Conceptual framework for balancing society and nature in net-zero energy transitions

Gemma Delafield, Caspar Donnison, Philippa Roddis, Theodoros Arvanitopoulos, Alexandros Sfyridis, Sebastian Dunnett, Thomas Ball,  Kathryn G. Logan 

Abstract

Transitioning to a low carbon energy future is essential to meet the Paris Agreement targets and Sustainable Development Goals (SDGs). To understand how societies can undertake this transition, energy models have been developed to explore future energy scenarios. These models often focus on the techno-economic aspects of the transition and overlook the long-term implications on both society and the natural environment. Without a holistic approach, it is impossible to evaluate the trade-offs, as well as the co-benefits, between decarbonisation and other policy goals. This paper presents the Energy Scenario Evaluation (ESE) framework which can be used to assess the impact of energy scenarios on society and the natural environment. This conceptual framework utilises interdisciplinary qualitative and quantitative methods to determine whether an energy scenario is likely to lead to a publicly acceptable and sustainable energy transition. Using the SDGs, this paper illustrates how energy transitions are interconnected with human development and the importance of incorporating environmental and socio-economic data into energy models to design energy scenarios which meet other policy priorities. We discuss a variety of research methods which can be used to evaluate spatial, environmental, and social impacts of energy transitions. By showcasing where these impacts will be experienced, the ESE framework can be used to facilitate engagement and decision-making between policymakers and local communities, those who will be directly affected by energy transitions. Outputs of the ESE framework can therefore perform an important role in shaping feasible and energy transitions which meet the Paris Agreement targets and SDGs.

1. Introduction

In 2015, the Paris Agreement and the 2030 Agenda for Sustainable Development set transformative implications for global development and sustainability (Gomez-Echeverri, 2018Castor et al., 2020). The Paris Agreement aims to keep global temperature rise this century below 2 °C above pre-industrial levels and to pursue efforts to limit this temperature increase to 1.5 °C (UNFCCC, 2015). A target of 1.5 °C will only be achieved if significant reductions of greenhouse gas (GHG) emissions are made, which implies a worldwide transition to net-zero by the mid-century (Rogelj et al., 2015). Simultaneously the 2030 Agenda introduced 17 Sustainable Development Goals (SDGs), with 169 sub-targets relating to global challenges including: climate change, environmental degradation, biodiversity loss, justice, poverty and inequality (Banister, 2019Cadez et al., 2018Küfeoğlu and Khah Kok Hong, 2020Yildiz, 2019). Together these frameworks provide a blueprint towards a sustainable, low-carbon and more equitable world.

Both the Paris Agreement and SDGs acknowledge the criticality of developing sustainable energy systems to address the environmental, economic and societal challenges of climate change (Phillis et al., 2020). Energy systems are intrinsically linked to the natural environment and human wellbeing: it is therefore imperative that decarbonisation is not tackled in isolation (Fuso Nerini et al., 2018). For example, if siloed thinking prevails, we could witness the adoption of energy scenarios that achieve net-zero targets but lead to the loss of threatened plant and animal species, or which generate or widen existing inequalities in society (Holland et al., 2019Sovacool et al., 2015). To avoid the unintended consequences of siloed policymaking, it is imperative that decision-makers adopt a more holistic approach to energy transitions in the coming decades.

In this paper, we present the Energy Scenario Evaluation (ESE) framework which has been developed to assist policymakers and researchers in evaluating the sustainability and public acceptability of energy scenarios. The framework uses a mixed method approach to evaluate energy scenarios based upon criteria which have been developed from the SDGs. We aim to demonstrate how an interdisciplinary approach can be used to support policymakers developing energy scenarios that consider a wider set of sustainability criteria. The framework can help stakeholders identify the opportunities and challenges in future energy scenarios, from a wide range of perspectives. In addition, the framework can be used to explore future avenues for incorporating environmental and socio-economic data into energy models to support the creation of energy scenarios which are reflective of a broad range of impacts.

No other framework exists which combines multiple quantitative and qualitative methods to evaluate energy scenarios against public acceptance and sustainability criteria. Such a framework is needed to explore the wider context of energy scenarios, which are produced by energy models that typically focus on techno-economic factors (Jebaraj and Iniyan, 2006Strachan et al., 2009). Energy models have been influenced by a limited number of SDGs such as: economic growth (SDG 8), industrialisation (SDG 9), climate action (SDG 13), and foreign investment (SDG 17) (e.g. Daly and Fais, 2014). Other environmental, social and political considerations of energy systems are often overlooked (Schuitema and Sintov, 2017Thormeyer et al., 2020). Only a limited number of studies have explored the trade-offs and opportunities that exist between the SDGs and decarbonising energy systems (e.g. Fuso Nerini et al., 2018). The majority of existing energy models have not been designed to engage with the high temporal and spatial nature of renewable energy generation (Pfenninger et al., 2014). As a result, energy scenarios do not consider spatially dependent factors such as land use requirements and environmental impact (Dockerty et al., 2014Bolton and Foxon, 2015Holland et al., 2018Thormeyer et al., 2020). In recent years, a limited number of studies have explored the role of high temporal and spatial resolution in energy modelling (e.g. Price et al., 2018Zeyringer et al., 2018Tröndle et al., 2020). It is clear however that coupling technological and socio-economic perspectives is necessary to identify technically feasible, financially viable, and socially equitable transition scenarios (Patrizio et al., 2020Hooper et al., 2018). Low-carbon energy transitions need to consider the trade-offs and complex interactions highlighted by the energy quadrilemma; the need to balance cost, the environment, energy security and job opportunities (Olabi, 2016).

1.1. What is a sustainable, publicly acceptable energy transition?

Energy scenarios are created to explore how countries may navigate the transition to a low-carbon energy system. For the purpose of this paper we define ‘energy transition’ as a fundamental and systematic change to the existing energy system (Parag and Janda, 2014Sovacool, 2016). An energy transition generally involves a transformation within the energy system, usually to a particular fuel source (i.e. from wood to coal), technology (i.e. internal combustion engines to electric) or prime mover (i.e. a device that converts energy into useful services) (Hirsh and Jones, 2014Miller et al., 2015Sovacool, 2016). Energy transitions are expected to have a considerable impact on the current energy system, with impacts and changes to the planning and operating paradigm, market structure and regulatory frameworks (Berjawi et al., 2021). The progress of this transition depends on multiple parameters and variables, including key stakeholders (including civil society groups, the media, local communities, political parties, and policymakers) and the circumstances that open up new paths and opportunities for change (Geels et al., 2017Kern and Rogge, 2016Sovacool, 2016). Globally, we are currently witnessing the next energy transition with the rapid expansion of renewable energy sources (IRENA, 2021), this transition will require a holistic and interdisciplinary approach to ensure this energy transition does not negatively impact society or the environment (Crnčec et al., 2021Mitrova and Melnikov, 2019).

Decarbonising our carbon intensive global energy system is of critical importance: it is currently considered unsustainable based on a wide range of social, economic, and environmental criteria (Riahi et al., 2011Grubler, 2012). To cover the wide range of impacts that an energy transition can have, we define sustainability in the broadest terms, those which are reflected in the 17 SDGs. We define a sustainable energy scenario as one that meets ‘the needs of the present without compromising the ability of future generations to meet their needs’ (World Commission on Environment and Development, 1987). We assume this is one which meets both economic, environmental and social objectives. As discussed by Moldan et al. (2012), although indicators can be used to determine whether sustainability targets are being met, it is difficult to define exactly what a sustainable future looks like. It is less whether an absolute value has been met, rather the notion that we are heading in the right direction (Moldan et al., 2012). This perspective is incorporated into the ESE framework to consider the complexity of what sustainability actually means.

When determining the feasibility of an energy scenario, policymakers should pay close attention to public attitudes around the transition to net-zero. A successful energy transition requires engagement with the public: the public often see things missed by experts, add legitimacy to the transition process, and have a democratic right to be involved in decision-making (Fiorino, 1990Szulecki, 2018). Public acceptance of an energy transition operates at different scales, with support at the broad socio-political level not necessarily translating to acceptance for a particular project at the community level, where factors including trust and justice are relevant (Wüstenhagen et al., 2007). For example, although support for wind farms in many countries is high at the national level, public acceptance at a local level is mixed (Rand and Hoen, 2017). Policymakers therefore need to be able to communicate appropriate information when they are engaging with the public.

Public support for an energy technology or project is not static but rather can grow or fall over time; the ‘social licence to operate’ (SLO) refers to the ongoing community and stakeholder acceptance of a particular technology or project (Prno, 2013). Key components of establishing a SLO include forming relationships with stakeholders, communicating impacts of the project with the local community, and addressing sustainability concerns (Prno, 2013). The ESE framework provides the opportunity to address these core elements of the SLO: whereby public attitudes and preferences can be integrated into the design of energy scenarios, and spatially resolved environmental and social outputs can be used to provide information to local communities, facilitating holistic decision-making. This approach should prevent the implementation of energy technology in ‘top-down’ or ‘place-blind’ ways, both of which are likely to provoke public opposition and failure to achieve a SLO (Goldthau, 2018Buck, 2018Burke and Stephens, 2018). Several recent studies have highlighted the importance of engaging with local communities and stakeholders during energy transitions to mitigate the risk of not achieving public backing or a SLO (Moffat et al., 2016Baumber, 2018Hurst et al., 2020Sovacool et al., 2019Roddis et al., 2018). The SDGs were designed not only for policymakers but also for engagement with the public, and to promote sustainability (United Nations, 2019). Energy system transitions which are designed to meet the SDGs, and where this connection is explicitly made, therefore presents the opportunity for clearer communication with the public, which could support public acceptance of energy system changes. Additionally, meeting the broad criteria of sustainability encapsulated by the SDGs will demonstrate sustainability in environmental, economic, and social terms. This too could be important for public acceptability, given public concern that there may be trade-offs between environmental sustainability and economic sustainability (Bain et al., 2019).

