section 1 of this regulation are notified
1. on the basis of Chapter 4. section 9 of the Environment Act in respect of section 10,
2. on the basis of Chapter 9. section 6 and 15. section 28 of the environmental code in
case of 9, 11, 25, 27-41, 45, 46, 48-54, 58, 59, 64, 67, 68
and 70 sections,
3. with the support of 26 kap. section 19 of the environmental code regarding paragraphs 42 to 44,
4. with the support of 26 kap. section 20 of the environmental code in terms of section 47,
5. with the support of 27 Cape. section 2 of the environmental code in relation to paragraphs 55 to 57,
and
6. Moreover, pursuant to Chapter 8. 7 or 11 §
the Constitution Act. Regulation (2014:432).
Words and expressions in the regulation
paragraph 2 of this regulation,
geological formation: a litostratigrafisk unit within which
distinct layers of rocks can be found and mapped,
geological storage of carbon dioxide: storage of carbon dioxide streams
who has injekterats in an underground geological formation,
storage place: a distinct volume within a geological formation
used for the geological storage of carbon dioxide with
the associated surface installations and injekteringsanläggningar,
the storage complex: the storage site and surrounding geological
area that can affect storage integrity and security,
and
supervisory authority: the authority under
environmental protection Regulation (2011:13) supervises
geological storage of carbon dioxide. Regulation (2014:432).
3 section hydraulic unit referred to in this regulation a cavity
as
1. is hydraulically communicating,
2. is porous,
3. has such properties that pressure changes are technically
measurable,
4. lead the technically measurable pressure changes on, and
5. limited by impenetrable faults, salt layers,
litologiska borders or other impermeable layer or
the wedge formation of the geologic formation or of a
bedrock in this formation comes into the day.
paragraph 4 for the purposes of this regulation,
CO2 stream: a flow of substances that results from
processes for CO2 capture, and
koldioxidplym: the volume of carbon dioxide which spreads in a geological
formation.
paragraph 5 of this regulation,
significant disturbance: any disturbance at the injection or
storage or in the case of the storage complex
nature that may pose a risk of leakage of CO2
or risk to human health or the environment,
corrective action: any action to remedy
a significant disturbance or seal a leak be taken to
prevent or stop emissions of carbon dioxide from a
storage complexes,
the closure of a storage site: permanent cessation of
koldioxidinjektering in a storage location, and
liability transfer: transfer to the State of the responsibility that
an operator has in the case of a storage location.
section 6, otherwise, words and expressions in this regulation the same
importance in the environmental code.
Application
section 7 of this Regulation shall apply to the geological storage of
carbon dioxide in Sweden, the Swedish continental shelf and the Swedish
economic zone. Provisions on the continental shelf, see the
Lagen (1966:314) om kontinentalsockeln. Provisions on
Sweden's economic zone, see the Act (1992:1140)
economic zone.
section 8 of the Ordinance shall not apply to storage
1. refers to a combined planned storage of less than 100 000
tonnes of carbon dioxide, and
2. measures are being taken for research, development or testing of new
products or processes.
The location of a repository
§ 9 A geological formation may be used for the storage of
CO2 only if
1. There is no significant risk of leakage of
carbon dioxide from the repository, and
2. storage of carbon dioxide on the site does not present any
significant risk to human health or the environment.
section 10 of the geological storage of CO2 may only occur in Swedish
economic zone and the areas that are not part of the real estate in
Swedish territorial waters from a nautical mile off
the baseline.
Such storage shall not take place
1. in the vertical water column (water column) between
the surface of the water and bottom sediments, or
2. in storage complexes extending beyond a State within
The territory of the European Union or outside the economic
zone into such a State.
If, pursuant to article 6 of the 1996 Protocol to the 1972
Convention on the prevention of marine pollution by
dumping of wastes and other matter (SUN 2000:48) requires a
specific agreement between Sweden and another State and Sweden
has not entered into such a contract, the storage of carbon dioxide
not be in a storage location that spans both
Swedish territory or the Swedish economic zone and
the other State's territory or economic zone.
Assessment of storage site suitability
section 11 of The who intends to carry on a business with geological
storage of CO2 will make an assessment of the geological
line suitability as repository and acquire the
knowledge and information necessary to make the assessment.
