Industries and Backfilling) Regulations, 2009
Table of Provisions (36)
Statutory Text (36 Articles)
L.N. 22 of 2009
ENVIRONMENT PROTECTION ACT
(CAP. 435)
OCCUPATIONAL HEALTH AND SAFETY AUTHORITY
ACT
(CAP. 424)
Waste Management (Management of Waste from Extractive
Industries and Backfilling) Regulations, 2009
IN exercise of the powers conferred by articles 9, 11(1)(b)
and 28 of the Environment Protection Act, and by article 12 of the
Occupational Health and Safety Authority Act, the Prime Minister
and the Minister for Social Policy, after consultation with the Malta
Environment and Planning Authority and the Occupational Health
and Safety Authority, have made the following regulations:-
(1) These regulations may be cited as the Waste
Management (Management of Waste from Extractive Industries and
Backfilling) Regulations, 2009.
(2) These regulations shall come into force on such date
as the Minister responsible for the environment may by notice in the
Gazette appoint and different dates may be so appointed for different
provisions and different purposes of these regulations.
(Paragraph b of sub-regulation (3) of regulations 7 and 18)
Waste characterisation
The waste to be deposited in a facility shall be characterised in such a way as to
guarantee the long-term physical and chemical stability of the structure of the facility
and to prevent major accidents. The waste characterisation shall include, where
appropriate and in accordance with the category of the waste facility, the following
aspects
1. description of expected physical and chemical characteristics of the waste
to be deposited in the short and the long term, with particular reference to its stability
under surface atmospheric/meteorological conditions, taking account of the type of
mineral or minerals to be extracted and the nature of any overburden and, or gangue
minerals that will be displaced in the course of the extractive operations;
2. classification of the waste according to the relevant entry in the Waste
Management (Permit and Control) Regulations, 2001, with particular regard to its
hazardous characteristics;
3. description of the chemical substances to be used during treatment of the
mineral resource and their stability;
4. description of the method of deposition;
5. waste transport system to be employed.
(1) These regulations bring into effect the provisions
of Directive 2006/21/EC 1 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 2 .
(2) These regulations provide for measures, procedures
and guidance to prevent or reduce as far as possible any adverse
effects on the environment, in particular water, air, soil, fauna and
flora and landscape, and any resultant risks to human health, brought
about as a result of the management of waste from the extractive
industries or of the backfilling into excavation voids.
(3) These regulations provide additional measures,
procedures and guidance to those in the Waste Management (Permit
and Control) Regulations, 2001.
(Sub-regulation (1) of regulation 6)
Criteria for determining the classification of waste facilities
A waste facility shall be classified under category A if
1. a failure or incorrect operation, such as the collapse of a heap or the bursting
of a dam, could give rise to a major accident, on the basis of a risk assessment
taking into account factors such as the present or future size, the location and the
environmental impact of the waste facility; or
2. it contains waste classified as hazardous under the Waste Management
(Permit and Control) Regulations, 2001, above a certain threshold; or
3. it contains substances or preparations classified as dangerous under the
Dangerous Substances (Notification) Regulations, 2001, or the Dangerous Substances
and Preparations Regulations, 2007 above a certain threshold.
(1) In these regulations, unless the context otherwise
requires
“the Act” means the Environment Protection Act;
“backfill” means any material, excluding waste other than
extractive waste, used for backfilling;
“backfilling” means refilling an excavation void, after
extraction of the mineral, for rehabilitation or construction
purposes related to the mineral extraction process, such as the
building or maintenance within such a void of means of access
for machinery, haulage ramps, bulkheads, safety barricades or
berms; and “backfilled” shall be construed accordingly;
OJ L 102,11.4.2006, p. 15.
OJ L 143, 30.4.2004, p. 56.
“best available techniques” is as defined in regulation 2 of
the Integrated Pollution Prevention and Control Regulations,
2002;
“the Competent Authority” means the Malta Environment
and Planning Authority and such other body or person as the
Minister may by order in the Gazette, prescribe and different
bodies or persons may be designated as the competent
authority for different provisions and different purposes of
these regulations;
“the Community” means the European Community;
“competent person” means a natural person who has
the technical knowledge and experience, as defined by
Maltese legislation, to perform the duties arising from these
regulations;
“dam” means an engineered structure designed to retain
or confine water and,or waste within a pond;
“dangerous substance” means a substance, mixture or
preparation which is dangerous within the meaning of the
Dangerous Substances (Notification) Regulations, 2001, or the
Dangerous Substances and Preparations Regulations, 2007;
“extractive industries” means all establishments and
undertakings engaged in surface or underground extraction
of mineral resources for commercial purposes, including
extraction by drilling boreholes, or treatment of the extracted
material;
“extractive waste” means waste resulting from the
prospecting, extraction, treatment and storage of mineral
resources and the working of quarries, such as tailings (i.e. the
waste solids or slurries that remain after the treatment of minerals
by a number of techniques), waste rock and overburden (i.e.
the material that extractive operations move during the process
of accessing an ore or mineral body, including during the pre-
production development stage), and topsoil (i.e. the upper layer
of the ground) provided that they constitute waste;
“hazardous waste” means any type of waste which is
marked with an asterisk in Schedule 1 to the Waste Management
(Permit and Control) Regulations, 2001, or which has any of
the properties which render a waste hazardous as specified in
Schedules 2 and 3 to those regulations, or which is deemed to
be hazardous by the competent authority;
“heap” means an engineered facility for the deposit of
solid waste on the surface;
“inert waste” means waste that does not undergo any
significant physical, chemical or biological transformations.
Inert waste will not dissolve, burn or otherwise physically
or chemically react, biodegrade or adversely affect other
matter with which it comes into contact in a way likely to
give rise to environmental pollution or harm human health.
The total leachability and pollutant content of the waste and
the ecotoxicity of the leachate must be insignificant, and in
particular not endanger the quality of surface water and, or
groundwater;
“leachate” means any liquid percolating through the
deposited waste and emitted from or contained within a waste
facility, including polluted drainage, which may adversely
affect the environment if not appropriately treated;
“major accident” means an occurrence on site in the course
of an operation involving the management of extractive waste
in any establishment covered by these regulations, leading
to a serious danger to human health and, or the environment,
whether immediately or over time, on-site or off-site;
“mineral resource” or “mineral” means a naturally
occurring deposit in the earth’s crust of an organic or inorganic
substance, such as energy fuels, metal ores, industrial minerals
and construction minerals, but excluding water;
“the Minister” means the Minister responsible for the
environment;
“off-shore” means that area of the sea and seabed
extending from the low water mark of ordinary or medium
tides outwards;
“operator” means the natural or legal person responsible
for the management of extractive waste, in accordance with
Maltese legislation, including in respect of temporary storage
of extractive waste as well as the operational and the after-
closure phases;
“pond” means a natural or engineered facility for
disposing of fine-grained waste, normally tailings, along with
varying amounts of free water, resulting from the treatment
of mineral resources and from the clearing and recycling of
process water;
“prospecting” means the search for mineral deposits of
economic value, including sampling, bulk sampling, drilling
and trenching, but excluding any works required for the
development of such deposits, and any activities directly
associated with an existing extractive operation;
“the public” means one or more natural or legal persons
and, in accordance with Maltese legislation or practice, their
associations, organisations or groups;
“the public concerned” means the public affected or likely
to be affected by, or having an interest in, the environmental
decision-making under regulations 8 and 9 of these regulations;
for the purposes of this definition, non-governmental
organisations promoting environmental protection and meeting
any requirement under Maltese legislation shall be deemed to
have such an interest;
“receiving body of water” means surface waters,
groundwater, transitional waters and coastal water as defined
in sub-regulation (1) of regulation 2 of the Water Policy
Framework Regulations, 2004;
“rehabilitation” means the treatment of the land affected
by a waste facility in such a way as to restore the land to a
satisfactory state, with particular regard to soil quality, wild
life, natural habitats, freshwater systems, landscape and
appropriate beneficial uses;
“site” means all land at a distinct geographic location
under the management control of an operator;
“substantial change” means a change in the structure
or operation of a waste facility that, in the opinion of the
competent authority, may have significant negative effects on
human health or the environment;
“tailings” means the waste solids or slurries that remain
after the treatment of minerals by separation processes (e.g.
crushing, grinding, size-sorting, flotation and other physico-
chemical techniques) to remove the valuable minerals from the
less valuable rock;
“treatment” means the mechanical, physical, biological,
thermal or chemical process or combination of processes
carried out on mineral resources, including from the working
of quarries, with a view to extracting the mineral, including
size change, classification, separation and leaching, and the
re-processing of previously discarded waste, but excluding
smelting, thermal manufacturing processes (other than the
burning of limestone) and metallurgical processes;
“unpolluted soil” means soil that is removed from the
upper layer of the ground during extractive activities and that
is not deemed to be polluted under Community or Maltese
legislation;
“waste” in addition to what is said in the Act, means
any thing, substance, product or object, whether in solid or
liquid form, whether hazardous or otherwise, which the holder
discards, or intends, or is required to discard, or any other which
is deemed to be waste by the competent authority nominated
by the Minister responsible for the environment under article
6 of the Act.