The SLO concept is related to and interconnected with that of energy justice. Energy justice is a conceptual framework which explores how the costs and benefits of an energy transitions are distributed amongst society and how stakeholders are engaged in the decision-making process (Boardman, 2013Bullard, 2005Heffron et al., 2015Heffron and McCauley, 2014Jenkins et al., 2016Jenkins et al., 2021Lee and Byrne, 2019Liddell and Morris, 2010Pastor et al., 2001Sovacool and Dworkin, 2015Walker, 2009Walker and Day, 2012). The ESE framework touches upon these elements of energy justice but does not, and cannot, fully cover the theory of energy justice. Instead, we argue that the ESE framework should be used alongside processes which are centred upon energy justice and can delve into the complex layers of the framework, such as the work of climate assemblies (Climate Assembly UK, 2020).

1.2. Evaluating energy transitions using mixed methods

Despite the increased use of qualitative research methods in exploring energy transitions, there remains a lack of studies which integrate these methods with the quantitative approaches traditionally used in energy systems models (Royston and Foulds, 2021). Current policymaking is still heavily influenced by the output of quantitative energy models, often overlooking the value of qualitative methods. This is despite the limitations of focusing purely on quantitative or qualitative methods having been well documented, with a mixed methods approach widely advocated to help expand our understanding of the phenomenon being studied (Lieber and Weisner, 2010Pluye and Hong, 2014Almalki, 2016). For example, economic and natural science modelling are unable to fully consider the complexities associated with public acceptability of integrating low-carbon energy infrastructure across different spatial scales. The ESE framework that we propose provides a range of mixed methods to holistically assess energy system transitions, identifying how they can achieve sustainability as set out across the SDGs, as well as public acceptance of these transitions. This approach will allow researchers and policymakers to identify and explore the trade-offs and co-benefits that exist within energy scenarios to transition the economy to net-zero emissions. The SDGs are used conceptually as a means to evaluate energy scenarios and communicate their potential impacts to both decision-makers and the general public.

This article is structured as follows: Section 2 provides the rationale of the ESE framework and is split into four sub sections. Section 2.1 provides an overview of the framework, Section 2.2 defines the evaluation criteria and Section 2.3 details how the framework can be used to evaluate energy scenarios. Section 2.4 explains how the outputs of the framework could be soft-linked to energy models to improve their consideration of environmental and social factors. Section 3 discusses the key strengths (Section 3.1) and challenges of using a mixed methods approach within the ESE framework (Section 3.2). Section 4 details the key conclusions of the paper and the need for the ESE framework for policymakers and decisionmakers.

2. The Energy Scenario Evaluation (ESE) framework

2.1. Overview of framework

The ESE framework has been developed to assist policymakers evaluate whether energy scenarios can be considered as likely to be sustainable and publicly acceptable based on a range of evaluation criteria informed by the SDGs. The framework aims to (i) identify the ways in which existing energy scenarios impact society and the natural environment; (ii) use quantitative and qualitative tools to measure and assess these impacts; (iii) show how environmental and socio-economic data can be integrated into energy models to generate energy scenarios; and (iv) support decision-makers to identify and shape energy scenarios that achieve public acceptance and sustainability as conceived through the SDGs.

The ESE framework provides a holistic appraisal of energy scenarios designed to meet climate change targets. By incorporating a variety of interdisciplinary methods, our framework provides an insight into how energy scenarios impact both society and the natural environment. The framework provides both an ex-post and ex-ante perspective on the development of energy scenarios (Fig. 1). Firstly, an ex-post perspective is used to explore whether an existing energy scenario would likely lead to a publicly acceptable and sustainable energy transition using a wide spectrum of evaluation criteria. An ex-ante approach is then used to identify how public acceptance and sustainability could be embedded within the energy systems models that generate the energy scenarios. This could, for example, include soft-linking the outputs of other interdisciplinary methods into energy systems models (Fig. 1). Various research methods could be applied within the ESE framework to evaluate energy scenarios; within Appendix Table A.1 we suggest various research approaches that could be particularly helpful.

Fig. 1
2.2. Evaluation criteria

The evaluation criteria proposed by the ESE framework spans multiple disciplines from the social sciences (e.g. geography, sociology, and economics) to the natural sciences (e.g. biology, ecology, and chemistry) and engineering. Fig. 2 shows how the criteria are directly linked to the SDGs, illustrating how energy transitions are interconnected to human development.1 As highlighted by previous studies however, there are multiple direct and indirect linkages between all 17 of the SDGs (Dawes, 2020Zhang et al., 2016Zhao et al., 2021). For example, Cernev and Fenner (2020) discussed that through the development of resilient infrastructure (SDG 9), enhancements can be made to water (SDG 6) and energy (SDG 7), leading to improvements in wellbeing (SDG 3), education (SDG 4), gender equality (SDG 5), sustainable cities (SDG 11), as well as improving economic growth (SDG 8). Therefore, it is important to have an awareness of the interactions and feedback between the SDGs as they can impact other SDGs either directly or indirectly (Zhang et al., 2016). Public acceptance is assumed to be based on an amalgamation of all of the evaluation criteria used in this study; with no one criteria able to define what it means to be publicly acceptable.

Fig. 2

Mapping the evaluation criteria helps to identify the opportunities and challenges present in energy transitions (Fuso Nerini et al., 2018). The methods proposed within this framework provide an insight into the geospatial issues associated with energy transitions. The deployment of new renewable energy technologies will result in land use change which will have implications for the sustainable management, conservation and protection of marine, coastal, freshwater and terrestrial ecosystems (SDG 6, 13–15). By exploring geospatial issues, the framework can improve policymakers’ understanding of how energy scenarios could impact biodiversity, food production, human health and wellbeing (SDG 2, 3, 15).

In addition to land use change, it is also important to consider the wider impacts of the energy transition on the economy. Using the energy transition to promote sustained, inclusive and sustainable economic growth (SDG 8) will influence other sectors including transport and industry. For example, if individuals transition away from relying on personal vehicles to using public transport, air quality could be improved and sustainable infrastructure developments supported, both of which can improve individual health and well-being (SDG 3, 11, 12). On the other hand, energy transitions may promote sustainable industrialisation and foster innovation through encouraging difficult to decarbonise economic sectors to adopt low carbon processes (SDG 9, 12).

2.3. Ex-post evaluation

To understand the public acceptance and sustainability implications of an energy scenario, the ESE framework sets out five questions key to the net-zero energy system transition, and the evaluation criteria and interdisciplinary methods which can be used to answer them. Fig. 3 shows how the five key questions are interconnected and the evaluation criteria used to answer each one. Appendix Table A.1 details all the methods suggested in this section. The five questions to evaluate an energy scenario are as follows:

  • 1.Where will new energy infrastructure be located?
  • 2.How will the natural environment be impacted?
  • 3.How will other energy-use sectors be affected?
  • 4.How will employment be impacted?
  • 5.Is the scenario likely to achieve public acceptance?
Fig. 3

The first question this framework addresses is the spatial distribution of new energy infrastructure. An energy scenario’s impact on the natural environment and society will be strongly dependent on the spatial context of its infrastructure (Calvert et al., 2013Howard et al., 2013). Multiple methods can be used to determine where energy infrastructure might be located including: spatial optimisation, predictive classification models, and inferential logistic regression (Delafield, unpublished; Donnison et al., 2020Dunnett et al., 2020). Comparing the outputs of different methods allows policymakers to explore the sensitivity of different methodological assumptions. Some proposed methods which determine where new energy infrastructure might be located also consider the second question: how will the natural environment be impacted? Various methods exist to assess the impact of energy infrastructure, and its associated land use change, on food production and a myriad of ecosystem services including: mitigation of flooding, recreation benefits, carbon sequestration, GHG emissions, visual impact and biodiversity benefits (Appendix Table A.1). Additional methods can be applied to explore specific environmental impacts in depth, for example viewshed analysis could be used to determine the visual impact of an energy scenario at a local level (Carver and Markieta, 2012Calvert et al., 2013Wen et al., 2018).