The assessment shall be made in accordance with paragraphs 12 and 25 and
1. include a description and an evaluation of
the storage complex and its surrounding area, and
2. be made to the methods which, at the time of the assessment is
the best.
Model for the assessment of appropriateness
section 12 of the assessment under section 11 is included making a volumetric
and three-dimensional static geological model of
the storage site and storage complex. CapRock and
areas and fluids that are interconnected by hydrological
the storage site and storage complex to be included in the model.
If necessary to meet the requirements of best practice,
assessed with a series of models.
section 13 A model under section 12 shall be done with the safe knowledge that
possible in the case of
1. storage complex geology and Geophysics,
2. the presence of the storage complex of the groundwater that can
be used for drinking water and storage complex hydrogeology
otherwise,
3. volumetric calculations of pore volume for injection of
CO2 in the storage complex and its final
storage capacity and storage complex in reservoarteknik
Moreover,
4. dissolution rate, mineraliseringstakt and other
geochemistry,
5. permeability, sprickbildnings press and other
geomekanik,
6. seismicity,
7. Wells and boreholes, which can serve as pathways and
the presence of otherwise of natural and manufactured cracks
and channels and wells, direction, cracks and
channel condition,
8. the areas surrounding the storage complex that may be affected by
the storage of CO2 in the storage site;
9. population distribution in the region is over
the place of storage;
10. close to Natura 2000 areas for protection under
European Parliament and Council directive 2009/147/EC of 30
November 2009 on the conservation of wild birds, in wording as
Council Directive 2013/17/EU, and Council Directive 92/43/EEC of
21 May 1992 on the conservation of natural habitats and of wild fauna
and plants, in the wording of Council Directive 2013/17/EU,
11. access to potable ground water, hydrocarbons and other
valuable natural resources,
12. activities relating to the exploration, production, or
storage of hydrocarbons, geothermal use of aquifers,
the use of underground water reserves and other
activities surrounding the storage complex, and any
interaction with such activities,
13. close to the places where carbon dioxide might
come for storage in a repository with an estimate of
the total potential of CO2 as economically can be
available for storage, and
14. access to suitable transport network for carbon dioxide.
The knowledge referred to in the first subparagraph shall be documented.
Knowledge of geoscience and storage complex
geomechanical characteristics referred to in the first subparagraph 1 – 7 are to be included in the
the model.
section 14 of the model under section 12 shall be carried out with computerised
reservoir Simulator and, with the use of the knowledge
obtained under section 13, describe the storage complex in the case of
1. the physical trap geological structure,
2. reservoir geomechanical, geochemical and flow-related
properties,
3. reservoir layer in the form of caprock,
seals, porous and permeable horizons and surrounding
formations,
4. the problem and the possible presence of antroprogena
fissures and channels,
5. storage complex area and depth,
6. pore volume and porstorleksfördelningen,
7. the initial liquid distribution, and
8. any other relevant characteristics.
section 15, Every uncertainty in a model under section 12 shall be assessed.
The uncertainty for each parameter that is used for the model shall
be assessed through the development of a series of scenarios for each
parameter and calculation of an appropriate
probability range.
Dynamic modeling for the aptitude assessment
16 § using the models referred to in section 12 shall
the assessment under section 11 shall be made with a dynamic modelling.
Simulations of injection of CO2 in the storage site
to be included in the modeling. The simulations shall relate to several different
time step of Grouting.
section 17 of the modeling aim to assess the
CO2 injection and storage site dynamic
behavior. Short-term and long-term simulations to be done
so that it is possible to assess what is going on with
the carbon dioxide and how it behaves for decades and
millennia.
Modelling should be made taking into account the
1. carbon dioxide streams characteristics,
2. the potential injekteringstakten,
3. how the injected carbon dioxide reaction with minerals in
the storage complex is reflected in the model (reactive
processes),
4. the dissolution rate of water,
5. the reservoir Simulator used and that it may be required
multiple simulations to validate certain findings, and
6. how effective modeling is concerned about how the different
individual effects in the Simulator to interact (merge
processes).