“waste facility” means any area designated for the
accumulation or deposit of extractive waste, whether in a solid
or liquid state or in solution or suspension, for the following
time-periods
(i) no time-period for Category A waste facilities
and facilities for waste characterised as hazardous in the
waste management plan;
(ii) a period of more than six months for facilities
for hazardous waste generated unexpectedly;
(iii) a period of more than one year for facilities
for non-hazardous non-inert waste;
(iv) a period of more than three years for facilities
for unpolluted soil, non-hazardous prospecting waste,
waste resulting from the extraction, treatment and storage
of peat and inert waste
Provided that such facilities are deemed to include
any dam or other structure serving to contain, retain,
confine or otherwise support such a facility, and also
to include, but not be limited to, heaps and ponds, but
excluding excavation voids;
“waste holder” means the producer of the extractive waste
or the natural or legal person who is in possession of it;
“weak acid dissociable cyanide” means cyanide and
cyanide compounds that are dissociated with a weak acid at a
defined pH.
(2) All other terms shall have the same meaning as that
assigned to them in regulation 2 of the Waste Management (Permit
and Control) Regulations, 2001.
(Subregolament (1) tar-regolament 6)
Kriterji sabiex tiġi determinata l-klassifikazzjoni tal-faċilitajiet ta’ l-iskart
Faċilità ta’ l-iskart għandha tiġi klassifikata fil-kategorija A jekk
1. ħsara jew operazzjoni ħażina, per eżempju l-kollass ta’ borġ jew iċ-ċediment
ta’ diga, tista’ tikkaġuna inċident maġġuri, abbażi ta’ valutazzjoni tar-riskju filwaqt
li jittieħed kont tal-fatturi bħad-daqs preżenti jew futur, il-lok u l-impatt ambjentali
tal-faċilità ta’ l-iskart; jew
2. ikollha skart li jkun klassifikat bħala perikoluż taħt ir-Regolamenti ta’ l-2002
għall-Prevenzjoni u l-Kontroll Integrati tat-Tniġġis ‘l fuq minn ċertu limitu; jew
3. ikollha sustanzi jew preparati li jkunu klassifikati bħala perikolużi taħt ir-
Regolamenti ta’ 1-2001 dwar Sustanzi Perikolużi (Notifikazzjoni), jew ir-Regolamenti
ta’ l-2007 dwar Sustanzi u Preparamenti Perikolużi ‘l fuq minn ċertu limitu.
(1) Subject to sub-regulation (2) of this regulation, these
regulations shall cover extractive waste and backfill.
(2) The following shall be excluded from the scope of
these regulations
(a) waste which is generated by the prospecting,
extraction and treatment of mineral resources and the working
of quarries, but which does not directly result from those
operations, e.g. food waste, waste oil, end-of-life vehicles,
spent batteries and accumulators. The management of
such waste should be subject to the provisions of the Waste
Management (Permit and Control) Regulations, 2001, or the
Waste Management (Landfill) Regulations, 2002, or any other
relevant Community or Maltese legislation;
(b) waste resulting from the offshore prospecting,
extraction and treatment of mineral resources;
(c) injection of water and re-injection of pumped
groundwater as defined in the first and second indents of
paragraph (j) of sub-regulation (3) of regulation 11 of the Water
Policy Framework Regulations, 2004, to the extent authorised
by that regulation.
(3) Any waste facility which has been granted a permit
or which is already in operation on 1 May 2008 shall comply with
these regulations by 1 May 2012.
(4) Any excavation void which has been granted a
permit or which is already in operation on 1 May 2008 may continue
operating in accordance with the Waste Management (Permit and
Control) Regulations, 2001, or the Waste Management (Landfill)
Regulations, 2002, unless the Competent Authority decides
otherwise.
(5) Regulation 7, sub-regulations (3) to (8) of regulation
8, regulations 9 and 10, sub-regulation (1) of regulation 12, sub-
regulations (1), (2) and (3) of regulation 14, regulation 17 and 18
of these regulations shall not apply to those waste facilities that are
completing the closure procedures in accordance with the applicable
Community or Maltese legislation or programmes approved by the
Competent Authority, and will be effectively closed by 31 December
2010
Provided that these facilities shall be managed in a
way that does not prejudice the achievement of the objectives of
these regulations, in particular the objectives of sub-regulation (1)
of regulation 5 of these regulations, including the Water Policy
Framework Regulations, 2004.
(6) Without prejudice to other Maltese legislation,
waste which falls within the scope of these regulations shall not be
subject to the Waste Management (Landfill) Regulations, 2002
Provided that the Waste Management (Landfill)
Regulations, 2002, shall continue to apply to waste other than
extractive waste used for backfilling into excavation voids, whether
created through surface or underground extraction, as appropriate.
(1) Extractive waste shall be managed and excavation
voids shall be backfilled without endangering human health
and without using processes or methods which could harm the
environment, and in particular without risk to water, air, soil and
fauna and flora, without causing a nuisance through noise or odours
and without adversely affecting the landscape or places of special
interest.
(2) The abandonment, dumping, uncontrolled depositing
of extractive waste or uncontrolled backfilling into excavation voids
shall be prohibited.
(3) The operator shall take all measures necessary
to prevent or reduce as far as possible any adverse effects on the
environment and human health brought about as a result of the
management of extractive waste or backfilling into excavation
voids. This includes the management of any waste facility, also
after its closure, and the prevention of major accidents involving that
facility and the limiting of their consequences for the environment
and human health.
(4) The measures referred to in sub-regulation (3)
of this regulation shall be based, inter alia, on the best available
techniques, without prescribing the use of any technique or specific
technology, but taking into account the technical characteristics of
the waste facility or excavation void, its geographical location and
the local environmental conditions.
PART II
TYPES OF WASTE FACILITIES
For the purposes of these regulations, waste facilities shall
be classified in one of the following categories
(1) Category A waste facility: any waste facility meeting
the criteria set out in Schedule 3 to these regulations or any waste
facility designated for the accumulation or deposit of hazardous
waste generated unexpectedly for a period of more than six months;
or
(2) Category B waste facility: any waste facility
designated for the accumulation or deposit of non-hazardous non-
inert waste for a period of more than one year; or
(3) Category C waste facility: any waste facility
designated for the accumulation or deposit of unpolluted soil, non-
hazardous prospecting waste, waste resulting from the extraction,
treatment and storage of peat and inert waste for a period of more
than three years
Provided that Category A, Category B and Category C
waste facilities are deemed to include any dam or other structure
serving to contain, retain, confine or otherwise support such a
facility, and also to include, but not be limited to, heaps and ponds,
but excluding excavation voids, whether created through surface or
underground extraction.
PART III
CATEGORY A WASTE FACILITY
(1) The operator shall draw up a waste management plan
for the minimisation, treatment, recovery and disposal of extractive
waste, taking account of the principle of sustainable development.