To further explore the sustainability implications of an energy scenario, it is important to consider how other sectors will be impacted. The energy supply sector and resultant installation of new energy infrastructure is not the only way an energy scenario impacts the environment, changes to sectors including transport and industry can do so too. For example, changes to the transport sector will affect both GHG emissions as well as air quality. Methods that include high spatial resolution are needed to explore how an energy scenario’s ratio of battery electric vehicles to conventionally fuelled vehicles will impact local air quality and consequently human health (Woodcock et al., 2009). Appendix Table A.1 details a data mining method which estimates the spatial distribution of traffic flows and subsequent air pollution at street (Sfyridis and Agnolucci, 2020Sfyridis and Agnolucci, 2021). At a national level, the GHG implications of changes to transport and industrial processes will have been estimated during the creation of the energy scenario. As these sectors have been classified as hard to decarbonise, this framework highlights the importance of exploring the accuracy of the emission reductions included in an energy scenario (Agnolucci and Arvanitopoulos, 2019). Appendix Table A.1 details the operating emissions and panel regression analysis methods which can be used to do this (Agnolucci and Arvanitopoulos, 2019Logan et al., 2020aLogan et al., 2020bLogan et al., 2020cLogan et al., 2021).

Another aspect of how energy scenarios can impact the environment, which is usually overlooked in national policies, relates to international impacts. The manufacturing, maintenance and development phases of energy infrastructure are often not fully accounted for in decision-making. This framework puts forward the application of life cycle analysis (LCA) to consider the full range of impacts caused by each stage, from raw material extraction, manufacturing to decommissioning (Chester and Horvath, 2009Helms et al., 2010Hawkins et al., 2012Lovett et al., 2015). This would interlink with on the ground assessments such as Environmental Impact Assessments (EIA) and Strategic Environmental Assessments (SEA) which seek to identify likely significant impacts on the environment from projects such as energy developments (Morrison-Saunders and Arts, 2004).

The impact of an energy transition on employment will also be important to both meeting SDG goals and supporting SLO of transitional energy technologies (Prno, 2013). A key societal impact of the transition to net-zero is the creation of new employment opportunities in various sectors, both through direct and indirect employment effects (Arvanitopoulos and Agnolucci, 2020IRENA, 2011Meyer and Sommer, 2014Cameron and Zwaan, 2015). Using econometric models, such as the one detailed in Appendix Table A.1, the framework can provide quantifiable evidence into how employment will be impacted by an energy scenario (Arvanitopoulos and Agnolucci, 2020).

In addition to employment, public attitudes and SLO of an energy technology will be shaped by engagement with local communities in the decision-making process, the cost of the transition, and how the benefits and costs of the transition are distributed amongst society (Rand and Hoen, 2017). Several studies highlight that energy transitions based on civic ownership of decentralised energy systems could have important implications for the energy democracy of that transition (Becker and Naumann, 2017Szulecki, 2018). Public support for an energy scenario will also be influenced by the cost of the energy transition, as the cost of electricity and fuel will impact the number of people facing fuel poverty, as well as perceived international social and environmental impacts (Bouzarovski and Simcock, 2017McCauley et al., 2019). How these impacts are distributed is also likely to influence the SLO of the energy transition (Prno, 2013). The ESE framework offers a range of methodological approaches to determining public acceptance of energy transitions. Decision-makers can measure the socio-political acceptance of an energy scenario using national scale surveys such as the UK Government’s Public Attitudes Tracker (Roddis et al., 2019). At the community scale, other means of measuring public attitudes will be needed, with public acceptance ‘in the abstract’ not necessarily translating to community acceptance ‘on the ground’ (Buck, 2018). For example, visual impact of wind turbines, closely connected to public attitudes, depends on factors such as how many people can see the turbines, the size of the turbines, the ‘naturalness’ of the surrounding landscape, and personal preferences (Devine‐Wright, 2005). This highlights the importance of a range of factors in public attitudes, and the role of spatial modelling as well as public attitude surveys methodologies.

There are a number of distinct forms of public engagement, referred to as ‘ecologies of participation’ by Chilvers et al. (2018), and mainstream approaches of societal engagement are often limited in their breadth. It is important to consider the interconnected nature of different collective participatory practices and how the public’s attitudes are multi-layered and subject to change over time. As a result of these insights, the ESE framework recommends the use of multiple methods to explore public attitudes and stresses that the outputs from this framework are used as a starting point for discussions with the general public through stakeholder engagement, rather than relying solely on top-down decision-making. The outputs could feed into a ‘balance sheet’ approach which has been recommended previously to collate, interrogate and present evidence in a pragmatic way (Turner, 2016). Multiple studies emphasise the importance of multi-scalar governance for energy transitions, in which there is scope for national energy scenarios to be translated into action at local and regional levels which are sensitive to context-specific circumstances (Turner, 2016Essletzbichler, 2012). The complexities of combining the outputs from multiple methods like this to be used in decision-making is explored in Section 3.2.

2.4. Ex-ante evaluation

By reflecting upon the outputs from the ex-post evaluation, this framework aims to identify ways in which the creation of energy scenarios could be improved. By soft-linking some of the methods in the framework with energy systems models, a wider range of impacts could be considered when creating energy scenarios. A soft-linking approach capitalises on the strengths of both methods by combining them using an iterative approach, this is preferential to a hard-linking approach which would require the full integration of both models (Krook-Riekkola et al., 2017). The soft-linking approach recommended could have repercussions on the variety of energy mixes proposed by the energy systems models.

Two soft-links are proposed for consideration by this framework. Firstly, hard restrictions on the amount of land that is available for different technologies could be included in energy systems models. The amount of land available could be calculated based upon what is deemed to be socially acceptable (e.g. excluding developments on National Parks or high-grade agricultural land). This would be particularly relevant for bioenergy as there are concerns that the level of land-use required to grow bioenergy crops suggested in some energy scenarios goes beyond what could be socially acceptable (Konadu et al., 2015). Secondly, the distribution of costs for energy technologies indicated by the spatial optimisation methods could be included in the energy systems models. Currently energy system models set costs based upon “today’s” cost and the expected trend in costs over time (Ellenbeck and Lilliestam, 2019). These cost assumptions contain a high level of uncertainty for multiple reasons. First, uncertainty is caused by not knowing how manufacturing costs will decrease over time due to technological advancements and economies of scale (Santos et al., 2016). Second, there is uncertainty around how the cost of energy development projects could be influenced by competition for land. So far developments have largely occurred on ‘low-hanging fruit’ locations, those which are low cost and where conflicts are minimal. However, as more infrastructure is deployed and competition for land increases, most notably in densely populated countries like the UK, energy technologies may have to be deployed to less cost-efficient land (Calvert and Mabee, 2015Coelho et al., 2012). By including insights from spatial optimisation models regarding how the cost may increase as less optimal locations have to be chosen, this second uncertainty could be reduced. In addition, the costs currently included in energy models only consider market costs (e.g. construction and grid connection costs), they overlook the wider environmental impacts that energy transitions could have including air quality, visual amenity, and soil carbon sequestration implications. A range of ecosystem service costs could therefore be incorporated into energy models to provide an insight into how the scale of renewable energy expansion could impact the natural environment. There are challenges associated with incorporating this type of data into energy models however, such concerns are discussed in Section 3.2.

3. Discussion

The ESE framework provides a holistic assessment of environmental and social impacts of energy scenarios across different spatial scales. As the framework is rooted to the SDGs (Fig. 2), it ensures that the evaluation of energy scenarios does not narrowly focus upon decarbonisation objectives, but instead provides a systematic method to identify and explore the trade-offs and co-benefits between energy goals and the SDG 2030 Agenda (Fuso Nerini et al., 2018). Far-reaching economy-wide change will be required to achieve net-zero transitions and this will be socially disruptive (Miller et al., 2013). A holistic approach to appraising and developing low carbon energy scenarios will be critical to ensuring that these transitions are sustainable and publicly acceptable. In providing this approach, our framework answers the call for the coupling of social and environmental priorities within energy modelling (Hooper et al., 2018). This framework highlights how sustainability and public acceptance should be seen as central, not simply complementary, to achieving net-zero emissions targets by mid-century.

3.1. Strengths of the ESE framework

The ESE framework is advantageous to policymakers because it can be used immediately in net-zero policymaking, alongside existing energy models, and does not require the construction of new models. Net-zero targets require decisive action in this decade and the ESE framework can be used to evaluate energy scenarios alongside the requirements of other policy goals. The methods recommended by this framework, including location-based assessments of the impact of renewable energy expansion, also allow policymakers to explore how trade-offs vary spatially: by using a mixture of methods, impacts at the local, national and global scale can be identified and explored. Using a similar framework which focussed on a subset of SDGs (SDGs 8–10), Patrizio et al. (2020) showed that the impact of energy policy can vary between country, with net-zero transitions leading to economic and employment loss in some countries and growth elsewhere. This sort of analysis can highlight where there may be resistance to energy transitions, and where policy support may be required. The ESE framework can also highlight how methods could be soft-linked to energy system models to broaden the set of impacts considered when creating energy scenarios. For example, the non-market costs of siting energy infrastructure, as estimated by environmental economic models, could be included into energy systems models.