section 18 of the modeling will provide knowledge about the
1. the geological formation pressure and temperature as a
function over time by injekteringshastighet and cumulative
injekteringsmängd,
2. areal and vertical spread over time,
3. characteristics of carbon flow in the reservoir and flow
behavior in different phases (phase behavior),
4. mechanisms for and extent of carbon sequestration
including overflow levels and lateral and vertical
seals,
5. secondary containment systems in the storage complex which
as a whole,
6. storage capacity and pressure gradients on
the place of storage;
7. risk of cracking of caprock
and storage complex;
8. the risk that carbon dioxide should penetrate into the caprock,
9. risk of leakage from the storage site by abandoned
or inadequately sealed wells or otherwise,
10. the migration rate from open reservoirs,
11. sprickförseglingstakten,
12. changes of pH, mineral formation or other
factors related to formationernas fluid chemistry or reactions
related to this,
13. displacement of fluids in the formation, and
14. increased seismicity and elevation at surface level.
section 19 of a reactive modelling should be made to assess the
the effects of changes and reactions referred to in section 18 of the
12.
Aptitude assessment accuracy
20 § Multiple simulations shall be undertaken to establish the
aptitude assessment accuracy in case of certain
parameters. The simulations shall be based on the parameters
changes in the static geological Earth model, as well as on various
probability calculations and assumptions in the dynamic
the modeling.
Risk assessment in the aptitude assessment
section 21 of the suitability assessment of storage site should contain
an assessment and description of the risks, an
exposure assessment and impact assessment under sections 22 to 25.
The assessment shall take into account all the factors that have
importance of assessment accuracy.
section 22 of the description of hazards should be done with the help of knowledge
from the dynamic modeling under paragraphs 16 to 19 and from
the simulations under section 20. Risk characterisation shall include
the full range of possible operating conditions for examining
Security storage complex and shall contain a statement
for the potential for leakage of CO2 from
the storage complex with regard to the
1. potential leakage pathways;
2. the potential magnitude of leakage from läckagevägarna
(feeds),
3. a maximum of reservoartryck, maximum injekteringstakt,
temperature, sensitivity to various assumptions in the static
geological models and other critical parameters that can
affecting potential leakage,
4. displacement of fluids and the formation of new topics in the
geologic formation and other secondary effects of
CO2 storage,
5. the structures that will be made in the context of the project,
and
6. factors that might pose a hazard to human
health or the environment.
section 23 of the exposure assessment shall be based on the description of the
environment, population and activities above
the storage complex, what happens to the carbon dioxide and how it
behave in the event of leakage from the potential
leakage pathways have been identified.
24 § Impact assessment shall be based on information about
the sensitivity of particular species, communities or habitats
who may be affected by potential läckagehändelser that has
have been identified. The assessment should include the effects of
1. exposure to high levels of carbon dioxide in the soil, in
bottom sediments in the biological world, the bottom (benthic
the zone) and in the biosphere that may lead to choking or
carbon dioxide poisoning,
2. reduced pH values in the surrounding area as a result of
carbon leakage, and
3. other substances that may be present in leaking CO2 streams on
because of the existence of impurities in the carbon dioxide streams
injekterats or new substances formed through storage of
carbon dioxide.
Impact assessment must be carried out with a temporal and spatial scale and
be linked to a series of potential läckagehändelser of different
scope.
section 25 of the risk assessment should
1. on the basis of risk description and exposure
and impact assessments,
2. cover the security and integrity of the storage complex on card
and long term as regards the risk of leakage under the
proposed conditions of use,
3. cover the effects on human health and the environment, and
4. include an assessment of the uncertainties that have
identified in connection with the description and assessment of
the storage location and, when possible, a description of the
opportunities to reduce uncertainty.
Permits and plans
section 26 of the Regulations that authorisation to geological
storage of carbon dioxide are found in environmental assessment regulation
(2013:251) and the Regulation (1998:899) concerning environmentally hazardous
activity and health protection.
section 27 of The who intends to carry on a business with geological
storage of carbon dioxide, before business begins establishing
proposal for a
1. a plan describing the measures to be taken in
the event of leakage of CO2 or significant disruptions to
storage complex (corrective action plan),
2. a monitoring plan for inspection in accordance with chapter 26. § 19
Environment Act and section 43 of this regulation, and
3. a plan for maintenance after closure.
Item 2 of the first paragraph apply in addition to the monitoring programmes that can
be required under Chapter 26. section 19 of the environmental code.
