As alluded to above, green criminology has emerged as a fertile area of study bringing together a wide range of research interests and theoretical orientations (see, e.g., Beirne and South 2007; Brisman 2014b; Sollund 2008; South 2014; White 2010a). It has not been and is not intended to be a unitary enterprise. Diversity is one of its great strengths and it is most helpfully seen as a capacious and evolving perspective (see, e.g., South 1998: 212–213; see also White 2008: 14)—a loose framework or set of intellectual, empirical and political orientations toward problems (crimes, harms and offences related to the environment, different species and the planet). Importantly, it is also an ‘open’ perspective and framework, arising from within the tradition(s) of critical criminology; at the same time, it actively seeks inter- and multi-disciplinary engagement. It is both a network of interested individuals and a forum for sharing and debating ideas. Green criminology is thus invitational, to borrow from cultural criminology’s self-description (Ferrell, Hayward and Young 2008).
Green criminology remains fluid and full of potential to link with other (both established and growing) areas within criminology (e.g., Agnew 2012; this volume, Chapter 2; Altopiedi 2019; Brisman 2014b, 2017a, 2018; Ferrell, this volume, Chapter 37). It also seeks to forge connections across the humanities, social sciences and natural sciences (e.g., Brisman 2011; Lynch and Stretesky 2011, 2014: 29–49). The ‘naming’ of the field has occasionally attracted debate and alternatives include ‘environmental criminology’, which White (2008) has argued could be reclaimed from what is more properly considered ‘place-based criminology’, to cover the study of environmental harms and threats, environmental legislation and related research activity. This usage is an obvious reflection of the way that the word ‘environment’ is frequently employed in everyday discussion and contemporary media but suffers the drawback of being too easily confused with its longer established usage in criminology to describe relationships between the incidence of crime and the spatial features of the built and urban environment.1 Without expressly abandoning this endeavour, White (2010b: 6) has also offered the term ‘eco-global criminology’ to
refer to a criminological approach that is informed by ecological considerations and by a critical analysis that is worldwide in its scale and perspective … one that expresses a concern that there be an inclusive definition of harm, and … a multidisciplinary approach … to the study of environmental harm.
In a related vein, Walters (2010a: 180) has suggested that the term ‘eco-crime’ is helpful and capable of ‘encapsulat[ing] existing legal definitions of environmental crime, as well as sociological analyses of those environmental harms not necessarily specified by law’. Other formulations include ‘conservation criminology’ (Gibbs et al. 2010; Herbig and Joubert 2006). It seems, however, that criminologists most frequently employ the term ‘green criminology’ to describe the study of ecological, environmental or green crime or harm, and related matters of speciesism and of environmental (in)justice. Even so, as Goyes and South (2017: 178) argue, while the term and concept are very useful, their true value lies in drawing attention to concerns about the health and future of our environments and planet.2
Putting aside various names and nuances, all these terms represent similar frameworks and share a common interest in the bio-physical and socio-economic consequences of different sources of threat and damage to the environment, whether biodiversity loss, climate change, pollution or resource degradation. Whatever the descriptor—and ignoring questions of aetiology and different levels of individual, micro and macro analysis (which we touch on later in this chapter)—there is agreement on the need for research and debate on matters such as: pollution and its causes, consequences and control; corporate criminality and its impact on the environment; health and safety in the workplace where breaches have environmentally damaging consequences; involvement of organised crime and official corruption in the illegal disposal of toxic waste; the impact and legacy of law enforcement and military operations on landscapes, water supply, air quality and living organisms populating these areas—human, animal and plant; and the potential and scope of criminal law to prevent environmental despoliation and punish perpetrators of harm.
It is important to recognise that the way we identify and organize clusters of issues and problems can influence research agendas, policy priorities and methodologies (White 2010c: 415; see also Heckenberg and White, this volume, Chapter 6), and some simple but useful typologies can assist us in thinking about how to present the research directions and challenges relevant to green criminology (Lynch et al. 2017: 8–12). One typology derives from a distinction between ‘primary’ and ‘secondary’ green crimes (Carrabine et al. 2004) and has been developed further by Potter (2014). This is a straightforward but suggestive way of differentiating clusters of harms and crimes by classifying some as resulting directly from the destruction and degradation of the Earth’s resources, and others as those crimes or harms that are symbiotic with or dependent upon such destruction and efforts made to regulate or prevent it.
Purely as an illustrative exercise, we can identify four ‘primary’ green crimes in which the environment and species other than humans are damaged, degraded or harmed by human actions—all of which, to add a positive note, have become the subject of some national and international legislative efforts to protect and intervene in recent years:
1. Crimes of air pollution | 2. Crimes of deforestation |
3. Crimes against animals | 4. Crimes of water pollution |
‘Secondary’ or ‘symbiotic’ green harms and crimes can arise from the exploitation of conditions that follow environmental damage or crisis (e.g., illegal markets for food, medicine, water) and/or from the violation of rules that attempt to regulate environmental harm and to respond to disaster. These can include numerous major and minor practices whereby states violate their own regulations (either by commission or omission) and, in so doing, contribute to environmental harms. Potter (2014: 11) takes this approach to a ‘tertiary’ level to add discussion of ‘green crimes’ that may be defined as those ‘committed by environmental victims or as a result of environmental victimization … [e.g.] committed as a deliberate or direct response to environmental harm … [or] exacerbated by the experience of environmental victimisation’, which might include: (1) crimes committed by those forced to migrate in response to environmental harms (e.g., Brisman 2019; Brisman, South and Walters 2018, this volume, Chapter 10; Hall and Farrall 2013); (2) increasing crime rates as environmental harm and changing environments (including access to natural resources) impact social and economic conditions that relate to crime (e.g. Agnew 2012); and (3) crimes relating to exposure to environmental pollutants, such as lead or other heavy metals, which can have behavioural effects (e.g., aggression, learning difficulties) that some criminological theories posit as causes of crime (see, e.g., Lynch and Stretesky 2014: 103–21; Muller, Sampson and Winter 2018; Sampson and Winter 2018).3
A different threefold typology is offered by White (2008: 98–99) in which ‘brown’ issues are defined in terms of urban life and pollution—air pollution, disposal of toxic/hazardous waste, oil spills, pesticides, pollution of beaches and water catchments, stormwater pollution; ‘green’ issues refer to conservation matters and ‘wilderness’ areas (e.g., acid rain, biodiversity loss, habitat destruction, invasive species introduced via human transport, logging practices, ozone depletion, toxic algae and water pollution); and ‘white’ issues include the impact of new technologies and various laboratory practices (e.g., animal testing and experimentation; cloning of human tissue; environmentally related communicable diseases; food irradiation; genetically modified organisms; in-vitro processes; and pathological indoor environments).
Rather than promote a particular categorisation or typology, we instead rehearse the substantive topics and themes addressed by the breadth of scholarship in green criminology, including harms to the environment, to humans and to animals. The following section considers theoretical developments and frameworks in green criminology. We end with some observations about future work.