(2) The objectives of the waste management plan shall
(a) to prevent or reduce waste production and its
harmfulness, in particular by considering
(i) waste management in the design phase and in
the choice of the method used for mineral extraction and
treatment;
(ii) the changes that the extractive waste may
undergo in relation to an increase in surface area and
exposure to conditions above ground;
(iii) backfilling into the excavation void, whether
created through surface or underground extraction,
after extraction of the mineral, as far as is technically
and economically feasible and environmentally sound
in accordance with existing Community or Maltese
environmental standards and with the requirements of
these regulations where relevant;
(iv) putting topsoil back in place after the closure
of the waste facility or, if this is not practically feasible,
reusing topsoil elsewhere;
(v) using less dangerous substances for the
treatment of mineral resources;
(b) to encourage the recovery of extractive waste by
means of recycling, reusing or reclaiming such waste, where
this is environmentally sound in accordance with existing
Community or Maltese environmental standards and with the
requirements of these regulations where relevant;
(c) to ensure short and long-term safe disposal of the
extractive waste, in particular by considering, during the design
phase, management during the operation and after-closure of a
waste facility and by choosing a design which
(i) requires minimal and, if possible, ultimately no
monitoring, control and management of the closed waste
facility;
(ii) prevents or at least minimises any long-term
negative effects, for example attributable to migration
of airborne or aquatic pollutants from the waste facility;
and
(iii) ensures the long-term geotechnical stability
of any dams or heaps rising above the pre-existing ground
surface.
(3) The waste management plan shall contain at least
the following elements
(a) the proposed classification for the waste facility
in accordance with the criteria laid down in regulation 6 of
these regulations and a document demonstrating that a major-
accident prevention policy, a safety management system for
implementing it and an internal emergency plan will be put
into effect in accordance with sub-regulation (3) of regulation
8 of these regulations;
(b) waste characterisation in accordance with Schedule
2 to these regulations and a statement of the estimated total
quantities of extractive waste to be produced during the
operational phase;
(c) a description of the operation generating such waste
and of any subsequent treatment to which it is subject;
(d) a description of how the environment and human
health may be adversely affected by the deposit of such waste
and the preventive measures to be taken in order to minimise
environmental impact during operation and after closure,
including the aspects referred to in paragraphs (a), (b), (d) and
(e) of sub-regulation (2) of regulation 11 of these regulations;
(e) the proposed control and monitoring procedures
pursuant to paragraph (c) of sub-regulation (2) of regulation 11
of these regulations;
(f) the proposed plan for closure, including rehabilitation,
after-closure procedures and monitoring as provided for in
regulation 12 of these regulations;
(g) measures for the prevention of water status
deterioration in accordance with the Water Policy Framework
Regulations, 2004, and for the prevention or minimisation
of air and soil pollution pursuant to regulation 13 of these
regulations;
(h) a survey of the condition of the land to be affected
by the waste facility.
(i) any other relevant information requested by the
Competent Authority.
(4) The waste management plan shall provide sufficient
information to enable the Competent Authority to evaluate the
operator’s ability to meet the objectives of the waste management plan
as set out in sub-regulation (2) of this regulation and his obligations
under these regulations. The plan shall explain, in particular, how
the option and method chosen as mentioned in indent (i) of paragraph
(a) of sub-regulation (2) of this regulation will fulfil the objectives
of the waste management plan as laid down in paragraph (a) of sub-
regulation (2) of this regulation.
(5) The Competent Authority may specify the format in
which such information is to be made available.
(6) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001.
(7) The waste management plan shall be reviewed every
five years and or amended, as appropriate, in the event of substantial
changes to the operation of the waste facility or to the waste deposited.
Any amendments shall be notified to the Competent Authority.
(8) Plans produced pursuant to other Community or
Maltese legislation and containing the information specified in sub-
regulation (3) of this regulation may be used where this obviates
the unnecessary duplication of information and the repetition of
work by the operator, on condition that all requirements under sub-
regulations (1), (2), (3), (4) and (7) of this regulation are met.
(9) The Competent Authority shall approve the waste
management plan on the basis of procedures to be decided by the
Competent Authority and shall monitor its implementation.
(1) This regulation shall apply to Category A waste
facilities, save for those waste facilities falling within the scope of
the Control of Major Accident Hazard Regulations, 2003.
(2) Without prejudice to other Community or Maltese
legislation, and in particular the Protection of Workers in the Mineral
Extracting Industries through Drilling and Workers in Surface and
Underground Mineral Extracting Industries Regulations, 2003, the
Competent Authority established by virtue of sub-regulation (1) of
regulation 3 of the Control of Major Accident Hazard Regulations,
2003, shall ensure that major-accident hazards are identified and that
the necessary features are incorporated into the design, construction,
operation and maintenance, closure and after-closure of the waste
facility in order to prevent such accidents and to limit their adverse
consequences for human health and, or the environment, including
any transboundary impacts.
(3) For the purposes of the requirements under sub-
regulation (2) of this regulation, each operator shall, before the
start of operations, draw up a major-accident prevention policy for
the management of extractive waste and put into effect a safety
management system implementing it, in accordance with the
elements set out in Section 1 of Schedule 1 to these regulations, and
shall also put into effect an internal emergency plan specifying the
measures to be taken on site in the event of an accident
Provided that, as part of that policy, the operator shall
appoint a safety manager responsible for the implementation and
periodic supervision of the major-accident prevention policy.
(4) The Competent Authority established by virtue of
sub-regulation (1) of regulation 3 of the Control of Major Accident
Hazard Regulations, 2003, shall draw up an external emergency
plan specifying the measures to be taken off-site in the event of
an accident. As part of the application for a permit the operator
shall provide the Competent Authority established by virtue of
sub-regulation (1) of regulation 3 of the Control of Major Accident
Hazard Regulations, 2003, with the information necessary to enable
the latter to draw up that plan.
(5) The emergency plans referred to in sub-regulations
(3) and (4) of this regulation shall have the following objectives
(a) to contain and control major accidents and other
incidents so as to minimise their effects, and in particular to
limit damage to human health and the environment;
(b) to implement the measures necessary to protect
human health and the environment from the effects of major
accidents and other incidents;
(c) to communicate the necessary information to the
public and to the relevant services or authorities in the area;
(d) to provide for the rehabilitation, restoration and
clean-up of the environment following a major accident.
(6) In the event of a major accident, the operator shall
immediately provide the Competent Authority established by virtue
of sub-regulation (1) of regulation 3 of the Control of Major Accident
Hazard Regulations, 2003, with all the information required to
help minimise its consequences for human health and to assess
and minimise the extent, actual or potential, of the environmental
damage.
(7) The public concerned shall be given early and
effective opportunities to participate in the preparation or review of
the external emergency plan to be drawn up in accordance with sub-
regulation (4) of this regulation. To that end, the public concerned
shall be informed about any such proposal and relevant information
shall be made available, including, inter alia, information about the
right to participate in the decision-making process and about the
Competent Authority established by virtue of sub-regulation (1) of
regulation 3 of the Control of Major Accident Hazard Regulations,
2003, to which comments and questions may be submitted.
(8) The public concerned shall be entitled to express
comments within reasonable time frames and, in the decision on
the external emergency plan, due account shall be taken of these
comments.
(9) Information on safety measures and on the action
required in the event of an accident, containing at least the elements
listed in Section 2 of Schedule 1 to these regulations, shall be
provided, free of charge and as a matter of course, to the public
concerned
Provided that that information shall be reviewed every
three years and, where necessary, updated.
(1) No waste facility shall be allowed to operate without
a permit granted by the Competent Authority.
(2) The permit shall contain the elements specified in
sub-regulation (3) of this regulation and shall clearly indicate the
category of the waste facility in accordance with the criteria referred
to in regulation 6 of these regulations
Provided that, subject to compliance with all requirements
under this regulation, any permit produced pursuant to other
Community or Maltese legislation may be combined to form a single
permit, where such a format obviates the unnecessary duplication of
information and the repetition of work by the operator or Competent
Authority.
Provided further that, the details specified in sub-
regulation (3) of this regulation can be covered by one single
permit or several permits, provided that all requirements under this
regulation are complied with.