Provisions relating to an application for a permit for geological
storage of carbon dioxide should include a proposal for a
monitoring plan and a draft plan for remediation
operations, see Chapter 22. 1 a of the environmental code.
section 28 Permits for geological storage of CO2 may only
be used if the operator demonstrates that the operator has
the financial resources required to carry out geological
storage of carbon dioxide and to carry out the monitoring
as required by section 42.
section 29 If someone has permission to the geological storage of
carbon dioxide according to Chapter 9. the environmental code, may not be
authorization for storage in the same storage location.
30 § If there is more than one storage location in a hydraulic
device, is authorized only if the potential
touch interaction is such that both the storage locations
at the same time, comply with the requirements of the Environment Act and regulations
announced on the basis of the beam.
section 31 On multiple has applied for permits for geological storage
of carbon dioxide in the same storage location, it shall take precedence as a
has
1. permission to explore the continental shelf for the purposes of geological
storage pursuant to lagen (1966:314) om
the continental shelf,
2. completed the survey of the site,
3. met all the conditions in the permit, and
4. applied for permission to the geological storage of carbon dioxide.
Monitoring plan
32 § the monitoring plan referred to in paragraph 27 2
shall relate to the management of the risks identified in the
the risk assessment according to paragraphs 21 to 25. The plan shall comply with the requirements of
paragraphs 33 to 37.
section 33 of the monitoring plan should be detailed
information on the monitoring that will be done during
the business ' main phases. This includes monitoring of
baseline, the monitoring of operation and monitoring
closing. For each operational phase to the monitoring plan
contain specific information about the
1. the parameters to be monitored,
2. What is the technology used for the monitoring and the reasons for
the selected surveillance technologies,
3. which locations are being monitored and the reasons for the selected
locations for sampling, and
4. when sampling should occur and the reasons for
tagningarnas sample distribution over time.
section 34 monitoring plan must include:
1. monitoring of leakage of CO2 at
injekteringsanläggningen,
2. monitoring of the volumetric flow of carbon dioxide at
injekteringsbrunnstopparna,
3. monitoring of the pressure and temperature at
injekteringsbrunnstopparna, to the extent necessary for the
determining the mass flow rate,
4. chemical analysis of the injected material,
5. monitoring of reservoir temperature and pressure, in the
extent necessary to determine CO2 phase,
behavior and status, and
6. monitoring of the parameters that are otherwise
identified as necessary to meet
the purpose of surveillance.
section 35 in relation to the technology used for monitoring should
the monitoring plan may mean that the technology is chosen as the
with the best available techniques when the plan is drawn up. The
selected technology should
1. involve the presence, location and
migration routes in the geological formations, and at
formationernas surface can be detected,
2. provide information on koldioxidplymens behavior in terms of
pressure and volume, as well as horizontal and vertical sprawl so
the simulations of the dynamic model in accordance with paragraph 16 of may
adjusted for increased accuracy, and
3. in the event of a significant disruption or
carbon migration from the storage complex give information about
previously undetected leakage pathways within a large geographic
area.
36 § monitoring plan will mean that the monitoring
adapted to current conditions by
1. information collected is compiled and interpreted, and
2. the observed results are compared with the behaviour that
foreseen in modelling and simulation under section 20.
section 37 If the observed results referred to in paragraph 2 of section 35 is different
significantly different from that envisaged, the
the models referred to in section 12 shall be calibrated so that the models
reflects the observed results. The calibration shall
based on the data captured in the plan and the
additional data that may be needed to increase security in the
assumptions that are added to the basis for the calibration.
Financial security
38 the security referred to in section 15. 36 § environmental code should
apply until
1. transfer of responsibility has been made, or
2. a new security has been provided in accordance with a new
permit, if the permit envisaged when the safety
asked have been revoked in accordance with Chapter 24. paragraph 3 of the Swedish environmental code and
the regulatory authority has not decided to the storage site should
be closed.
