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Criminal Justice > Criminology Theories > Green Criminology > Green Criminology and Public Policy

Green Criminology and Public Policy




Green criminology and public policy intersect wherever research on environmental harm translates into concrete proposals for regulatory reform, sentencing practice, corporate accountability mechanisms, and international cooperation, marking the field’s evolution from a primarily descriptive and theoretical enterprise toward one increasingly engaged with prescriptive questions of institutional design. This policy orientation has grown substantially as the field has matured, moving beyond documenting environmental harm and its distribution toward more sustained engagement with what specific legal, regulatory, and institutional changes might most effectively reduce that harm going forward. The discussion that follows examines green criminology’s policy turn, approaches to strengthening criminal enforcement and corporate accountability, situational and preventive strategies, environmental justice considerations in policy design, and international policy coordination, closing with a synthesis of future directions for the field.

Introduction

Green criminology’s early development prioritized establishing the field’s conceptual foundations, including its harm-based definitional approach and its extension of victim status to ecosystems and nonhuman animals, over sustained engagement with specific policy prescription. Michael Lynch, Michael Long, Paul Stretesky, and Kimberly Barrett’s comprehensive treatment of green criminology traces how this balance has shifted considerably as the field has accumulated a substantial empirical base documenting environmental harm’s causes and distribution, providing the evidentiary foundation necessary for more confident policy recommendation than the field’s earlier, more exploratory period could support (Lynch, Long, Stretesky, & Barrett, 2017).

This policy engagement spans the full range of environmental crime categories green criminology addresses, from corporate pollution and hazardous waste enforcement to wildlife trafficking, climate change, and environmental justice, though the specific policy mechanisms most relevant to each category vary considerably given the differing regulatory, economic, and institutional contexts in which each type of environmental harm occurs.




From Description to Prescription: Green Criminology’s Policy Turn

Green criminology’s foundational harm-based framework, distinguishing the field from criminology’s conventional focus on formally illegal conduct, initially served primarily analytical rather than prescriptive purposes, expanding what counted as criminologically significant without necessarily specifying what legal or regulatory changes should follow from that expanded analytical scope. Rob White’s extensive scholarship across multiple green criminology domains has increasingly emphasized translating this harm-based analysis into concrete policy engagement, arguing that a field capable of identifying environmental harm bears some responsibility for engaging seriously with how that harm might be reduced rather than treating documentation alone as a sufficient scholarly contribution (White, 2013).

This policy turn has generated methodological as well as substantive shifts within green criminology scholarship, with increasing attention to program evaluation, comparative institutional analysis, and other methods better suited to assessing specific policy interventions than the more purely descriptive and theoretical methods that characterized the field’s earlier development. Andrew Lemieux and Ronald Clarke’s situational analysis of ivory trade bans exemplifies this methodological shift, applying rigorous empirical evaluation to a specific policy intervention rather than remaining at the level of general theoretical argument regarding wildlife trafficking’s causes (Lemieux & Clarke, 2009).

Academic and policy audiences for green criminology scholarship have expanded correspondingly, with increasing engagement from environmental agencies, international organizations, and legislative bodies seeking evidence-based guidance for environmental crime policy, a development that has itself shaped subsequent scholarship toward questions more directly relevant to active policy debates rather than purely academic theoretical concerns.

Strengthening Criminal Enforcement and Corporate Accountability

Persistent scholarly attention to the gap between documented corporate environmental violation and comparatively rare criminal prosecution has generated several recurring policy recommendations, including expanded individual officer liability provisions intended to overcome the diffusion of responsibility that has historically insulated corporate decision-makers from personal criminal accountability for organizational environmental offending. David Uhlmann’s scholarship on prosecuting environmental crime has argued that meaningful deterrence requires sanctions capable of affecting the individual decision-makers whose choices actually determine corporate compliance behavior, since organizational fines alone, however substantial, may be insufficiently connected to the specific individuals responsible for violation decisions to generate meaningful deterrent effect (Uhlmann, 2009).

Sentencing reform proposals have similarly focused on better calibrating environmental crime penalties to actual harm severity, addressing the mismatch between conventional sentencing guideline calculations and the diffuse, long-latency harm characteristic of many environmental offenses that Mark O’Hear’s sentencing scholarship has documented as poorly captured by guideline frameworks developed primarily for more immediately quantifiable offense categories (O’Hear, 2004). Proposals in this domain have included expanded consideration of long-term ecological and community health consequences in sentencing calculations, moving beyond the volume-based metrics that have historically dominated environmental sentencing guideline structures.