(3) The application for a permit shall contain at least
the following details
(a) the identity of the operator;
(b) the proposed location of the waste facility, including
any possible alternative locations;
(c) the waste management plan pursuant to regulation 7
of these regulations;
(d) adequate arrangements by way of a financial
guarantee or equivalent, as required under regulation 14 of
these regulations;
(e) the information provided by the operator in
accordance with the Environmental Impact Assessment
Regulations, 2007, if an environmental impact assessment is
required under those regulations; and
(f) any other relevant information requested by the
Competent Authority.
(4) The Competent Authority may specify the format in
which such information is to be made available.
(5) The Competent Authority shall only grant a permit
if it is satisfied that
(a) the operator complies with the relevant requirements
under these regulations;
(b) the management of waste does not conflict directly
or otherwise interfere with the implementation of the relevant
waste management plan or plans referred to in sub-regulation
(3) of regulation 4 of the Waste Management (Permit and
Control) Regulations, 2001.
(6) The Competent Authority shall reconsider and,
where necessary, update permit conditions periodically
(a) where there are substantial changes in the operation
of the waste facility or the waste deposited;
(b) on the basis of monitoring results reported by the
operator pursuant to sub-regulations (3) and (4) of regulation
11 of these regulations or inspections carried out pursuant to
regulation 29 of these regulations;
(c) in the light of information exchange on substantial
changes in best available techniques.
(7) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001
Provided that the information contained in a permit granted
under these regulations shall be made available to the competent
national and Community statistical authorities where requested for
statistical purposes.
Provided further that sensitive information of a purely
commercial nature, such as information concerning business
relations and cost components and the volume of economic mineral
reserves, shall not be made public.
(1) The public shall be informed, by public notices or
other appropriate means, such as electronic media where available,
of the following matters early in the procedure for granting a
permit or, at the latest, as soon as the information can reasonably be
provided on
(a) the application for a permit;
(b) where applicable, the fact that a decision concerning
an application for a permit is subject to consultation with
an other State in accordance with regulation 15 of these
regulations;
(c) details of the relevant competent authorities
responsible for taking the decision, those from which relevant
information can be obtained, those to which comments or
questions can be submitted, and details of the time schedule
for transmitting comments or questions;
(d) the nature of possible decisions;
(e) where applicable, the details relating to a proposal
for the updating of a permit or of permit conditions;
(f) an indication of the times and places where, or
the means by which, the relevant information will be made
available;
(g) details of the arrangements for public participation
made pursuant to sub-regulation (7) of this regulation.
(2) Within appropriate time frames, the following shall
be made available to the public concerned
(a) in accordance with Maltese legislation, the main
reports and advice transmitted to the Competent Authority at
the time when the public was informed in accordance with
sub-regulation (1) of this regulation;
(b) in accordance with the provisions of the Freedom
of Access to Information on the Environment Regulations,
2001, any information in addition to that referred to in sub-
regulation (1) of this regulation which is relevant for the
decision in accordance with regulation 9 of these regulations
and which only becomes available after the time the public
have been informed in accordance with sub-regulation (1) of
this regulation.
(3) The public shall be informed, in accordance
with sub-regulation (1) of this regulation of an update of permit
conditions in accordance with sub-regulation (6) of regulation 9 of
these regulations.
(4) The public concerned shall be entitled to express
comments and opinions to the Competent Authority before a decision
is taken.
(5) The results of the consultations held pursuant to
this regulation shall be duly taken into account in the taking of a
decision.
(6) When a decision has been taken the Competent
Authority shall, in accordance with the appropriate procedures,
inform the public concerned and shall make the following information
available to the public concerned
(a) the content of the decision, including a copy of the
permit;
(b) the reasons and considerations on which the decision
is based.
(7) The detailed arrangements for public participation
under this regulation shall be determined by the Competent Authority
so as to enable the public concerned to prepare and participate
effectively.
(1) The management of a waste facility shall be in the
hands of a competent person and technical development and training
of staff shall be provided.
(2) In constructing a new waste facility or modifying an
existing waste facility, the operator shall ensure that
(a) the waste facility is suitably located, taking into
account in particular Community or Maltese obligations
relating to protected areas, and geological, hydrological,
hydrogeological, seismic and geotechnical factors, and is
designed so as to meet the necessary conditions for, in the short
and long-term perspectives, preventing pollution of the soil, air,
groundwater or surface water, taking into account especially the
Pollution Caused by Certain Dangerous Substances Discharged
Into the Aquatic Environment Regulations, 2001, Regulations
for the Protection of Groundwater against Pollution caused by
Certain Dangerous Substances, 2002, and the Water Policy
Framework Regulations, 2004, and ensuring efficient collection
of contaminated water and leachate as and when required under
the permit, and reducing erosion caused by water or wind as
far as it is technically possible and economically viable;
(b) the waste facility is suitably constructed, managed
and maintained to ensure its physical stability and to prevent
pollution or contamination of soil, air, surface water or
groundwater in the short and long-term perspectives as well as
to minimise as far as possible damage to landscape;
(c) there are suitable plans and arrangements for regular
monitoring and inspection of the waste facility by competent
persons and for taking action in the event of results indicating
instability or water or soil contamination
Provided that records of monitoring and inspections shall
be kept, together with permit documentation, in order to ensure
the appropriate hand-over of information, particularly in the
event of a change of operator.
(d) suitable arrangements are made for the rehabilitation
of the land and the closure of the waste facility; and
(e) suitable arrangements are made for the after-closure
phase of the waste facility.
(3) The operator shall, without undue delay and in
any event not later than 48 hours thereafter, notify the Competent
Authority of any events likely to affect the stability of the waste
facility and any significant adverse environmental effects revealed
by the control and monitoring procedures of the waste facility.
(4) The operator shall implement the internal emergency
plan, where applicable, and follow any other instruction from the
Competent Authority as to the corrective measures to be taken.
(5) The operator shall bear the costs of the measures to
be undertaken.
(6) At least once a year, the operator shall report, on the
basis of aggregated data, all monitoring results to the Competent
Authority for the purposes of demonstrating compliance with permit
conditions and increasing knowledge of waste and waste facility
behaviour. On the basis of this report the Competent Authority may
decide that validation by an independent expert is necessary.
(1) A waste facility shall only start the closure procedure
if one of the following conditions is satisfied
(a) the relevant conditions stated in the permit are met;
(b) authorisation is granted by the Competent Authority,
at the request of the operator;
(c) the Competent Authority issues a reasoned decision
to that effect.
(2) A waste facility may be considered as finally closed
only after the Competent Authority has, without undue delay, carried
out a final on-site inspection, assessed all the reports submitted by
the operator, certified that the land affected by a waste facility has
been rehabilitated and communicated to the operator its approval of
the closure.
Provided that this approval shall not in any way reduce
the operator’s obligations under the conditions of the permit or
otherwise in law.
(3) The operator shall be responsible for the maintenance,
monitoring, control and corrective measures in the after-closure
phase for as long as may be required by the Competent Authority,
taking into account the nature and duration of the hazard, save where
the Competent Authority decides to take over such tasks from the
operator, after a waste facility has been finally closed and without
prejudice to any Community or Maltese legislation governing the
liability of the waste holder.
(4) When considered necessary by the Competent
Authority, in order to fulfil relevant environmental requirements
set out in Community or Maltese legislation, in particular those in
the Pollution Caused by Certain Dangerous Substances Discharged
Into the Aquatic Environment Regulations, 2001, the Protection
of Groundwater against Pollution caused by Certain Dangerous
Substances Regulations, 2002, and the Water Policy Framework
Regulations, 2004, following closure of a waste facility, the operator
shall, inter alia, control the physical and chemical stability of the
facility and minimise any negative environmental effect, in particular
with respect to surface and groundwater, by ensuring that
(a) all the structures pertaining to the facility are
monitored and conserved, with control and measuring apparatus
always ready for use;
(b) where applicable, overflow channels and spillways
are kept clean and free.