Using a combination of quantitative and qualitative methods the ESE framework allows for a more thorough understanding of the level of public acceptance, taking account of spatial and temporal variations in public attitudes. This part of the framework can be used to support policymakers as they test appropriately for public acceptance at broad national levels, and at the community level, as well as establishing and maintaining a SLO for particular energy technologies and projects, which could help inform decision-making at the national, regional and local levels. ‘Community’ acceptance describes people’s responses to infrastructure at the local level and is not always consistent with the results from national scale surveys (Wüstenhagen et al., 2007Buck, 2018). Public acceptance at a local level can be influenced by factors such as employment and environmental impact (Healy and Barry, 2017). Roddis et al. (2019), for example, found that support for onshore wind was greater in areas where high levels of people were employed in relation to that technology. Social acceptance can be influenced by a wide range of factors including the perceived visual, noise and biodiversity impacts of the energy infrastructure as well as process-related issues such as the transparency and fairness of the decision-making process (Ellis and Ferraro, 2016). Rand and Hoen (2017) provide an extensive review of wind energy acceptance research highlighting how studies should not view opposition as something to overcome, instead suggesting that individual’s concerns should be listened to and not dismissed. They argue that societal acceptance has long been overlooked and it is imperative that socioeconomic impacts, sound and visual annoyance, distributional justice and fairness in the decision-making process are carefully considered. Although economic and natural science modelling can provide some insight into aspects which influence public acceptance like visual impact (e.g. how many people can see a wind farm, willingness to pay to increase the distance between wind turbines and human settlements), they are unable to fully consider the complexities associated with public acceptability of energy transitions across different spatial scales (e.g. the perceived ‘naturalness’ of the landscape, place attachment) (Devine‐Wright, 2005Rand and Hoen, 2017).

The ESE framework embeds the concepts of the SLO, highlighting the importance of engagement with communities, providing information on impacts of the project, addressing sustainability concerns, and building trust (Prno, 2013). Traditional energy modelling which optimises based on emissions and financial cost is not capable of addressing the requirements of achieving a SLO. Without considering these principles of the SLO, renewable energy projects are likely to face public backlash (Goldthau, 2018). The ESE framework can be used to bring stakeholders into the decision-making process, encouraging societal buy-in by ensuring all voices are listened to (Abram et al., 2020). The framework can provide spatially-explicit information for engagement with local decision-makers and communities to feed into stakeholder engagement activities. The framework promotes the use of qualitative research which can integrate citizen views, attitudes, and values when considering energy transitions. Qualitative research can provide further insights into energy transition discussions, addressing some of the gaps and limitations of quantitative research. Policy is more likely to achieve a SLO when citizens are brought into the decision-making process, shown during the recent climate assemblies in France and the UK (Capstick et al., 2020). These aspects of the framework answer the calls from the 2030 Agenda for greater justice in energy decision-making (Fuso Nerini et al., 2018) and from the Paris Agreement for a just transition to a low-carbon economy (UNFCCC, 2015).

An example of how the ESE framework could be utilised by policymakers is its potential application to the assessment of negative emission technologies (NETs) which are increasingly likely to be required to meet Paris Agreement targets (Rogelj et al., 2018). Whilst technical discussions of bioenergy carbon capture and storage (BECCS) are taking place in policy circles major social barriers to the technologies remain (Fuss et al., 2020Morrow et al., 2020) and stronger governance structures are called for to promote the SLO (O’Beirne et al., 2020). Trade-offs, as well as co-benefits, between the SDGs and NETs will be context and scale-dependent (Smith et al., 2019). The methodology put forward by our framework can provide holistic and spatially-explicit assessment of the impact of NETs, and employ qualitative research methods to address the existing limited public understanding of the technologies (Cox et al., 2020). Greater understanding of the location-specific impacts of NETs such as BECCS could facilitate public debate and the identification of most suitable locations, increasing the likelihood of achieving a SLO (Buck, 2018).

The ESE framework highlights the challenges and complexities of bringing environmental and societal considerations into energy and decarbonisation policies. Previous models have focused narrowly on evaluating energy scenarios principally upon two metrics: minimising GHG emissions and cost. Whereas identifying environmental and social impacts requires the inclusion of a range of methodologies and the use of a number of different criteria, which leads to disagreement over how best to evaluate these impacts simultaneously. Arguably, the most recent advances in the integration of environmental and social impacts into policymaking have been achieved through the ecosystem service framework, often using monetary valuation, allowing optimisation and clear outputs of policy scenarios (e.g Bateman et al., 2013). We argue that this approach will need to be complemented with more qualitative methodologies which account for winners and losers of particular scenarios if energy scenarios are likely to be sustainable, publicly acceptable and achieve SLO (Peng et al., 2021). Additionally, the ‘balance sheet’ approach recommended by the UK’s National Ecosystem Service Assessment may be a suitable complement to our framework (Turner, 2016Turner et al., 2014). By using mixed methods, the ESE framework is able to combine the strengths of quantitative and qualitative methods to deepen our understanding of how the energy transition will impact both society and nature (Hussein, 2009Pluye and Hong, 2014Lieber and Weisner, 2010). The ESE framework uses a critical interpretive synthesis approach, as defined by Pluye and Hong (2004), to extract concepts from both quantitative and qualitative studies, critically examine these concepts to identify similarities and differences. Although the process of using mixed methods is challenging, it allows researchers to recognise the multiple realities of looking at the same problem (Hussein, 2009).

3.2. Challenges associated with using mixed methods

Some studies have raised concerns with mixed methodologies of quantitative and qualitative research methods. There is a perception that mixing paradigms is problematic because the nuance and detail highlighted by the qualitative data may be lost when insights are drawn more generally (Lieber and Weisner, 2010Onwuegbuzie and Leech, 2005Eyisi, 2016). This is one of the reasons why the concept of energy justice has not been embedded directly within the ESE framework. The complexities of assessing energy scenarios in terms of energy justice remains challenging when the paradigm is fundamentally different to the positivist lens used in the ecosystem service approach (Roddis et al., 2018). In this paper, we argue that viewing the ESE framework in parallel to methods which explore energy justice, such as climate assemblies, would be more appropriate. One framework is unable to encapsulate all of the complexities involved in the energy justice paradigm, we would argue that it is possible that no singular framework should try.

A further challenge presented by using mixed research methods is the multiple outcomes that can be observed: corroboration (i.e. the same result), elaboration (i.e. qualitative data analysis exemplifies how the quantitative findings apply in particular cases), complementarity (i.e. results differ but together generate insights) and contradiction (i.e. conflicting results) (Brannen, 2005). When the outcomes of the methods are contradictory, this presents problems when trying to ensure meaningful results are created which can be clearly communicated to a variety of stakeholders (Lieber and Weisner, 2010). Using an interdisciplinary approach to shed light on a complex problem from multiple perspectives is challenging but this does not mean it should not be attempted (Beaumont, 2020). For example, the ESE framework suggests soft-linking the outputs of environmental economic models with energy system models to expand how the natural environment is considered in energy scenario creation. This presents a challenge however, as only certain environmental impacts can be quantified and monetised, and this monetisation provides only a partial value of the impacts (Pearce et al., 2013Dasgupta, 2021). It would therefore be essential that these insights were only viewed as part of the picture, alongside the insights provided by other methods.

We believe that the ESE framework offers the advantage of bringing together the outputs from multiple methods to allow researchers and policymakers to have discussions across traditional disciplinary boundaries to elaborate on findings, discover contradictions and explore the problem from different perspectives. As other studies have highlighted already, mixed methods can increase the credibility of scientific knowledge and perform an important role in informing policy (Hussein, 2009Pluye and Hong, 2014). The question of whether an energy scenario is likely to achieve public acceptance and sustainability is one that cannot be explored using one method or one paradigm, it is a question which needs different perspectives and understandings. We agree with the use of a ‘jigsaw of evidence’ (O’Sullivan and Howden-Chapman, 2017): bringing together multiple findings to create valuable policy relevant information.

4. Conclusions

A whole-systems approach is essential to assess how the transition to a low carbon energy system may impact the economy, environment, and society. A wide range of methodological approaches are required to ensure all aspects of the transition are covered, however, historically the differences in a mixed methods approach across disciplines has made this whole-system approach difficult to achieve. The need for interdisciplinary and transdisciplinary approaches has been recognised as vital to tackling the world’s current global environmental challenges, with the decarbonisation of energy systems one such challenge (Sovacool et al., 2015). The ESE framework outlined in this paper reflects the broad range of approaches that can be taken to evaluate energy scenarios in terms of their sustainability and public acceptability. In assessing how different methods can be used to complement each other, this paper has explored practical ways in which decision-makers can use multiple methods to evaluate transformative changes to an energy system.

As countries across the world transition to low carbon economies, new energy infrastructure will need to be constructed, and a strategy employing multiple research methods will be needed to achieve the objectives of the SDGs including: GHG reductions, low financial cost, environmental protection, job creation and public acceptance. This paper shows how multiple methods can be used together to improve integrated approaches for assessing energy scenarios considering impacts at different spatial scales. Overall, we propose the ESE framework can be used to support decision-makers evaluating the financial, environmental, political and social feasibility of energy scenarios, thereby contributing to the pursuit of realistic, deliverable and sustainable decarbonisation goals.

Appendix

See Appendix Table A.1.

Table A.1. Overview of suggested methods and how they apply to the framework.