Regulatory reform proposals addressing the civil-criminal enforcement balance documented across multiple environmental crime categories have called for clearer statutory guidance regarding when criminal rather than civil enforcement is appropriate, seeking to reduce the substantial prosecutorial discretion that critics argue has historically channeled corporate environmental offending toward civil resolution regardless of underlying violation severity. Vincenzo Ruggiero and Nigel South’s analysis of green criminology and crimes of the economy has argued that this civil-criminal balance question ultimately implicates broader political economy questions regarding how seriously legal systems are willing to treat corporate environmental harm relative to comparable harm caused by individual offenders (Ruggiero & South, 2013).

Situational and Preventive Approaches to Environmental Crime

Situational crime prevention approaches, emphasizing opportunity-structure reduction over deterrence-based enforcement alone, have gained increasing policy traction across several environmental crime categories, particularly wildlife trafficking and illegal fishing, where the vast geographic scope of relevant activity limits conventional enforcement’s practical reach. Gohar Petrossian’s situational analysis of illegal fishing has demonstrated how this approach translates into specific policy mechanisms, including port state measures and market-based verification requirements that shift enforcement leverage toward points in the supply chain where monitoring is more practically feasible than at the point of initial violation (Petrossian, 2015).

Market-based and demand-reduction interventions, complementing conventional supply-side enforcement, have received particular attention within wildlife trafficking and illegal logging policy discussions, reflecting recognition that persistent demand in end markets will continue generating trafficking pressure regardless of enforcement intensity at the point of poaching or harvest. Andrew Lemieux and Ronald Clarke’s evaluation of ivory trade bans found that demand-side interventions could meaningfully reduce trafficking pressure when implemented with sufficient consistency, though the finding proved sensitive to enforcement gaps across the range of countries where the affected species populations are found, underscoring that demand reduction alone cannot substitute for coordinated supply-side enforcement (Lemieux & Clarke, 2009).

Import-side verification requirements, exemplified by the Lacey Act’s timber provisions governing illegal logging, represent a particular category of preventive policy innovation that shifts compliance burden toward downstream purchasers rather than relying exclusively on producing-country enforcement capacity that may remain limited for the foreseeable future regardless of international capacity-building investment.

Environmental Justice and Policy Design

Policy proposals addressing the environmental justice disparities documented in research on race, class, and environmental crime have increasingly emphasized cumulative impact assessment requirements, mandating that permitting decisions account for the total environmental burden a community already bears rather than evaluating each proposed facility in isolation from existing nearby sources of environmental risk. Robert Bullard’s foundational environmental justice research has informed subsequent policy proposals arguing that facility-by-facility permitting review systematically understates cumulative community risk in areas already hosting multiple hazardous facilities, a pattern this policy approach specifically targets (Bullard, 1990).

Community participation requirements, giving affected residents meaningful voice in permitting and enforcement decisions rather than merely nominal notification, have emerged as a further environmental justice policy priority, reflecting the procedural justice concerns David Pellow’s environmental justice scholarship has argued are equally significant alongside the distributive justice concerns that dominated the field’s earlier policy discussions (Pellow, 2007). Effective implementation of these participation requirements has proven uneven across jurisdictions, with some treating community input as substantively binding on permitting decisions and others treating it as a procedural formality without meaningful consequence for the ultimate outcome.

Enforcement equity monitoring, tracking whether inspection frequency and penalty severity vary systematically across communities with differing demographic composition, has been proposed as a mechanism for identifying and correcting the enforcement disparities Michael Lynch and Paul Stretesky’s quantitative research has documented across multiple environmental crime categories, providing an evidentiary basis for targeted enforcement reform beyond what facility-level compliance data alone would reveal (Lynch & Stretesky, 2003).

International Policy Coordination and Future Directions

International policy coordination, addressing the transboundary dimensions of environmental crime, has increasingly emphasized capacity-building investment in nations facing the greatest resource constraints, reflecting recognition that sustainable improvement in global environmental crime enforcement requires addressing underlying capacity gaps rather than relying exclusively on case-by-case international cooperation for individual enforcement actions. Lorraine Elliott’s scholarship on transnational environmental crime has argued that this capacity-building approach, while resource-intensive, offers more durable enforcement improvement than repeated ad hoc international cooperation on individual cases without addressing the underlying institutional capacity gaps that enable continued offending (Elliott, 2012).

Climate policy represents an increasingly significant intersection between green criminology and public policy, given the field’s growing engagement with questions of state and corporate responsibility for greenhouse gas emissions. Ronald Kramer’s state-corporate crime framework applied to climate change has informed policy proposals extending beyond conventional environmental regulation toward more direct corporate accountability mechanisms for climate harm, including expanded climate litigation theories seeking to establish liability for documented corporate knowledge of climate risk predating public disclosure (Kramer, 2013).