(5) Following closure of a waste facility, the operator
shall, without delay, notify the Competent Authority of any events
or developments likely to affect the stability of the waste facility,
and any significant adverse environmental effects revealed by the
relevant control and monitoring procedures.
(6) The operator shall implement the internal emergency
plan, where applicable, and follow any other instruction from the
Competent Authority as to the corrective measures to be taken
Provided that the operator shall bear the costs of the
measures to be undertaken.
(7) In cases and at a frequency to be determined by
the Competent Authority, the operator shall report, on the basis of
aggregated data, all monitoring results to the relevant competent
authorities for the purposes of demonstrating compliance with
permit conditions and increasing knowledge of waste and waste
facility behaviour.
(1) The operator shall take the necessary measures in
order to meet Community or Maltese environmental standards, in
particular to prevent, in accordance with the Water Policy Framework
Regulations, 2004, the deterioration of current water status, inter
alia, by
(a) evaluating the leachate generation potential,
including contaminant content of the leachate, of the deposited
waste during both the operational and after-closure phase of
the waste facility, and determining the water balance of the
waste facility;
(b) preventing or minimising leachate generation and
surface water or groundwater and soil from being contaminated
by the waste; and
(c) collecting and treating contaminated water and
leachate from the waste facility to the appropriate standard
required for their discharge.
(2) The operator shall take adequate measures to prevent
or reduce dust and gas emissions.
(3) On the basis of an assessment of environmental
risks, when taking into account, in particular, the Pollution Caused
by Certain Dangerous Substances Discharged Into the Aquatic
Environment Regulations, 2001, the Protection of Groundwater
against Pollution caused by Certain Dangerous Substances
Regulations, 2002, or the Water Policy Framework Regulations,
2004, as applicable, the Competent Authority has decided that
collection and treatment of leachate is not necessary or it has been
established that the waste facility poses no potential hazard to soil,
groundwater or surface water, the requirements set out in paragraphs
(b) and (c) of sub-regulation (1) of this regulation may be reduced or
waived accordingly.
(4) In the case of a pond involving the presence of
cyanide, the operator shall ensure that the concentration of weak acid
dissociable cyanide in the pond is reduced to the lowest possible level
using best available techniques and, in any case, at waste facilities
which have previously been granted a permit or have already been
in operation on 1 May 2008 that the concentration of weak acid
dissociable cyanide at the point of discharge of the tailings from
the processing plant into the pond does not exceed 50 ppm as from
1 May 2008, 25 ppm as from 1 May 2013, 10 ppm as from 1 May
2018 and 10 ppm at waste facilities which are granted a permit after
1 May 2008
Provided that, if the Competent Authority so requests, the
operator shall demonstrate, through a risk assessment that takes site-
specific conditions into account, that those concentration limits need
not be further lowered.
(1) The Competent Authority shall, prior to the
commencement of any operations involving the accumulation or
deposit of extractive waste in a waste facility, require a financial
guarantee (such as in the form of a financial deposit, including
industry-sponsored mutual guarantee funds) or the equivalent,
in accordance with procedures to be decided by the Competent
Authority, so that
(a) all obligations under the permit issued pursuant
to these regulations, including after-closure provisions, are
discharged; and
(b) there are funds readily available at any given time
for the rehabilitation of the land affected by the waste facility, as
described in the waste management plan prepared pursuant to
regulation 7 of these regulations and required by the regulation
9 permit.
(2) The calculation of the guarantee referred to in sub-
regulation (1) of this regulation shall be made on the basis of
(a) the likely environmental impact of the waste facility,
taking into account in particular the category of the waste
facility, the characteristics of the waste and the future use of
the rehabilitated land; and
(b) the assumption that independent and suitably
qualified third parties will assess and perform any rehabilitation
work needed.
(3) The size of the guarantee shall be periodically
adjusted in accordance with any rehabilitation work needed to be
carried out on the land affected by the waste facility, as described
in the waste management plan prepared pursuant to regulation 7 of
these regulations and required by the regulation 9 permit.
(4) Where the Competent Authority approves closure
in accordance with sub-regulation (2) of regulation 12 of these
regulations, it shall provide the operator with a written statement
releasing him from the guarantee obligation referred to in sub-
regulation (1) of this regulation with the exception of after-closure
obligations as referred to in sub-regulation (3) of regulation 12 of
these regulations.
(1) Where the Minister is aware that the operation of
a Category A waste facility in Malta is likely to have significant
adverse effects on the environment of, and any resultant risks to
human health in, another State, or where a State likely to be thus
affected so requests, the Minister shall forward the information
provided pursuant to regulation 9 of these regulations to the other
State at the same time as when the public is informed in terms of
sub-regulation (1) of regulation 10 of these regulations
Provided that such information shall serve as a basis for
any consultation necessary within the context of bilateral relations
between Malta and the other State on a reciprocal and equivalent
basis.
(2) Within the framework of their bilateral relations, the
Minister shall ensure that in the cases referred to in sub-regulation
(1) of this regulation the applications are also made available for an
appropriate period of time to the public concerned of the State likely
to be affected so that they will have the right to comment on them
before the Competent Authority reaches its decision.
(3) The Minister shall ensure that, in the event of an
accident involving a waste facility as referred to in sub-regulation
(1) of this regulation, information provided by the operator to the
Competent Authority pursuant to sub-regulations (5) and (6) of
regulation 8 of these regulations shall be immediately forwarded
to the other State in order to help minimise the consequences of the
accident for human health and to assess and minimise the extent of
the actual or potential environmental damage.
PART IV
CATEGORY B WASTE FACILITY
Category B waste facility shall be subject to all regulations
under Part III of these regulations, except sub-regulations (3) and (4)
of regulation 11, sub-regulations (4), (5), (6) and (7) of regulation
12, sub-regulation (4) of regulation 13, regulations 14 and 15 of
these regulations.
PART V
CATEGORY C WASTE FACILITY
(1) No waste facility shall be allowed to operate without
a permit granted by the Competent Authority.
(2) The permit shall contain the elements specified in
sub-regulation (3) of this regulation and shall clearly indicate the
category of the waste facility in accordance with the criteria referred
to in regulation 6 of these regulations
Provided that, subject to compliance with all requirements
under this regulation, any permit produced pursuant to other
Community or Maltese legislation may be combined to form a single
permit, where such a format obviates the unnecessary duplication of
information and the repetition of work by the operator or Competent
Authority
Provided further that, the details specified in sub-
regulation (3) of this regulation can be covered by one single
permit or several permits, provided that all requirements under this
regulation are complied with.
(3) The application for a permit shall contain at least
the following details
(a) the identity of the operator;
(b) the proposed location of the waste facility, including
any possible alternative locations;
(c) the waste management plan pursuant to regulation
18 of these regulations; and
(d) any other relevant information requested by the
Competent Authority.
(4) The Competent Authority may specify the format in
which such information is to be made available.
(5) The Competent Authority shall only grant a permit
if it is satisfied that
(a) the operator complies with the relevant requirements
under these regulations;
(b) the management of waste does not conflict directly
or otherwise interfere with the implementation of the relevant
waste management plan or plans referred to in sub-regulation
(3) of regulation 4 of the Waste Management (Permit and
Control) Regulations, 2001.
(6) The Competent Authority shall reconsider and,
where necessary, update permit conditions periodically
(a) where there are substantial changes in the operation
of the waste facility or the waste deposited;
(b) on the basis of inspections carried out pursuant to
regulation 29 of these regulations;
(c) in the light of information exchange on substantial
changes in best available techniques.
(7) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001
Provided that the information contained in a permit granted
under these regulations shall be made available to the competent
national and Community statistical authorities where requested for
statistical purposes.
Provided further that sensitive information of a purely
commercial nature, such as information concerning business
relations and cost components and the volume of economic mineral
reserves, shall not be made public.
(1) The operator shall draw up a waste management plan
for the minimisation, treatment, recovery and disposal of extractive
waste, taking account of the principle of sustainable development.