MethodDescriptionFramework application*
Spatial optimisationThe ADVENT-NEV (Delafield et al., unpublished) and BECCS optimisation models (Donnison et al., 2020) use spatial optimisation techniques to identify the least cost locations for new solar farms, wind farms, bioenergy power stations and/or BECCS. These models optimise both market (e.g. construction and opportunity costs) and non-market costs (e.g. visual impact and carbon sequestration) to determine the financially or socially optimal spatial distribution of energy infrastructure.Image 1 Image 2
Random forestThe random forest potential (RFP) probability surfaces developed by (Dunnett et al., unpublished) identify where new solar and wind farms are most likely to be located in the future based upon existing locations of energy infrastructure and environmental impacts including biodiversity. The model was developed using existing locations of wind turbines and solar panels identified with OpenStreetMap in Dunnett et al. (2020).Image 1 Image 2
Inferential logistic regressionLogistic regression can be inferentially used to show where infrastructure is more or less likely to be accepted based upon historical planning acceptance (Roddis et al., 2018). Trends in planning acceptance is an indicator of how communities feel about energy developments and therefore can be analysed to consider how acceptable energy scenarios might be in terms of deployment ‘on the ground’.Image 1 Image 4
Regional box modelA regional box model is being developed to assess the location and quantity of land available for BECCS globally (Ball et al., unpublished). The model considers how the availability and suitability of land for BECCS is driven by a range of factors, including food system efficiency, dietary trends and sustainable governance. The model can determine the global sustainability implications of importing biomass from specific countries by combining metrics for environmental governance and political stability.Image 2
Viewshed analysisThe visual impact of an energy scenario can be assessed using viewshed analysis: a Geographic Information System technique which calculates the area (i.e. viewshed) where an object is visible, taking into account the height of the object and the intervening terrain (Carver and Markieta, 2012Wen et al., 2018). Viewshed analysis can be applied at local or national scales to estimate the visual impact of different low carbon energy scenarios.Image 2
Data mining and machine learning algorithmsBy estimating traffic flows for any given point on the road network, air pollution across the UK at a street level can follow. Sfyridis and Agnolucci (2020) have developed a model to estimate traffic volumes on a street segment level using a hybrid clustering-regression approach, while the follow up research by Sfyridis and Agnolucci (2021) determines the spatial distribution of GHGs and air pollutants using a probabilistic classification-regression model. The model estimates air pollution using assumptions from the COPERT model (Ntziachristos et al., 2009). Traffic flows are estimated using: traffic count points from the UK’s Department for Transport, the K-prototypes clustering algorithm, and random forests, OLS and support vector regression.Image 2
Panel regression analysisAgnolucci and Arvanitopoulos (2019) have developed a method to assess how emissions from the manufacturing sector have changed over time using panel regression analysis. This information can be used to check whether the elasticities estimated by Agnolucci and Arvanitopoulos (2019) and Agnolucci et al. (2017) can be used to calibrate the economic models that generate energy scenarios.Image 2 Image 3
OPerating Emissions ModelThe operating emissions model (OPEM) is a deterministic model developed to project operating emissions through a series of different conventionally fuelled vehicles and electric vehicles integration scenarios. Input data for this model can incorporate different energy scenarios. The OPEM is a simple model and easy to manipulate and comparable and is easier to use when comparing countries (Logan et al., 2020a, 2020b, 2020c, 2021).Image 2 Image 3
Life cycle analysis (LCA)LCA can provide an insight into the environmental implications of a shift to low-carbon electricity supply by considering the manufacturing and material life of energy technologies (Hertwich et al., 2015). Stamford and Azapagic (2014) provides an example of applying LCA to a UK energy scenario.Image 2
Vector Auto- regressive ModelAn empirical methodology, based on econometric methodology such as Vector Autoregressive Model (VAR), can be used to quantify the potential employment impact from the deployment of renewable energy technologies (Arvanitopoulos and Agnolucci, 2020). This method can, therefore, be used to estimate the expected number of jobs generated (or lost) related to a specific energy scenario.Image 5
Regression analysis of public attitudesA regression model using data from the UK Government’s Energy and Climate Change Public Attitudes Tracker (PAT) was developed to understand the drivers of positive and negative attitudes towards energy technologies (Roddis et al., 2019). The results of this regression model and other similar analyses of public attitudes could be used to gain insight into how different UK low carbon energy scenarios may be regarded by the public on a national scale.Image 4
Balance sheet approachThe Balance Sheet Approach (BSA) can be used to build an evidence base to support decision-making. The framework provides an approach to collect, analyse and present data which considers the distributional impacts of the costs and benefits of an intervention (Turner, 2016Turner et al., 2014).Image 4 Image 2 Image 5

* 

Image 1

 depicts methods which relate to where energy infrastructure will be located, 

Image 2

 relates to natural environment impacts, 

Image 3

 sectoral impacts, 

Image 4

 public opinion and 

Image 5

 employment.

References

The Anthropocene Divide: Obscuring Understanding of Social-Environmental Change

Andrew M. Bauer

 and 

Erle C. Ellis

Andrew M. Bauer is Assistant Professor in the Department of Anthropology at Stanford University (450 Serra Mall, Stanford, California 94305, USA [ambauer@stanford.edu]). Erle C. Ellis is Professor in the Department of Geography and Environmental Systems at the University of Maryland, Baltimore County (1000 Hilltop Circle, Baltimore, Maryland 21250, USA).

Abstract

Much scientific debate has focused on the timing and stratigraphic signatures for the Anthropocene. Here we review the Anthropocene in its original usage and as it has been imported by anthropology in light of evidence for long-term human-environment relationships. Strident debate about the Anthropocene’s chronological boundaries arises because its periodization forces an arbitrary break in what is a long-enduring process of human alterations of environments. More importantly, we argue that dividing geologic time based on a “step change” in the global significance of social-environmental processes contravenes the socially differentiated and diachronous character of human-environment relations. The consequences of human actions are not the coordinated synchronous product of a global humanity but rather result from heterogeneous activities rooted in situated sociopolitical contexts that are entangled with environmental transformations at multiple scales. Thus, the Anthropocene periodization, what we term the “Anthropocene divide,” obscures rather than clarifies understandings of human-environmental relationships.

Since the Anthropocene’s formulation by atmospheric chemist Paul Crutzen and ecologist Eugene Stoermer (2000) to recognize a new period of geologic time marking human transformations of Earth’s environmental systems, the designation has been taken up vociferously across the academy. From Earth scientists to literary critics, scholars now debate the usefulness of distinguishing an Anthropocene from the Holocene, the currently recognized geological epoch spanning the past 11,600 years since Earth’s last glaciation (e.g., Autin and Holbrook 2012; Braje 2016; Finney and Edwards 2016; Lewis and Maslin 2015; Waters et al. 2016a; Zalasiewicz et al. 2015). The implications of this designation have also been discussed as a framing concept for environmental governance (e.g., Biermann et al. 2016; Moore 2016; Purdy 2015; Ribot 2014) and as a way of disrupting the long-held distinction between natural history and human history (cf. Chakrabarty 2009; Malm and Hornborg 2014; Mikhail 2016). The Anthropocene is thus a potentially revolutionary concept—not just because it has become synonymous with the unprecedented global environmental impacts of humans but also because it implies an end to basic frameworks of science, society, and scholarship that have long guided Western intellectual thought (e.g., Latour 2004). As the philosopher of science Bruno Latour (2014) has noted, it subverts traditional conceptions of an external objective world devoid of humans, given that human “action is visible everywhere—in the construction of knowledge as well as in the production of the phenomena … sciences are called to register” (6, italics in the original). Such statements underscore the need to evaluate how we understand human social action in the context of an Earth transformed by humans, especially in relation to anthropological concerns for historical relationships among humans, other organisms, and the material processes and associated discourses that give shape to environments.

While the Anthropocene has rightly called attention to a suite of grave global environmental consequences related to human activities, the various emphases among scholars now using the designation have also reoriented the concept in multiple directions, many of which work at cross-purposes from each other. For instance, while some argue that the concept dissolves the great binary between society and nature—“the end of the division between people and nature” in the words of environmental historian Jedediah Purdy (2015:3; see also McKibben 1989)—others emphasize its binary foundations, stressing, for example, that humans are now “overwhelming the great forces of nature” (e.g., Steffen, Crutzen, and McNeill 2007). The Anthropocene has become a differential lens through which disciplines across the academy are reviewing, debating, and reinventing their conceptions of humanity and nature.

Below we address the Anthropocene concept from a perspective more directly related to its original framing—asking foremost how the concept and geological time period might both constrain and enable scholarly understandings of human-environment relationships. To do so, we review the term’s broader usage in light of archaeological and ecological evidence on long-term relationships among humans and the environments they both inhabit and produce.

