The system in IS is pretty similar to the system in DK. New permits are not issued when there is a change. The permitting authority reconsiders the permit to see if the change fits within the scope of the permit; if not, the authority changes the permit. The process is very much the same as for a new permit, with consultation for 4 weeks etc. The system in Iceland is also similar to DK regarding the EIA, if the change fits within the EIA after a screening. The IS law gives the authority the possibility to review if there is a need to make a new EIA process. Permits are issued every 12 or 16 years and the authorities have regular overviews to see if it is up to date. If there is a new technology or if the law has changed, the permit can be reviewed. A review can be initialised by the operator or the agency.
The operator is required to notify the supervisory authority about changes in the operation. The supervisory authority and permitting authority are the same authority.
Regarding the question about green transition there are no special processes for this in the permitting process. However, there are some other tools such as tax relief promoting green transition.
NO regulates the activity, not the installation. In many ways a permit is a combination of decisions made over a time period of many years. For changes in a permit that extend emissions the operator has to apply for a change as a new activity. The process is the same as for a new permit. In the process the authority has to assess if the increase has an effect on the pollution. The operator is required to do a new EIA if the thresholds for when an EIA is needed are exceeded. It is then a new hearing process as if there were a new application. However, if there are no changes to the emissions or nuisance to the environment, there is no need for a new EIA.
The operator is required by law to work continuously to reduce emissions from the industry. The operator also is responsible to have a permit that reflects the activity carried out, based on how the activity is described in the application. Not all changes require a change in permit or notification to the authority, only increases in emissions, but if the activity is no longer in line with the permit, then a change in the permit is needed. The operator must then begin a dialogue with the permitting authority.
The operator reports to the supervisory authority every year and there are regular inspections.
SE concluded that the systems are quite similar in this aspect. There is a possibility to make a change in the permit unless the change is too great; the process is pretty much the same as a new permit.
In SE, if the change in the operation is small, the operator can just inform the supervisory authority. If the supervisory authority deems that the change is too big to be subject to notification, if there have been many changes to the activity, or if the permit is old, it is possible for the supervisory authority to require the operator to apply for a new permit.
The supervisory authority is separated from the permitting authority.
There is so far no priority or possibility to prioritise installations for the green transition.
If the authorities think that there is a need for a new application and the operator does not agree, what happens? What happens when the system builds upon a joined organisation for supervision and permitting, and you don’t agree with each other? Can the authorities make changes to the permits of their own accord?
In DK the supervising and permitting authority is the same. If the operator does not agree with the authority’s assessment an administrative procedure is initiated.
It is basically the same in NO as in DK. When an inspection is performed and the activities are out of the scope of the permit, the operator is informed that they operate illegally. If the operator does not take action, there are enforcement activities. The decision can be appealed in an administrative order (decisions from statsförvalter can be appealed to miljödirektoratet).
A change in the existing permit is a part of the supervising process and not the permitting process. The supervisory authority inspects if the operator acts within the permit or in a manner that creates pollution outside the frame of the given permit. Also there has to be a proportionality between the need for change in the existing permit and the costs of a new application.
IS: If the operator does not want to apply for a change in the permit, the authority can make changes to the permit. The authority can for example make changes to conditions and demand information from the operator. This is not done frequently; it is only for big and important changes, and the procedure needs to follow administrative law. The situation where the officers responsible for supervision and the officers responsible for permitting do not agree has not occurred yet. If the public health authority and the Environmental Agency do not agree the conflict is referred to the Minister for a final ruling.
In NO It is possible for the authority to make changes to the permit. There are conditions in the law that describes when and the authority must inform the operator. The operators need predictability, and the change has to be reasonable. Necessary investments and costs must be considered. For example, if the authority is informed that new technology is developed that can decrease emissions and the industry does not adopt this new technology the authority can have a dialogue with the operator and inform the operator that the authority intends to change the permit. NO lost many pulp and paper industries because the industry could not keep up with the new techniques. As in IS, the possibility for authorities to change permits is not used on a frequent basis.
In FI changes in permits can no longer be initiated by the permitting authority, but changes can be initiated by the supervisory authority, by the relevant authority protecting the public interest or a party suffering harm, or by certain registered associations or foundations (whose purpose is to promote the protection of the environment, human health or nature conservation, or the pleasantness of the living environment), and in whose operating area the environmental impacts in question arise. There has been a concern that the information in these cases is not the same as in the cases where the change is initiated by the operator. Changes are being made in the regulation to increase the possibility for permitting authorities to ask for supplements to the application.
What are the main challenges in the permitting process?
FI: One challenge is of course to define which changes are major changes. If there are no numbers or any exact data to base the decision on, it can be problematic to decide if the change is big enough to change the permit.
In principle the problems are very similar as the ones discussed regarding scenario A: to get the proper information and quality of the applications, to make sure there are enough supervisors to maintain a dialogue, keep track of developments and to work proactively, and to ensure enough resources for the permitting authorities. The legislation is comprehensive, and that is necessary, but some processes can take years.
DK: As the permitting process for changes is pretty much the same the challenges are pretty much the same: the quality of the applications, and the need to ask for more information. The authorities struggle with baseline reports, the habitat directive and the water frame directive because they are time consuming and legally difficult.
IS agrees with DK; the same problems occur in IS. It can be time consuming to go over the data and to see if it is satisfactory or not. One of the latest changes that was not implemented in Iceland until 2018 is the requirement for a baseline report. It has proved complicated to get started with these reports, but it is getting better.
NO: In short, we can echo what others said.
The challenges in SE are the same as in the other countries. A main challenge is to determine whether a whole new permit is needed or not.