Composition of CO2 streams
section 39 The CO2 stream that are injected in the storage location,
consist of only carbon dioxide. CO2 stream may, however,
contain traces of other substances than carbon dioxide derived from
sources of carbon dioxide emissions, the separation or
injekteringsprocessen and trace substances added in connection
with monitoring and control of the movements within the
the storage complex. The concentrations of such substances must not
exceed levels that could
1. have a negative impact on the storage location or security
and operation of the infrastructure used
transport of carbon dioxide,
2. constitute a significant risk to human health or the
the environment, or
3. contrary to the requirements of other legislation.
section 40 of the operator must not allow a low power
injected into the storage site without having
1. composition of the CO2 stream is analysed and
the presence in it of corrosive substances and other substances that have
significance for risk assessment according to paragraphs 21 to 25, and
2. made a risk assessment of carbon dioxide the power given
to the levels of other substances than carbon dioxide referred to in section 39
and with respect to licence conditions on
the composition of the CO2 stream.
41 § the operator shall keep a list of
the quantity and composition of, and the characteristics of the
CO2 streams delivered to and injected in
plant.
Monitoring and control
42 § the operator's inspection in accordance with chapter 26. § 19
the environmental code, in terms of geological storage of carbon dioxide
aim to
1. compare the actual and modelled behaviour of the
carbon dioxide and the water contained in the storage location,
2. detect significant disturbances,
3. monitor the movements within the storage complex;
4. detecting leakage of CO2;
5. detection of significant adverse effects on drinking water and
the surrounding environment;
6. detection of significant adverse effects on human health
or the environment,
7. assess the effectiveness of remedial actions
taken,
8. continually assess safety and storage complex
function in the short and long term, and
9. assess whether the stored carbon dioxide will remain
completely and permanently contained.
The control should include injekteringsanläggningen and
the storage complex. If it is possible to control even
include koldioxidplymen and the surrounding area.
43 § the operator shall update the monitoring plan in
needs and not more frequently than every five years.
44 section supervisor shall examine the updates of
the monitoring plan.
Leakage of CO2 and interference
45 section where for a facility for the storage of carbon dioxide
occurs significant leakage of CO2 or significant
interference, the operator shall
1. as soon as possible inform the supervisory authority and the
the authority is the supervisory authority under the law
(2004:1199) on emissions trading, and
2. adopt measures, in accordance with the plan for remediation
measures and other measures that may be required to
protect human health or the environment.
§ 46 if the operator fails to comply with an order from
the supervisory authority to take action as required under section 45
or if the supervisory authority is of the opinion that it is required by other
reasons, the supervisory authority shall apply the measures provided for in
the operator's expense.
Environmental report
47 § in the case of geological storage of carbon dioxide, such
environmental report referred to in chapter 26. section 20 of the environmental code, in addition to the
as follows from section 31 of the Ordinance (1998:899) concerning environmentally hazardous
activity and health protection or regulations announced by
The environmental protection agency, contain
1. the results of the surveillance referred to in section 42;
2. information about the surveillance technology being used,
3. a copy of the list that has been conducted in accordance with section 41, and
4. proof that the financial guarantee is still
valid and in force.
Conditions for closure of the storage site
48 § a storage site shall be closed only if the
the supervisory authority decided that the place of storage,
be closed.
Decision to a storage site should be closed
49 section Supervisor, after application of the
the operator may decide that the storage site should be closed,
If
1. the operator has fulfilled the conditions for closure
as determined in the permit,
2. the operator has made an update of the plan
for maintenance after closure referred to in section 27, first paragraph
3 and the update include a risk analysis and an analysis of
the best possible technology for closure of the repository, and
3. the supervisory authority considers that the updated plan for
maintenance after closure can be approved.
section 50 of the regulatory authority may, in the particular case, give dispensation
from the requirement that all conditions relating to the closure of the State
must be fulfilled.
Responsibilities and obligations after
closure
51 § When the regulator has decided that an
the storage site should be closed, the operator shall
1. sealing the storage site and the removal of
injekteringsanläggningarna, and
2. prior to the transfer of responsibility has been
(a) according to § 42) monitor,
b) take remedial action under section 45;
c) surrender if necessary according to the law
(2004:1199) on emissions trading in the event of
leakage of CO2;
d) where necessary, take preventive measures under Chapter 2.
the environmental code and the remedial measures in accordance with Chapter 10.
the environmental code, and
e) establish environmental report in accordance with chapter 26. section 20 of the environmental code and
section 47 of this regulation.
