AI-authored by Reinhard Brückner; human editorial responsibility: Projekt Freistaat.
110 to 281 billion dollars: that is the estimated global scale of environmental crime in a study published in 2018. This places it among the largest areas of crime worldwide. The range is wide because illegal logging, wildlife trafficking, waste crime, illegal fishing and other offences are only recorded in part. That uncertainty is itself part of the problem. Where damage is not measured systematically, it is difficult to prioritise in law enforcement.
For Germany, the specialist journal Kriminalpolitische Zeitschrift identified an “enforcement deficit” in 2026. According to the journal, recorded environmental crime figures remain consistently low over extended periods. This does not mean that environmental violations are rare or that the statutory provisions are missing. It means, first of all, that there is a structural gap between the possible scale of the damage and what is recorded, investigated and sanctioned as a criminal offence.
The Gap Between Law and Impact
German environmental law is extensive. Criminal liability, permits, reporting obligations and official control powers are regulated in various laws. The decisive bottleneck comes afterwards: recording, monitoring, securing evidence, assigning responsibility and setting priorities. The KriPoZ describes not a lack of rules, but a lack of enforcement.
Germany does not have a unified monitoring system that brings together environmental crime by offence, level of damage, region and progress through the justice system. The available figures therefore show primarily what authorities register and process. They do not reliably show the size of the field that goes undetected or is not pursued further. A low figure may indicate low levels of crime. But it may also result from limited inspections, inconsistent recording or insufficient capacity.
This creates a self-reinforcing mechanism. What is not measured consistently receives no reliable priority. What receives no priority ties up fewer specialised resources. What is monitored with limited resources appears in the statistics as a small area of crime. The statistics then confirm the low level of political urgency, even though they may also be the result of weak recording.
The division of responsibilities reinforces this pattern. Environmental authorities, police forces, public prosecutors and specialist agencies work with different tasks, data sets and assessment criteria. For an individual authority, an offence may be considered processed once an administrative procedure has been completed or a permit has been reviewed. For the state as a whole, however, it remains unclear whether the damage was identified, stopped, remedied and assessed under criminal law. The implementation architecture too often ends at the interfaces.
Canada as a Countermodel
Elements of Canada’s federal enforcement model show that risk-based monitoring and enforcement can be organised systematically. Federal compliance and enforcement functions involving Environment and Climate Change Canada and Fisheries and Oceans Canada operate alongside provincial and territorial authorities under different legal frameworks. Risks are recorded, inspections are prioritised and enforcement is organised as a distinct state function. The qualitative difference is not that Canada detects every environmental offence. It is that parts of the state can align limited resources more systematically with risk and impact.
This is not evidence that a Canadian administrative structure could be transferred directly. Germany has different responsibilities, powers held by the Länder and legal procedures. The comparison does show, however, that environmental enforcement can be understood as a system that can be managed. It need not stop at the number of complaints received. It can ask which offences cause the greatest ecological or economic damage, where inspections are lacking and how long a case takes to reach a decision.
The German structure, by contrast, creates weak incentives for precisely this kind of management. Authorities are organised around procedures, responsibilities and available positions, not around nationally comparable measurements of impact. A small, formally completed case is more visible within an organisation than a large, complex damage case whose proof takes months or years. Without a shared database and clear priorities, speed becomes a random product of local capacity.
Germany measures environmental crime, but does not yet measure its impact consistently across Länder and authorities. That is the cool conclusion of the diagnosis: the state has created a legal claim, but no continuous architecture that reliably turns this claim into control and sanction. The low number of recorded cases is therefore not sufficient evidence that the problem is small. It is also an indication of a system that does not reliably know its own performance.
Bauplan
The next step would be a German environmental enforcement index. It would not need to compress the complexity of reality into a single figure. It would first need to establish a common basis for measurement. In a similar way to a corruption perception index, it could make visible how environmental crime is recorded, monitored and prosecuted. Only indicators that are actually collected and can be made comparable across Länder or authorities would be useful: for example, registered offence categories, inspection density, the scale of damage, case duration and the proportion of cases pursued from detection through to sanction. Where data is missing, the index would have to identify precisely that gap.
On this basis, resources could be allocated according to the scale of damage. Not every case requires the same level of investigation. A common risk framework could distinguish between a violation limited to a local area and one that causes lasting damage to waterways, soils, species populations or public budgets. Priorities would have to be professionally justified, reviewed regularly and coordinated between environmental authorities, police and public prosecutors. This would not automatically create more money. The available funds would first be used where their impact is greatest.
The central condition is a binding responsibility for data and prioritisation. Without an agency responsible for setting definitions, checking data quality and publishing results, the index would become another reporting requirement. The pitfall is equally clear: an indicator can easily become an administrative target and then displace the actual impact of the damage. The index would therefore have to combine several dimensions and allow for qualitative review.
Elements of Canada’s federal enforcement model show that combining risk, monitoring and enforcement can be organised systematically. For Germany, the Bauplan would not be the import of a foreign agency, but the translation of a functioning principle into the federal system: a shared operating picture, clear priorities, transparent allocation of resources and feedback on impact. That is how environmental law would become enforcement.
The diagnosis of this mechanism belongs in Band 1 “Freistaat”. The volume describes why state authority is decided not by the resolution, but by its implementation.