Strident debate about where to place the Anthropocene’s chronological boundaries arises—with the mid-twentieth or late eighteenth century being the most commonly advocated among others (cf. Crutzen 2002; Lewis and Maslin 2015; Ruddiman 2013; Smith and Zeder 2013; Waters et al. 2016a; Zalasiewicz et al. 2015)—because the Anthropocene’s periodization forces scholars to apply an arbitrary break in what is a lengthy process of human modifications to both local and planetary environmental conditions. There should be no doubt that the magnitude of human influence on Earth’s environmental systems has intensified alarmingly since the Industrial Revolution and particularly since the 1950s (e.g., Steffen, Crutzen, and McNeill 2007; Waters et al. 2016a). Nevertheless, an Anthropocene periodization that begins at these points fundamentally obfuscates qualitative similarities and historical linkages with the dynamics of human-environmental relationships in previous periods (e.g., Boivin et al. 2016; Braje 2015; Braje and Erlandson 2013; Erlandson and Braje 2013; Kirch 2005; Moore 2015; Ruddiman et al. 2015; Smith and Zeder 2013). To understand the role of human activities in transforming Earth, it is essential that these not be conceived as a binary distinction—before versus after—but rather as a continuously changing process, which necessarily calls attention to a variety of differentiated actors and historical, cultural, political, and ecological contexts. The challenge of the Anthropocene proposal is not simply its formal division of geologic time but also the need to call attention to the entanglements through which social relationships, inequalities, and environmental histories are continually unfolding and producing novel Earth trajectories.

The Anthropocene(s)

To contribute usefully to the Anthropocene conversation, it is critical to differentiate what the designation has come to mean among the various academic fields that have taken it up. The Anthropocene’s multiple referents (e.g., as marker of anthropogenic stratigraphic materials, as period in which Earth’s climatic and environmental workings have been shaped by humans, as the end of the division between society and nature) have allowed it to be adopted with a variety of different emphases among scholars of the natural sciences, humanities, and social sciences. Ironically, many of these framings work at cross-purposes from one another, a point we stress in arguing that the Anthropocene divide obscures understandings of the long-term dynamics of human-environment relationships.

For many scholars of the humanities and social sciences, the Anthropocene stands in for a dark period of human-environment relationships associated with modernity and the outgrowth of the Eurocentric belief in the divide between nature and humanity that now “catastrophically affects the destinies of all—plant, animal, and human—through global warming and mass extinctions” (Carrithers, Bracken, and Emery 2011:663). Environmental historian Ian Miller (2013), for example, has specifically argued that the Anthropocene be considered coeval with the development of “ecological modernity.” Yet, by highlighting humans’ current roles in shaping planetary conditions, the Anthropocene has largely come to signify a period in which this great divide is now obsolete. In environmental imaginaries and historiographies, it is a period that is “after nature” (Purdy 2015:3). Thus, for many anthropologists it represents the dissolution of the long-standing modernist binary that has structured understandings of human social life in distinction from a separate natural world. The Anthropocene has also engaged anthropologists in critically evaluating how the natural sciences represent humans as a single entity—that is, the species (cf. Bauer and Bhan 2016; Carrithers, Bracken, and Emery 2011; Gibson and Venkateswar 2015). The emphasis on the human species as a “geophysical force” has allowed some scholars to raise foundational epistemological and ontological questions about the nature of history, historical subjects, and the world humans inhabit. For instance, by signaling a period of human-caused global environmental change, the Anthropocene has spurred a philosophical recognition of phenomena and objects (e.g., climate) that are beyond, or at least challenge, human perception and experience (e.g., Morton 2013). In this way, the Anthropocene has disrupted historiography in this new period and how the ontological relationships between subjects and objects, the constitution of social actors, and the mediation of perception and historical imagination are theorized (cf. Chakrabarty 2009; Latour 2014; Mikhail 2016; Morton 2013; see Bauer and Bhan 2018).

Among the natural sciences, the Anthropocene has come to more strictly reference a period during which humans now dominate the “great forces of nature” (Steffen, Crutzen, and McNeill 2007) or rather, as the environmental scientists William Ruddiman and colleagues (2015) have characterized it, when humans have “replaced nature as the dominant environmental force on Earth.” Earth system science (ESS) views Earth as a system of interacting “spheres”—the atmosphere, lithosphere, hydrosphere, and biosphere—and uses Earth system models to describe the long-term dynamics of Earth’s interacting physical, chemical, and biological processes (Schellnhuber 1999; Steffen, Crutzen, and McNeill 2007). By connecting human history with ESS, this work helped build a foundation for assessing the most critical scientific claim of the Anthropocene narrative: that human activities have substantially changed the functioning of the Earth system. While evidence of human alteration of local environments has long been widespread, the claim that humans are altering the functioning of Earth as a whole has now been confirmed by a wide array of observations, perhaps most prominently by long-term trends in atmospheric carbon dioxide and their coupling with human combustion of fossil fuels and other alterations of the global “biogeochemical” cycling of carbon that are causing global changes in climate. These global changes are now potentially forcing the Earth system to undergo an irreversible step change or regime shift (tipping point) from a Holocene-like climate state to an Anthropocene climate state (Steffen, Crutzen, and McNeill 2007; Steffen et al. 2016; Waters et al. 2016a).

In these frameworks the Anthropocene is seen to demarcate a shift from humans as merely agents of local ecological changes to agents of geophysical history that are capable of affecting all planetary life by modifying the Earth system (cf. Chakrabarty 2009; Hamilton 2015; Morton 2013:7; Steffen, Crutzen, and McNeill 2007). Unsurprisingly, the Earth systems scholarship from which the term largely emanates has also focused on the Anthropocene’s utility in confirming humans’ planetary impacts within the stratigraphic systematics of the Geologic Time Scale maintained by the International Commission on Stratigraphy—that is, how humans’ global physical environmental impacts produce an unambiguous and permanent signature in Earth’s lithological and sedimentary records (e.g., Steffen et al. 2016; Vince 2011; Waters et al. 2016a; Zalasiewicz et al. 2015). On these lines, scientific debate focuses on where to place the Anthropocene’s stratigraphic boundary, or “golden spike.” The mid-twentieth or late eighteenth centuries are the most commonly advocated among a slew of other suggestions, including the “Orbis spike” of 1610, the mid-Holocene rise of agricultural land clearing, using the term to apply to the entirety of the Holocene, and even the megafaunal extinctions of the late Pleistocene (e.g., Braje and Erlandson 2013; Crutzen 2002; Erlandson and Braje 2013; Hamilton 2015; Lewis and Maslin 2015; Smith and Zeder 2013; Waters et al. 2016a; Zalasiewiz et al. 2015).

It is important to stress that proposals for formalizing the Anthropocene as a new epoch are based on three different forms of evidence that are not all applicable to the analytical framing of the Anthropocene by humanities and social science scholars noted above. Formal geological time periods are delimited through the identification of Global Boundary Stratotype Sections and Points (GSSPs or “golden spikes”) or the identification of Global Standard Stratigraphic Ages (GSSAs; Zalasiewicz et al. 2015). While both GSSPs and GSSAs are commonly used to mark geologic time transitions, GSSPs require the identification of a physical marker in a specific stratigraphic sequence of rocks, sediments, ice, or other layered materials, while GSSAs are simply chronologic times selected to mark significant changes in the Earth system. For example, Zalasiewicz et al. (2015) proposed to use radionuclide deposits from atomic bomb testing as a potential Anthropocene GSSP and recommended the precise timing of the first atomic bomb test be used as an Anthropocene GSSA. ESS presents a third form of evidence by identifying major shifts in Earth system functioning as an Anthropocene state transition (Steffen et al. 2016). While the first two approaches (GSSP and GSSA) are concerned with identifying anthropogenic strata or significant historical events, the last is concerned with environmental processes.

It should already be clear that these different designations should not be conflated. While a stratigraphic designation (GSSP) might serve as a practical reference for geological systematics to order sediments, the other (ESS) is a reference to the historical behavior of the relationships among Earth’s various interacting “spheres”—the atmosphere, lithosphere, hydrosphere, and biosphere—that have been similarly categorized for heuristic and analytical purposes. In that sense, only this last mode of designation is primarily concerned with understanding long-term relationships among human inhabitants and the workings of the Earth system. It is also the only Anthropocene designation that speaks directly to the concerns of humanities and social science scholars for the period’s dissolution of natural history and human history or for assessing the species as a “geophysical actor.” Indeed, ESS is foundationally concerned with how human activities both are embedded within and help to constitute the Earth system (e.g., Schellnhuber 1999). By way of contrast, stratigraphers concerned with GSSP designations might usefully categorize a new geological period by the presence of plastics and Styrofoam in sediments, just as an archaeologist of South India might identify the Iron Age by the presence of Black and Red Ware ceramics (e.g., Thapar 1957); yet neither stratigraphic designation necessarily implies an ontological shift in human-environment relationships. Moreover, the GSSP need for stratigraphic identifiers to mark globally synchronous Earth changes, rather than diachronous changes that typify historically specific environmental changes, prohibits the application of GSSPs to characterize more gradual and accumulative human alterations across Earth’s surface (Edgeworth et al. 2015; Ruddiman et al. 2015; Turner et al. 1990).

Periodization criteria for Anthropocene formalization in the Geologic Time Scale are thus clearly problematic for understanding long-term human environment relationships. Yet, it is worth stressing that the most literal translation of its etymology in scientific nomenclature references the “recent age” (cene) of “humans” (anthropos). Indeed, the Anthropocene concept appears first and foremost as a temporal designation—a period during which scholars recognize humans’ emergence as a “great force of nature,” the end of the division between society and nature, or the global presence of stratigraphic material evidence produced by the anthropos. Considering that the Anthropocene is at root a chronological designation about human activities and their relationships to the global environment, one might expect that anthropology would have had input into its formulation.