The conditions for transfer of responsibility
section 52 The responsibility referred to in paragraph 2 of section 51 shall be taken over by
the supervisory authority when it has decided to
the transfer of responsibility will take place and the obligations set out in paragraphs 53 to 55 is
met.
section 53 Before transfer of responsibility shall include all available
data show that the stored CO2 will remain
totally enclosed permanently. To carbon dioxide must be assessed
be totally permanently enclosed,
1. the injected CO2 behaviour in conformity with
the modeled behavior,
2. there be no detectable leakage of CO2;
and
3. it is likely that the repository will
be sustainable.
54 section supervisor shall determine the time at which the
the transfer of responsibility pursuant to section 52 shall take place at the earliest. Period
between the time of the decision to the storage site should
closed and the time of the transfer of responsibility should, however, always
amount to at least 20 years, unless the supervisory authority
considers that all available data indicate that the stored
the carbon dioxide will remain fully and permanently
contained at an earlier time.
55 § the operator shall pay a fee to
the supervisory authority before the transfer of responsibility.
The fee will be used to cover the supervisory
costs to ensure that the carbon dioxide remains
completely and permanently contained after
the transfer of responsibility.
56 section supervisor shall determine in each individual case
the size of the fee pursuant to § 55, taking into account the
information about the storage that is relevant in order to assess
the costs for discharging the responsibilities covered by
the transfer of responsibility. The fee shall, however, always cover
the costs of monitoring for a period of 30 years from the
the transfer of responsibility.
57 § Supervisor may provide for how
the fee will be calculated, how it should be paid and other conditions
relating to the fee.
Cases of transfer of responsibility
58 section If an operator applying for the transfer of responsibility
or the regulatory authority on its own initiative take up such a
question, the operator shall provide a report certifying that the
the requirements of section 53 is met.
59 section Supervisor may provide for what
report under section 58 shall contain and how the data should
are reported.
60 § supervisor shall make the report referred to in 58
§ available for European Commission within one month from the
the report has been received in the case.
61 § When the conditions according to §§ 53 and 54 are met
the supervisory authority shall prepare a draft decision on
the transfer of responsibility and in the draft set
1. the manner in which it has been established that the repository has
sealed and injekteringsanläggningarna have been removed, and
2. the additional requirements for the sealing of the storage site and
for the removal of injekteringsanläggningarna as
the supervisory authority deems necessary.
If the supervisory authority is of the opinion that the conditions for
the transfer of responsibility is not met, it shall
inform the operator about the reasons for this.
62 section supervisor shall send a copy of the data
the case and the draft decision on transfer of responsibility to the
The European Commission and give it the opportunity to be heard.
63 § when the European Commission has given its opinion of the draft
to decisions or announced that it will not give its opinion
and when the regulator is satisfied that
the conditions in paragraph 51 and 53 to 55 sections are
met, the supervisory authority shall issue a final decision in
If the transfer of responsibility. The decision shall contain the reasons for the
deviation from the comments made by the Commission.
The supervisory authority shall inform the Commission of the decision.
Revocation of authorization
section 64 Of the authorisation for the geological storage of carbon dioxide has
been revoked by virtue of Chapter 24. section 3 of the environmental code, may
the supervisory authority may decide that the place of storage,
be closed.
65 section if it is likely that a new State for
activities will be provided, the regulatory authority in the
rather than decide that the storage site should be closed
submit to the operator to take the necessary steps in
pending a new authorisation is needed to
1. monitor according to § 42,
2. take corrective measures under section 45;
3. comply with the CO2 streams in the State
and in paragraphs 39 and 40,
4. surrender allowances under the Act (2004:1199) if
carbon trading, and
5. take action under Chapter 2. section 3 and 10.
the environmental code.
If the supervisory authority's injunction does not
followed, the supervisory authority of the operator's
the cost of carrying out the necessary measures. The injunction shall
contain an indication to that effect.
section 66 If the regulator decides that a storage site shall
closed after the authorization has been revoked, shall
the supervisory authority at the expense of the operator
1. make sure that the plan for maintenance after closure is
updated and the update include a risk analysis and
an analysis of the best available technology for technical improvements
and the closing of the place of storage;
2. take measures according to the plan, and
3. take the necessary measures to comply with the requirements of § 51
2.