(2) The objectives of the waste management plan shall
(a) to prevent or reduce waste production and its
harmfulness, in particular by considering
(i) waste management in the design phase and in
the choice of the method used for mineral extraction and
treatment;
(ii) the changes that the extractive waste may
undergo in relation to an increase in surface area and
exposure to conditions above ground;
(iii)
backfilling into the excavation void, whether
created through surface or underground extraction,
after extraction of the mineral, as far as is technically
and economically feasible and environmentally sound
in accordance with existing Community or Maltese
environmental standards and with the requirements of
these regulations where relevant;
(iv) putting topsoil back in place after the closure
of the waste facility or, if this is not practically feasible,
reusing topsoil elsewhere;
(v) using less dangerous substances for the
treatment of mineral resources;
(b) to encourage the recovery of extractive waste by
means of recycling, reusing or reclaiming such waste, where
this is environmentally sound in accordance with existing
Community or Maltese environmental standards and with the
requirements of these regulations where relevant;
(c) to ensure short and long-term safe disposal of the
extractive waste, in particular by considering, during the design
phase, the management during the operation and after-closure
of a waste facility and by choosing a design which
(i) requires minimal and, if possible, ultimately no
monitoring, control and management of the closed waste
facility;
(ii) prevents or at least minimises any long-term
negative effects, for example attributable to migration
of airborne or aquatic pollutants from the waste facility;
and
(iii) ensures the long-term geotechnical stability
of any dams or heaps rising above the pre-existing ground
surface.
(3) The waste management plan shall contain at least
the following elements
(a) the proposed classification for the waste facility in
accordance with the criteria laid down in regulation 6 of these
regulations and sufficient information justifying that a Category
A waste facility is not required, including an identification of
possible accident hazards;
(b) waste characterisation in accordance with Schedule
2 to these regulations and a statement of the estimated total
quantities of extractive waste to be produced during the
operational phase;
(c) a description of the operation generating such waste
and of any subsequent treatment to which it is subject;
(d) a description of how the environment and human
health may be adversely affected by the deposit of such waste
and the preventive measures to be taken in order to minimise
environmental impact during operation and after closure,
including the aspects referred to in sub-regulations (1), (2), (4)
and (5) of regulation 19 of these regulations;
(e) the proposed control and monitoring procedures
pursuant to sub-regulation (3) of regulation 19 of these
regulations;
(f) measures for the prevention of water status
deterioration in accordance with the Water Policy Framework
Regulations, 2004, and for the prevention or minimisation
of air and soil pollution pursuant to regulation 20 of these
regulations;
(g) a survey of the condition of the land to be affected
by the waste facility.
(h) any other relevant information requested by the
Competent Authority.
(4) The waste management plan shall provide sufficient
information to enable the Competent Authority to evaluate the
operator’s ability to meet the objectives of the waste management plan
as set out in sub-regulation (2) of this regulation and his obligations
under these regulations. The plan shall explain, in particular, how
the option and method chosen as mentioned in indent (i) of paragraph
(a) of sub-regulation (2) of this regulation will fulfil the objectives
of the waste management plan as laid down in paragraph (a) of sub-
regulation (2) of this regulation.
(5) The Competent Authority may specify the format in
which such information is to be made available.
(6) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001.
(7) The waste management plan shall be reviewed
every five years and, or amended, as appropriate, in the event of
substantial changes to the operation of the waste facility or to the
waste deposited. Any amendments shall be notified to the Competent
Authority.
(8) Plans produced pursuant to other Community or
Maltese legislation and containing the information specified in sub-
regulation (3) of this regulation may be used where this obviates
the unnecessary duplication of information and the repetition of
work by the operator, on condition that all requirements under sub-
regulations (1), (2), (3), (4) and (7) of this regulation are met.
(9) The Competent Authority shall approve the waste
management plan on the basis of procedures to be decided by the
Competent Authority and shall monitor its implementation.
In constructing a new waste facility or modifying an
existing waste facility, the operator shall ensure that
(1) the waste facility is suitably located, taking into
account in particular Community or Maltese obligations relating
to protected areas, and geological, hydrological, hydrogeological,
seismic and geotechnical factors, and is designed so as to meet the
necessary conditions for, in the short and long-term perspectives,
preventing pollution of the soil, air, groundwater or surface water,
taking into account especially the Pollution Caused by Certain
Dangerous Substances Discharged Into the Aquatic Environment
Regulations, 2001, the Protection of Groundwater against Pollution
caused by Certain Dangerous Substances Regulations, 2002, and the
Water Policy Framework Regulations, 2004, and ensuring efficient
collection of contaminated water and leachate as and when required
under the permit, and reducing erosion caused by water or wind as
far as it is technically possible and economically viable;
(2) the waste facility is suitably constructed, managed
and maintained to ensure its physical stability and to prevent
pollution or contamination of soil, air, surface water or groundwater
in the short and long-term perspectives as well as to minimise as far
as possible damage to landscape;
(3) there are suitable plans and arrangements for regular
monitoring and inspection of the waste facility by competent persons
and for taking action in the event of results indicating instability or
water or soil contamination
Provided records of the monitoring and inspections shall
be kept, together with permit documentation, in order to ensure the
appropriate hand-over of information, particularly in the event of a
change of operator.
(4) suitable arrangements are made for the rehabilitation
of the land and the closure of the waste facility;
(5) suitable arrangements are made for the after-closure
phase of the waste facility.
(1) The operator shall take the necessary measures in
order to meet Community or Maltese environmental standards, in
particular to prevent, in accordance with the Water Policy Framework
Regulations, 2004, the deterioration of current water status, inter
alia, by
(a) evaluating the leachate generation potential,
including contaminant content of the leachate, of the deposited
waste during both the operational and after-closure phase of
the waste facility, and determining the water balance of the
waste facility;
(b) preventing or minimising leachate generation and
surface water or groundwater and soil from being contaminated
by the waste; and
(c) collecting and treating contaminated water and
leachate from the waste facility to the appropriate standard
required for their discharge.
(2) The operator shall take adequate measures to prevent
or reduce dust and gas emissions.
(3) Where, on the basis of an assessment of
environmental risks, taking into account, in particular, the
Pollution Caused by Certain Dangerous Substances Discharged
Into the Aquatic Environment Regulations, 2001, the Protection
of Groundwater against Pollution caused by Certain Dangerous
Substances Regulations, 2002, or the Water Policy Framework
Regulations, 2004, as applicable, the Competent Authority has
decided that collection and treatment of leachate is not necessary
or it has been established that the waste facility poses no potential
hazard to soil, groundwater or surface water, the requirements set
out in paragraphs (b) and (c) of sub-regulation (1) of this regulation
may be reduced or waived accordingly.
PART VI
INVENTORY OF CLOSED WASTE FACILITIES
The Competent Authority shall draw up and periodically
update an inventory of closed waste facilities, including abandoned
waste facilities, which cause serious negative environmental impacts
or have the potential of becoming in the medium or short term a
serious threat to human health or the environment
Provided that such an inventory, to be made available to the
public, shall be carried out by 1 May 2012.
PART VII
BACKFILLING INTO EXCAVATION VOIDS
(1) No excavation void, whether created through
surface or underground extraction, shall be allowed to be backfilled
without a permit granted by the Competent Authority.
(2) The permit shall contain the elements specified in
sub-regulation (3) of this regulation
Provided that, subject to compliance with all requirements
under this regulation, any permit produced pursuant to other
Community or Maltese legislation may be combined to form a single
permit, where such a format obviates the unnecessary duplication of
information and the repetition of work by the operator or Competent
Authority
Provided further that, the details specified in sub-
regulation (3) of this regulation can be covered by one single
permit or several permits, provided that all requirements under this
regulation are complied with.
(3) The application for a permit shall contain at least
the following details
(a) the identity of the operator;
(b) the location of the excavation void, whether created
through surface or underground extraction;
(c) the backfilling plan pursuant to regulation 23 of
these regulations; and
(d) any other relevant information requested by the
Competent Authority.
(4) The Competent Authority may specify the format in
which such information is to be made available.
