulations (Northern Ireland) 2010
2010 The Management of Extractive Waste (Scotland) Regulations 2010
2006 Directive 2006/21/EC of the European Parliament and of the Council of 15 March 2006 on the management of waste from extractive industries and amending Directive 2004/35/EC - Statement by the European Parliament, the Council and the Commission
2009 S.I. No. 566/2009 - Waste Management (Management of Waste From the Extractive Industries) Regulations 2009
2015 The Planning (Management of Waste from Extractive Industries) Regulations (Northern Ireland) 2015
2009 Regulation On The Implementation Of Directive 2006/21/ec Of The European Parliament And Of The Council Of 15 March 2006 On The Management Of Waste From Extractive Industries And Amending Directive 2004/35/ec
Decree Of 19 April 2010 On The Management Of Waste From Extractive Industries