Future directions for green criminology’s policy engagement will likely continue expanding alongside the field’s growing empirical base, with particular growth anticipated in climate policy given the phenomenon’s escalating documented consequences, in biotechnology and food system regulation given the novel policy questions genetic modification and food system consolidation continue to raise, and in the ongoing development of situational and market-based prevention strategies as complements to conventional criminal enforcement across the full range of environmental crime categories the field addresses.

Sustained scholarly engagement with policy implementation and evaluation, rather than policy recommendation alone, represents perhaps the most significant methodological development likely to shape green criminology’s continued evolution, as the field’s accumulated empirical base increasingly supports rigorous assessment of which policy interventions actually achieve their intended harm-reduction goals rather than relying on theoretical plausibility alone to justify specific policy proposals.

Conclusion

Green criminology and public policy together represent the field’s maturing engagement with prescriptive questions of institutional design, building on decades of accumulated empirical and theoretical development spanning environmental harm, corporate and state offending, and environmental justice. The policy directions examined throughout this discussion, spanning enforcement reform, situational prevention, environmental justice policy design, and international coordination, reflect the field’s growing confidence in translating harm documentation into concrete institutional recommendation.

Green criminology’s development, from its theoretical foundations through the specific environmental crime categories and enforcement mechanisms scholars have examined across the field’s growing literature, ultimately converges on the policy questions this discussion has addressed, since documenting environmental harm gains its fullest significance when connected to sustained engagement with how that harm might be reduced. Continued development of green criminology’s policy orientation, informed by rigorous empirical evaluation of specific interventions, remains essential to the field’s ongoing contribution to reducing the environmental harm its scholarship has so extensively documented.

Related Articles

  • Environmental Harm and Green Criminology
  • Environmental Law and Criminal Justice
  • International Environmental Crime
  • Environmental Justice in America
  • Climate Change and Green Criminology

References and Further Reading

  1. Bullard, R. D. (1990). Dumping in Dixie: Race, class, and environmental quality. Westview Press.
  2. Burns, R. G., Lynch, M. J., & Stretesky, P. B. (2008). Environmental law, crime, and justice. LFB Scholarly Publishing.
  3. Elliott, L. (2007). Transnational environmental crime in the Asia Pacific: An “un(der)securitized” security problem? The Pacific Review, 20(4), 499–522.
  4. Elliott, L. (2012). Fighting transnational environmental crime. Journal of International Affairs, 66(1), 87–104.
  5. Faure, M. G. (2017). The revolution in environmental criminal law in Europe. Virginia Environmental Law Journal, 35(3), 321–356.
  6. Kramer, R. C. (2013). Carbon in the atmosphere and power in America: Climate change as state-corporate crime. Journal of Crime and Justice, 36(2), 153–170.
  7. Lemieux, A. M., & Clarke, R. V. (2009). The international ban on ivory sales and its effects on elephant poaching in Africa. British Journal of Criminology, 49(4), 451–471.
  8. Lynch, M. J., Long, M. A., Stretesky, P. B., & Barrett, K. L. (2017). Green criminology: Crime, justice, and the environment. University of California Press.
  9. Lynch, M. J., & Stretesky, P. B. (2003). The meaning of green: Contrasting criminological perspectives. Theoretical Criminology, 7(2), 217–238.
  10. O’Hear, M. M. (2004). Sentencing the green-collar offender: Punishment, culpability, and environmental crime. Journal of Criminal Law and Criminology, 95(1), 133–276.
  11. Pellow, D. N. (2007). Resisting global toxics: Transnational movements for environmental justice. MIT Press.
  12. Petrossian, G. A. (2015). Preventing illegal, unreported and unregulated (IUU) fishing: A situational approach. Biological Conservation, 189, 39–48.
  13. Pink, G., & White, R. (Eds.). (2016). Environmental crime and collaborative state intervention. Palgrave Macmillan.
  14. Ruggiero, V., & South, N. (2013). Green criminology and crimes of the economy: Theory, research and praxis. Critical Criminology, 21(3), 359–373.
  15. Stretesky, P. B., Long, M. A., & Lynch, M. J. (2013). The treadmill of crime: Political economy and green criminology. Routledge.
  16. Uhlmann, D. M. (2009). Prosecuting crimes against the earth. Trends in Organized Crime, 12(2), 130–140.
  17. Uhlmann, D. M. (2011). After the spill is gone: The Gulf of Mexico, environmental crime, and the criminal law. Michigan Law Review, 109(8), 1413–1442.
  18. White, R. (2011). Transnational environmental crime: Toward an eco-global criminology. Routledge.
  19. White, R. (2013). Environmental harm: An eco-justice perspective. Policy Press.
  20. White, R. (2018). Climate change criminology. Bristol University Press.




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