(5) The Competent Authority shall only grant a permit
if it is satisfied that
(a) the operator complies with the relevant requirements
under these regulations;
(b) the backfilling into the excavation void, whether
created through surface or underground extraction, does not
conflict directly or otherwise interfere with the implementation
of the relevant waste management plan or plans referred to in
sub-regulation (3) of regulation 4 of the Waste Management
(Permit and Control) Regulations, 2001.
(6) The Competent Authority shall reconsider and,
where necessary, update permit conditions periodically
(a) where there are substantial changes in the backfilling
into the excavation void, whether created through surface or
underground extraction, or the backfill;
(b) on the basis of inspections carried out pursuant to
regulation 29 of these regulations;
(c) in the light of information exchange on substantial
changes in best available techniques.
(7) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001
Provided that the information contained in a permit granted
under these regulations shall be made available to the competent
national and Community statistical authorities when requested for
statistical purposes
Provided further that sensitive information of a purely
commercial nature, such as information concerning business
relations and cost components and the volume of economic mineral
reserves, shall not be made public.
(1) The operator shall draw up a backfilling plan for
the backfilling into the excavation void, whether created through
surface or underground extraction.
(2) The objectives of the backfilling plan shall be
(a) to ensure that the backfilling into the excavation void,
whether created through surface or underground extraction, is
carried out in accordance with existing Community or Maltese
environmental standards and with the requirements of these
regulations where relevant; and
(b) to encourage material recovery by means of
backfilling, where this is environmentally sound in accordance
with existing Community or Maltese environmental standards
and with the requirements of these regulations where
relevant.
(3) The backfilling plan shall contain at least the
following elements
(a) a description of how the environment and human
health may be adversely affected by the backfilling into
the excavation void, whether created through surface or
underground extraction, including the relocation of temporary
constructions, and the preventive measures to be taken in order
to minimise environmental impact during operation and after
closure, including the aspects referred to in sub-regulations
(1), (2), (4) and (5) of regulation 24 of these regulations;
(b) the proposed control and monitoring procedures
pursuant to regulations 24, 25, 26 and 27 of these regulations,
when applicable;
(c) the proposed plan for closure, including
rehabilitation, after-closure procedures and monitoring as
provided for in regulation 26 of these regulations;
(d) measures for the prevention of water status
deterioration in accordance with the Water Policy Framework
Regulations, 2004, and for the prevention or minimisation
of air and soil pollution pursuant to regulation 25 of these
regulations;
(e) a survey of the condition of the land to be affected
by the backfilling.
(f) any other relevant information requested by the
Competent Authority.
(4) The backfilling plan shall provide sufficient
information to enable the Competent Authority to evaluate the
operator’s ability to meet the objectives of the backfilling plan as set
out in sub-regulation (2) of this regulation and his obligations under
these regulations.
(5) The Competent Authority may specify the format in
which such information is to be made available.
(6) The Competent Authority shall make this information
available in accordance with the Freedom of Access to Information
on the Environment Regulations, 2001.
(7) Plans produced pursuant to other Community or
Maltese legislation and containing the information specified in sub-
regulation (3) of this regulation may be used where this obviates
the unnecessary duplication of information and the repetition of
work by the operator, on condition that all requirements under sub-
regulations (1), (2), (3) and (4) of this regulation are met.
(8) The Competent Authority shall approve the
backfilling plan on the basis of procedures to be decided by the
Competent Authority and shall monitor its implementation.
In backfilling into an excavation void, whether created
through surface or underground extraction, the operator shall ensure
that
(1) the excavation void, whether created through surface
or underground extraction, is suitably located, taking into account in
particular Community or Maltese obligations relating to protected
areas, and geological, hydrological, hydrogeological, seismic and
geotechnical factors, and is backfilled in such a way so as to meet
the necessary conditions, in the short and long-term perspectives,
preventing pollution of the soil, air, groundwater or surface water,
taking into account especially the Pollution Caused by Certain
Dangerous Substances Discharged Into the Aquatic Environment
Regulations, 2001, the Protection of Groundwater against Pollution
caused by Certain Dangerous Substances Regulations, 2002, and the
Water Policy Framework Regulations, 2004, and ensuring efficient
collection of contaminated water and leachate as and when required
under the permit, and reducing erosion caused by water or wind as
far as it is technically possible and economically viable;
(2) the excavation void, whether created through
surface or underground extraction, is suitably backfilled to ensure
its physical stability and to prevent pollution or contamination of
soil, air, surface water or groundwater in the short and long-term
perspectives as well as to minimise as far as possible damage to
landscape; and
(3) there are suitable plans and arrangements for regular
monitoring and inspection of the excavation void, whether created
through surface or underground extraction, by competent persons
and for taking action in the event of results indicating instability or
water or soil contamination
Provided records of the monitoring and inspections shall
be kept, together with permit documentation, in order to ensure the
appropriate hand-over of information, particularly in the event of a
change of operator.
(4) suitable arrangements are made for the rehabilitation
of the land and the closure of the excavation void, whether created
through surface or underground extraction; and
(5) suitable arrangements are made for the after-closure
phase of the excavation void, whether created through surface or
underground extraction.
(1) The operator shall take the necessary measures in
order to meet Community or Maltese environmental standards, in
particular to prevent, in accordance with the Water Policy Framework
Regulations, 2004, the deterioration of current water status, inter
alia, by
(a) evaluating the leachate generation potential, including
contaminant content of the leachate, of the backfill during both
the operational and after-closure phase of the excavation void,
whether created through surface or underground extraction, and
determining the water balance of the excavation void, whether
created through surface or underground extraction;
(b) preventing or minimising leachate generation and
surface water or groundwater and soil from being contaminated
by the backfill; and
(c) collecting and treating contaminated water and
leachate from the excavation void, whether created through
surface or underground extraction, to the appropriate standard
required for their discharge.
(2) Where, on the basis of an assessment of
environmental risks, taking into account, in particular, the
Pollution Caused by Certain Dangerous Substances Discharged
Into the Aquatic Environment Regulations, 2001, the Protection
of Groundwater against Pollution caused by Certain Dangerous
Substances Regulations, 2002, or the Water Policy Framework
Regulations, 2004, as applicable, the Competent Authority has
decided that collection and treatment of leachate is not necessary
or it has been established that the backfilling into the excavation
void, whether created through surface or underground extraction,
poses no potential hazard to soil, groundwater or surface water, the
requirements set out in paragraphs (b) and (c) of sub-regulation (1)
of this regulation may be reduced or waived accordingly.
(3) When backfilling into excavation voids, whether
created through surface or underground extraction, which will be
allowed to flood after closure, the operator shall take the necessary
measures to prevent or minimise water status deterioration and soil
pollution in accordance, mutatis mutandis, with sub-regulations (1)
and (2) of this regulation
Provided that the operator shall provide the Competent
Authority with the information necessary to ensure compliance with
Community or Maltese obligations, in particular those in the Water
Policy Framework Regulations, 2004.
(1) The operator shall be responsible for the
maintenance, monitoring, control and corrective measures in the
after-closure phase for as long as may be required by the Competent
Authority, taking into account the nature and duration of the hazard,
save where the Competent Authority decides to take over such
tasks from the operator, after an excavation void, whether created
through surface or underground extraction, has been finally closed
and without prejudice to any Community or Maltese legislation
governing the liability of the operator.
(2) When considered necessary by the Competent
Authority, in order to fulfil relevant environmental requirements
set out in Community or Maltese legislation, in particular those in
the Pollution Caused by Certain Dangerous Substances Discharged
Into the Aquatic Environment Regulations, 2001, the Protection
of Groundwater against Pollution caused by Certain Dangerous
Substances Regulations, 2002, and the Water Policy Framework
Regulations, 2004, following closure of an excavation void, whether
created through surface or underground extraction, the operator
shall, inter alia, control the physical and chemical stability of the
excavation void, whether created through surface or underground
extraction, and minimise any negative environmental effect, in
particular with respect to surface and groundwater, by ensuring
that
(a) all the structures pertaining to the excavation void,
whether created through surface or underground extraction,
are monitored and conserved, with control and measuring
apparatus always ready for use; and
(b) where applicable, overflow channels and spillways
are kept clean and free.