An Archaeology of the Anthropocene

It is remarkable that the scholarly discipline most focused on long-term changes in human-environmental relationships has been one of the most peripheral to discussions on the Anthropocene. As archaeologist Keith Kintigh and colleagues (2014) have recently noted, archaeology has hardly contributed to the formulation of the Anthropocene concept. Many of the early canonical pieces that defined the Anthropocene cite little or no archaeology (e.g., Crutzen 2002; Crutzen and Stoermer 2000). Indeed, its principal advocates over the last 15 years were largely natural scientists who stressed humans’ unique species-level effects on the Earth system over the last few centuries, largely dismissing the archaeological record of prehistoric periods as insignificant. While some of these foundational papers included historical scholarship in support of their claims of the uniqueness of environmental systems following the Industrial Revolution, they did not substantially rely on archaeological evidence. In fact, the pioneering work of Ruddiman and colleagues is the exception that seemingly proves the rule in this characterization: Ruddiman (2003) seriously considered the archaeological record to argue that prehistoric human agricultural activities greatly affected the climatic history of Earth by at least the middle Holocene but was generally dismissed early on by some of the more strident advocates of the Anthropocene (e.g., Ruddiman 2007; Ruddiman et al. 2016; Steffen, Crutzen, and McNeill 2007). This is not to suggest that early proponents of the Anthropocene did not have some general understanding of an archaeological record for long-term environmental change; clearly they did (e.g., Steffen, Crutzen, and McNeill 2007). However, the Anthropocene’s emphasis on humanity’s large-scale planetary effects allowed many scholars to easily overlook the archaeological and ecological evidence for pervasive long-term, human-related environmental changes that were tied to specific places or regions. As more recent scholarship on the Anthropocene has begun to incorporate regional archaeological records for human-related environmental histories, proponents of the Anthropocene have been forced to confront the difficulties of clearly demarcating it temporally (cf. Boivin et al. 2016; Braje and Erlandson 2013; Butzer 2015; Crumley et al. 2015; Edgeworth et al. 2015; Erlandson and Braje 2013; Rosen et al. 2015; Ruddiman et al. 2015). Indeed, the archaeologist Karl Butzer (2015) has suggested that the Anthropocene should be considered an “evolving paradigm.” Yet an emphasis on global-scale changes has continued to allow many scholars to explicitly argue that anthropologists, archaeologists, paleoecologists, and others building on place-based and regional environmental evidence have little to contribute to Anthropocene scholarship (e.g., Hamilton 2015). This position is untenable.

If the Anthropocene is an “evolving paradigm,” it is because its formulation depends on several underlying ontological challenges that require an anthropological and ecological intervention. To begin with, much of the Anthropocene literature reproduces the very dichotomy of nature and society that many scholars suggest it dissolves, separating one recent period during which the two realms could be usefully held apart from another more recent period in which they cannot. Such scholarship inherently perpetuates the natural-cultural distinction and also ignores historical and cultural diversity of human-environment conceptualizations; if, for instance, the Anthropocene represents a period in which people no longer acknowledge a clear divide between nature and society, as some argue, then many people were living in it well before Western scientists designated the period (e.g., Bradley 2000; Escobar 1999; see Bauer and Bhan 2018 for discussion). Moreover, in singling out the agency of humans as a “geophysical force,” the Anthropocene narrative also “silences” (sensu Trouillot 1995) a wide variety of social distinctions and landscape histories that are critical to contemporary understandings and experiences of socio-environmental conditions. In attributing climate change to humanity as an homogenous actor or species, it obscures underlying social differences and “asymmetries related to both the production and experience of environmental circumstances” and associated vulnerabilities (Bauer and Bhan 2016:66; Malm and Hornborg 2014; Ribot 2014; Sayre 2012). This is the case even as the most common proposals for marking the Anthropocene highlight decidedly Eurocentric drivers of Earth and human history, such as the invention of the steam engine (see discussion in Crossland 2014; Morrison 2015).

Humans, of course, do not modify global environmental systems by acting as an undifferentiated and homogeneous web, network, or species. They do so as socially, culturally, ecologically, and geographically situated and differentiated actors that have long been documented by archaeologists, cultural anthropologists, ecologists, and geographers (e.g., Bauer 2015a; Bauer and Bhan 20162018; Crumley 1994; Ellis 2015; Witmore 2014). Moreover, there can be little debate that humans who facilitated the production of greenhouse gases and global warming that originally inspired the Anthropocene designation have done so unequally and in different ways in different times. Crutzen (2002:23) himself recognized this early on: “these effects have largely been caused by only 25% of the world population.” This remains equally true today, with recent US per capita carbon dioxide emissions a full order of magnitude greater than those of India, for example (17 vs. 1.7 metric tons; World Bank 2015). Moreover, human-related climate change likely has early roots in land clearance and fire use in the early Holocene and perhaps even in the mass extinctions of megafauna across continents through the actions of late Pleistocene hunter-gatherers (cf. Braje and Erlandson 2013; Doughty 2013; Ruddiman et al. 20152016). Though a recent Anthropocene periodization might call needed attention to humans as agents of contemporary climate change, it does so while potentially obscuring historical processes and social differences related to the production of environmental changes at local, regional, and global scales over multiple time horizons.

Anthropocene narratives also risk downplaying the many nonhuman materials, things, and organisms that people are entangled with and that also contribute to climate and other global environmental changes through a variety of relationships. As the historian Dipesh Chakrabarty (2009) reminds us, humans have always been “biological” agents who shaped their environments, both collectively and as individuals. What sets the Anthropocene apart from previous periods for many scholars is that humans are now historiographically geophysical or “geological” agents. Yet, the distinction between humans as “biological” agents of ecology versus humans as “geological” agents of climate that arguably warrants the designation Anthropocene needs critical discussion, as it imagines a realm of geophysics somehow disconnected and separate from the biological world in the past. Ironically, the functional interconnections among humans—and all living organisms—and “the spheres” is a fundamental precept of ESS (Schellnhuber 1999).

Differences between humans as agents of “biology” and “geology” are not clearly differences in kind. There should be no doubt that people utilizing contemporary fossil-fuel technologies are transforming Earth’s climate, marking them as geophysical actors when considered within the broader assemblage of material relationships that affect greenhouse gases. Yet this should not preclude other people, dependent largely on human labor in clearing land and releasing carbon, for example, from being considered “geological” actors, relegating them to mere “biological” or ecological roles. It is not difficult to see such a position slipping into the problematic historiographical divide between “modern” and “primitive” people, differentiating people that are now capable of transcending the confines of nature to alter their environmental circumstances from those of previous times (Bauer and Bhan 2016). Moreover, such a distinction between biological and geological agents ignores basic ESS, in which the dynamics of diverse bacteria, plants, and other species are coupled with and alter the composition and functioning of Earth’s atmosphere, lithosphere, and climate systems (Ruddiman et al. 2016; Schellnhuber 1999). To identify any one of these as a geophysical agent to the exclusion of others is to ignore the numerous interactions among Earth’s organisms that constitute the biosphere and their coproduction of atmospheric conditions and climate. Thus, to address when any organism, human or nonhuman, affects geophysical conditions is to also address how they are enmeshed historically within the material relationships of ecologies and geographies that contribute to atmospheric conditions. Humans—and other species—began altering greenhouse gas concentrations in the atmosphere long before the invention of the steam engine (e.g., Ruddiman et al. 2016).

The Historical Ecology of Geophysical History

ESS is founded on the principle that interactions among the atmosphere, lithosphere, hydrosphere, and biosphere together with the external forcings of solar irradiance form a complex system that contributes to the processes of climate change, the global biogeochemical cycling of many elements, and other dynamics of the Earth system (Schellnuber 1999). Actively growing trees, for example, sequester carbon dioxide from the atmosphere that on release through combustion or decomposition contribute to greenhouse gas concentrations and therefore alter climate and the growth of other trees through feedback interactions (Archer and Rahmstorf 2010; Barford et al. 2001; Flannery 2005; Vavrus, Ruddiman, and Kutzbach 2008). On geologic timescales, the oxygenation of the atmosphere during the Proterozoic eon (ca. 2.5 bya) by cyanobacterial photosynthesis profoundly and permanently altered Earth’s atmosphere and climate over hundreds of millions of years—a geophysical and geochemical state shift produced by biological relationships and an example of niche construction; atmospheric oxygenation produced the ozone layer, shielding Earth’s surface from harmful ultraviolet radiation, making Earth’s land habitable to multicellular organisms for the first time (Erwin 2008). This process also reduced concentrations of methane and triggered a period of global glaciation (cf. Frei et al. 2009; Kopp et al. 2005). These examples demonstrate that biological agents inherently also function as geophysical and geochemical agents in the Earth system, as the term biogeochemical implies.