67 § If a permit for geological storage of carbon dioxide has
been revoked by virtue of Chapter 24. section 3 of the environmental code, may
the regulatory authority may decide to transfer of responsibility will take place.
Liability in such a case, the transfer may take place only when all
the available evidence indicates that the stored CO2
will remain completely and permanently contained,
the repository is sealed and injekteringsanläggningarna
been removed.
Liability after transfer of responsibility
68 section costs incurred due to inadequate
information, non-disclosure of relevant information, negligence,
intentional deception, lack of care or other errors of
the operator, shall be paid by the operator while
If the transfer of responsibility has been made.
List of closed storage sites
section 69 authority should maintain a list of given
permission for storage of carbon dioxide and of closed
storage sites.
In the case of closed storage sites to the list
contain
1. information in the form of maps and cross-sections showing the
closed storage site spatial demarcation, and
2. information that is relevant to assessing whether the stored
the carbon dioxide will remain fully and permanently
enclosed.
70 section Supervisor may provide for
obligation on operators to provide the information
needed list pursuant to section 69.
71 § When the supervisory authority manifests itself in questions about permits
for activities that may affect or be affected by a closed
storage site shall ensure that the information from the
the list is entered in the trial.
Supervision
section 72 rules 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.
73 section for each facility for the purposes of geological
storage of carbon dioxide, the supervisory authority shall make at least one
monitoring visits a year for three years from the
the storage site was shut down and every five years thereafter, until
transfer of responsibility has been made.
Tillsynsbesöken shall include Grouting resin and
monitoring plants and storage complex effects
on human health and the environment. If necessary, the visits
also include injekteringsanläggningarna and other
surface facilities, assessing the injection and monitoring
carried out by the operator and the control of the registry
held by the operator.
74 § Supervisor should always make the monitoring visits
1. If the supervisor became aware of leakage of
carbon dioxide or significant disruptions,
2. the environmental report indicates that the condition or conditions that
applicable to the business have not been followed and the deviation does not
is calling,
3. If serious complaints relating to human health or the
the environment has been focused on the business, or
4. in other situations where the administrative authority finds that
appropriate.
75 section no later than two months after the monitoring visits to
the supervisory authority
1. in a supervision report describe how the business meet
the terms and conditions applicable to it and specify whether
additional measures need to be taken, and
2. send the report to the operator and the appropriate
make the report available to the public.
76 section supervisor shall regularly review the
financial security referred to in section 38, and assess whether it is
adapted to the need.
section 77 When the transfer of responsibility has taken place, monitoring visits in accordance with
sections 73 and 74. The regulatory authority may reduce its
surveillance as specified in section 42 to the level that is needed to
detecting leakage of CO2 and significant disruption.
If leakage of CO2 or significant interference detected
of the supervisory authority or will to the supervisory
knowledge, the storage location is being monitored to the extent
required to assess the scale of the problems and the
remedial effectiveness.
Cross-border cooperation
78 section Supervisor and the authorities examining the issues
for the geological storage of CO2 shall take the
measures for cooperation with other relevant EU countries needed
for questions regarding transboundary movements of
CO2, transboundary storage sites and
transboundary storage complexes should be resolved in a way that
comply with the provisions of the concerned countries are implementing
European Parliament and Council directive 2009/31/EC of 23
April 2009 on the geological storage of carbon dioxide and amending
Council Directive 85/337/EEC, European Parliament and Council
Directive 2000/60/EC, 2001/80/EC, 2004/35/EC, 2006/12/EC and
2008/1/EC and Regulation (EC) No 1013/2006, the wording
pursuant to European Parliament and Council Directive 92/EU.
Questions about storing carbon for someone else
§ 79 Questions about storing carbon for someone else under 28
Cape. 14 and 15 of the environmental review by the
the supervisory authority.
80 section Of a query according to Chapter 28. section 14 of the
the environmental code falls under the jurisdiction of both the Swedish and
or more other EU countries ' jurisdiction, shall
the review authority shall consult the relevant authorities in
the other countries so that the provisions apply to a
uniform manner.
Reporting
81 section supervisor shall fulfil the
reporting obligations arising from
1. Article 27 of the European Parliament and Council directive
2009/31/EC, and
2. decision 2007/2 of the Convention for the protection of the marine
environment of the North-East Atlantic (SUN 1994:25).