PART VIII
DISPOSAL INTO A RECEIVING BODY OF WATER
The disposal of extractive waste, whether in solid, slurry
or liquid form, into any receiving body of water other than one
constructed for the purpose of disposing of extractive waste, shall
be conditional upon compliance by the operator with the relevant
requirements of the Pollution Caused by Certain Dangerous
Substances Discharged Into the Aquatic Environment Regulations,
2001, the Protection of Groundwater against Pollution caused by
Certain Dangerous Substances Regulations, 2002, and the Water
Policy Framework Regulations, 2004.
PART VIII
ENFORCEMENT
(1) Prior to the commencement of deposit operations
and at regular intervals thereafter, including the after-closure phase,
to be decided by the Competent Authority, the Competent Authority
shall inspect any waste facility covered by regulation 9 or 16 or
17 of these regulations in order to ensure that it complies with the
relevant conditions of the permit
Provided that an affirmative finding shall in no way
reduce the responsibility of the operator under the conditions of the
permit.
(2) The operator shall keep up-to-date records of
all waste management operations and make them available for
inspection by the Competent Authority.
(3) In the event of a change of operator during the
management of a waste facility, the operator shall ensure that there
is an appropriate transfer of relevant up-to-date information and
records relating to the waste facility.
(1) Prior to the commencement of deposit operations
and at regular intervals thereafter, including the after-closure phase,
to be decided by the Competent Authority, the Competent Authority
shall inspect any excavation void, whether created through surface
or underground extraction, covered by regulation 22 of these
regulations in order to ensure that it complies with the relevant
conditions of the permit
Provided that an affirmative finding shall in no way
reduce the responsibility of the operator under the conditions of the
permit.
(2) The operator shall keep up-to-date records of all
backfilling operations and make them available for inspection by
the Competent Authority.
(3) In the event of a change of operator during the
backfilling into an excavation void, whether created through surface
or underground extraction, the operator shall ensure that there is an
appropriate transfer of relevant up-to-date information and records
relating to the excavation void, whether created through surface or
underground extraction.
Any person shall be guilty of an offence under these
regulations if
(a) he fails to comply with any provisions of these
regulations or fails to comply with permit conditions or with
any order lawfully given in terms of any provision of these
regulations; or
(b) he contravenes any restriction, prohibition or
requirement imposed by or under these regulations; or
(c) he acts in contravention of any of the provisions of
these regulations; or
(d) he conspires or attempts, or aids, or abets, any other
person by whatever means, including advertising, counselling
or procurement to contravene the provisions of these regulations
or to fail to comply with any such provisions (including any
order lawfully given in terms of any of the provisions of these
regulations) or to contravene any restriction, prohibition or
requirement imposed by or under the said regulations.
Any person who commits an offence against these
regulations shall, on conviction, be liable
(a) on a first conviction, to a fine (multa) of not less
than one thousand and one hundred and sixty-four euro and
sixty-nine cents (€1,164.69), but not exceeding two thousand
and three hundred and twenty-nine euro and thirty-seven cents
(€2,329.37);
(b) on a second conviction or subsequent convictions, to
a fine (multa) of not less than two thousand and three hundred
and twenty-nine euro and thirty-seven cents (€2,329.37), but
not exceeding four thousand and six hundred and fifty-eight
euro and seventy-five cents (€4,658.75), or to imprisonment
for a term not exceeding two years, or to both such fine and
imprisonment
Provided that whenever any person is found guilty of
committing an offence under these regulations by means of a
vehicle, the owner of the said vehicle, where applicable, is held
liable in the same manner and degree
Provided further that the court may order any person who
has been found guilty of committing an offence against these
regulations to pay for the expenses incurred by the Competent
Authority mentioned in these regulations as a result of the said
offence, the revocation of the permit issued by the Competent
Authority and the confiscation of the corpus delicti, including
the vehicle, if applicable.
(1) The provisions of articles 23 and 30 of the Criminal
Code shall, mutatis mutandis, apply to proceedings in respect of
offences against these regulations, so however that the disqualification
from holding or obtaining a licence, permit or authority shall in no
case be for less than one year.
(2) Notwithstanding the provisions of article 370 of the
Criminal Code, proceedings for an offence against these regulations
shall be held before the Court of Magistrates (Malta) or the Court of
Magistrates (Gozo), as the case may be, and shall be in accordance
with the provisions of the Criminal Code regulating the procedure
before the said courts as courts of criminal judicature.
(3) Notwithstanding the provisions of the Criminal
Code, the Attorney General shall always have a right of appeal to the
Court of Criminal Appeal from any judgement given by the Court of
Magistrates (Malta) or the Court of Magistrates (Gozo) in respect of
proceedings for any offence against these regulations.
Schedule 1
(Regulation 8)
Major-accident prevention policy and information to be communicated to the
public concerned
1. Major-accident prevention policy
The operator’s major-accident prevention policy and safety management system
should be proportionate to the major-accident hazards presented by the waste facility.
For the purpose of implementing them, account shall be taken of the following
elements
(1) the major-accident prevention policy should include the operator’s overall
aims and principles of action with respect to the control of major-accident hazards;
(2) the safety management system should include the part of the general
management system which includes the organisational structure, responsibilities,
practices, procedures, processes and resources for determining and implementing the
major-accident prevention policy;
(3)
the following issues shall be addressed by the safety management
system
(a) organisation and personnel — the roles and responsibilities of
personnel involved in the management of major hazards at all levels in
the organisation; identification of training needs of such personnel and the
provision of the training so identified; and involvement of employees and,
where appropriate, subcontractors;
(b) identification and evaluation of major hazards — adoption and
implementation of procedures for systematically identifying major hazards
arising from normal and abnormal operations and assessment of their likelihood
and severity;
(c) operational control — adoption and implementation of procedures
and instructions for safe operation, including maintenance of plant, processes,
equipment and temporary stoppages;
(d) management of change — adoption and implementation of procedures
for planning modifications to, or the design of, new waste facilities;
(e) planning for emergencies — adoption and implementation of
procedures to identify foreseeable emergencies by systematic analysis and to
prepare, test and review emergency plans to respond to such emergencies;
(f) monitoring performance — adoption and implementation of
procedures for the ongoing assessment of compliance with the objectives set by
the operator’s major-accident prevention policy and safety management system,
and the mechanisms for investigation and taking corrective action in case of non-
compliance. The procedures should cover the operator’s system for reporting
major accidents or near misses, particularly those involving failure of protective
measures, and their investigation and follow-up on the basis of lessons learnt;
(g) audit and review — adoption and implementation of procedures for
periodic systematic assessment of the major-accident prevention policy and the
effectiveness and suitability of the safety management system; the documented
review of performance of the policy and safety management system and its
updating by senior management.
2. Information to be communicated to the public concerned
1. Name of operator and address of the waste facility.
2. Identification, by position held, of the person providing the information.
3. Confirmation that the waste facility is subject to these regulations and,
when applicable, that the information relevant to the elements referred to in sub-
regulation (2) of regulation 8 of these regulations has been submitted to the Competent
Authority.
4. An explanation in clear and simple terms of the activity or activities
undertaken at the site.
5. The common names or the generic names or the general danger classification
of the substances and preparations involved at the waste facility as well as waste which
could give rise to a major accident, with an indication of their principal dangerous
characteristics.
6. General information relating to the nature of the major-accident hazards,
including their potential effects on the surrounding population and environment.
7. Adequate information on how the surrounding population concerned are to
be warned and kept informed in the event of a major accident.
8. Adequate information on the actions the population concerned should take,
and on the behaviour they should adopt, in the event of a major accident.
9. Confirmation that the operator is required to make adequate arrangements
on site, in particular liaison with the emergency services, to deal with major accidents
and to minimise their effects.
10. A reference to the external emergency plan drawn up to cope with any
off-site effects from an accident. This should include advice to co-operate with any
instructions or requests from the emergency services at the time of an accident.
11. Details of where further relevant information can be obtained, subject to
the requirements of confidentiality laid down in Maltese legislation.