Early members of the genus Homo arguably developed abilities to alter the atmosphere with the use of fire hundreds of thousands of years ago when set within the context of biogeochemical assemblages (cf. Albert 2015; Roebroeks and Villa 2011). Moreover, human activities were likely related to mass extinctions of a range of land animals with a cascade of profound consequences for ecosystem functioning across Australia around 50,000 years ago and later elsewhere in the world (cf. Barnosky 2008; Boivin et al. 2016; Braje and Erlandson 2013; Grayson 2001; Kirch 2005; Miller et al. 2005; Rule et al. 2012). In the Holocene, intensified forms of land use associated with agriculture, animal husbandry, and human population and settlement growth reshaped animal populations, vegetation communities, and the ecological and geomorphic trajectories across large regions of the globe (e.g., Alizadeh et al. 2004; Bauer 2014; Boivin et al. 2016; Casana 2008; Conolly et al. 2012; Ellis 2011; Ellis et al. 2013; Erlandson and Braje 2013; Fuller et al. 2011; Morrison 2009; Rosen et al. 2015; Wilkinson 2003). These data alone have supported multiple suggestions that the Holocene has “long been the Anthropocene” (Morrison 2013:23; see also Braje 2016; Certini and Scalenghe 2015; Erlandson and Braje 2013; Smith and Zeder 2013). While archaeological research has focused on humans’ roles in local and regional ecological and geographical histories, as opposed to a global role as geophysical agents in a coupled “human-Earth” system, a few examples from the archaeological literature amply demonstrate the significance of assemblages of humans and nonhumans in creating climatic and other environmental conditions at global scales, problematizing claims of a newly emergent “geophysical” effect associated only with industrialization.

Prehistoric expansion of rice agriculture, irrigation, and pastoralism likely caused a reversal in atmospheric levels of methane, a greenhouse gas that decreased in the first half of the Holocene but then increased after ca. 5000 years ago (cf. Fuller et al. 2011; Ruddiman and Thomson 2001; Ruddiman et al. 20082016; Vavrus, Ruddiman, and Kutzbach 2008). Fuller et al. (2011) have argued that archaeologically estimated increases in rice cultivation and livestock pastoralism in South and East Asia correlate with rises of atmospheric methane documented in Greenland ice cores. This correspondence has allowed a growing cadre of climate scientists to convincingly argue that “the anthropogenic greenhouse era began thousands of years ago,” as per Ruddiman’s increasingly well-supported “Early Anthropogenic” hypothesis (Ruddiman 2003).

Yet crucial to our broader point, both prehistoric and contemporary environmental transformations and their effects cannot be attributed equally to all members of these societies. Neolithic and Iron Age inhabitants of South India, for instance, differentially participated in agropastoral activities that produced methane and large-scale geomorphological transformations, such as soil erosion, and these differences were related to the development of status distinctions and social inequalities (e.g., Bauer 20142015a2015b; Sinopoli 2013). Moreover, early irrigated rice cultivation across large areas of South and East Asia was likely a highly politicized practice; there is strong evidence that not all inhabitants had access to irrigation facilities for growing rice and that irrigated and dry-farmed cultigens had differences in productivity, value, and symbolic uses in many precolonial contexts (e.g., Bauer and Morrison 2008; Ellis and Wang 1997; Huang 1990; Morrison 2009). Thus, even in these preindustrial periods, the historical ecology of geophysical history was also a political ecology, a point that is critical to recognize if we are to understand and engage actively with the long-term entanglements between cultural practices, social relationships, and the material workings of Earth. To understand the historical degree to which human activities have altered Earth systems thus requires that the full assemblage of processes and actors be considered and, equally important, the differences among them.

Discussion: The Anthropocene Divide and the Social Environment

Different designations of the Anthropocene direct scholarly attention toward different things—a stratigraphic marker (GSSP), a global historical event indicating a new “age” (GSSA), and the historical behavior of relationships among Earth’s various “spheres” of interaction (ESS). Only the latter, the Anthropocene formulation of Earth system scientists, is primarily concerned with understanding long-term relationships among humans and the workings of Earth’s climate and other systems. In that sense, it is also the only Anthropocene designation that speaks directly to the concerns of humanities and social science scholars for the period’s dissolution of natural history and human history or for assessing the species as a geophysical actor. Yet, as we demonstrated above, humans have been participants in Earth’s biogeochemical processes for thousands of years, and their influence on geophysical and climatic conditions likely significantly predates the most common chronological proposals for the Anthropocene. In short, there is not, and could never be, a clear date at which humans became “geophysical.” To be biological is also to be geophysical. Thus, the degree to which humans have influenced climate must necessarily be considered as a dynamic long-term process, a process that we have argued above and elsewhere is also deeply enmeshed in a political ecology—that is to say, how social affiliations, differences, and inequalities are also produced and reconstituted.

For these reasons, proposals for an Anthropocene periodization—for a geological divide between the “recent age” of humans and that which preceded it—significantly constrain historical understandings of human-environment relationships, including the recent processes and histories that have shaped contemporary contexts and the increase in human effects on global warming over the last few centuries. Thus, we are in agreement with other scholars who have recently sought to supplant the designation Anthropocene with other terms that critically represent the sociohistorical processes that are related to contemporary global warming. Jason Moore (2015), for example, has suggested an alternative “Capitalocene” to highlight relations of power in the production of social and environmental conditions over the last five centuries that underlie contemporary carbon dioxide emissions under capitalism. The “Plantationocene” has also been proposed to stress the “transformation of diverse kinds of human-tended farms, pastures, and forests into extractive and enclosed plantations, relying on slave labor and other forms of exploited, alienated, and usually spatially transported labor” that might also critically frame the current connections between human history and global warming (see discussion in Haraway 2015).

Critiques of the Anthropocene that call attention to how the designation silences underlying social relationships and inequalities could also be applied to many treatments of “anthropogenic” environments that fail to differentiate social actors (Sayre 2012), including those of archaeologists, historians, and ecologists who argue for a pre-Industrial origin of the period as well as Earth system scientists who view humanity as a homogeneous geophysical force following industrialization. To reiterate an earlier example, cattle pastoralism and irrigated rice agriculture associated with mid- to late Holocene land use in South India had well-attested political effects (e.g., Bauer 2015a2015b; Bauer and Morrison 2008; Morrison 19952009). In short, prehistoric environmental transformations within Asia that altered atmospheric conditions (e.g., Ellis and Wang 1997; Fuller et al. 2011; Huang 1990; Ruddiman et al. 20152016) were tightly linked to the production of social relationships and institutionalized forms of inequality and in that sense were similar to those of contemporary capitalism.

These archaeological and historical cases demonstrate the need to comprehend the politics and social processes of environmental production in the past as well as the present if we are to understand the development of global warming and other changes in the Earth system that articulate with social conditions (see also Ribot [2014] on the “sociocene”). For instance, many large irrigation reservoirs that were constructed in southern India within highly politicized contexts during the period of Vijayanagara imperial rule (ca. 1330–1565) continue to hold water, irrigate crops, and contribute to atmospheric methane today (cf. Bauer and Morrison 2008; Morrison 19952009). These features illustrate the diachronous character of human-related landscapes and their multiple temporalities in contributing to socio-environmental conditions at various scales (see also Bauer and Bhan 2018; Crumley 1994; Morrison 2009). Reframing the Anthropocene as the Capitalocene or the Plantationocene (e.g., Haraway 2015; Moore 2015) places much-needed focus on the social relations of production and consumption that have produced alarming increases in the magnitude of humans’ effects on the Earth system. Both terms also cogently supplant the Anthropocene by focusing on historical sociopolitical processes through which humans have come to dramatically alter Earth, emphasizing social conditions that preceded the invention of the steam engine or the atomic bomb. Even so, we should not forget the fact that humans contributed to geophysical conditions well before the emergence of capitalism.

Land use and its accompanying social relations have long been related to environmental histories and their concurrent contribution to planetary changes. By no means does this minimize the role of capitalist forms of production in understanding the current phenomenon of intensified global warming. Nor does it produce an evolutionary scheme that suggests that an Anthropocene was an “inevitable outcome of human becoming” (Witmore 2014:129; see also Crossland 2014). To the contrary, it is an explicit call to historicize socio-material conditions that have resulted in environmental transformations at multiple scales and to resist progressive evolutionary narratives that imply a distinction in the externality of humans in relation to nature—the “civilized” and the “savage” sensu Morgan (1964 [1878]).

Despite the explicit emphasis that many Anthropocene advocates place on disrupting the concept and ideology of nature, many Anthropocene narratives silently reproduce it by distinguishing a recent time when the Earth system was external to or unaffected by humans from a more recent period in which it is not. In our view, a critical role of archaeology and other historically oriented disciplines is not to push back the start of the Anthropocene; rather, it is to call attention to the historicity of nature, so that we might more fully expose and discuss assumptions about what socio-environmental conditions are desirable, for whom, and how those might be achieved or disturbed. Calling attention to this history unsettles a teleological sense of “the species” as a singular geophysical “force.” It also suggests reconsideration of “business as usual” environmentalist approaches that historically have been structured by the nature-society divide (e.g., Latour 2004) and that, ironically, maintain the ideological basis for global warming deniers to frame climate change as a strictly “natural” process rather than a social-environmental one. To be clear, profound and pervasive planetary changes cannot be attributed equally to the entirety of the anthropos, and it is essential that social relationships and material conditions be investigated among the different institutions, cultural practices, and material processes that produce them; yet, the development of capitalism cannot be the entirety of our account, even as we agree that it is critical to call attention to its importance in underlying alarming and ongoing environmental transformations (see also Bauer and Bhan 2018).

Conclusion

To reinforce the notion of a historical binary, of an “Anthropocene divide,” by precisely dividing the history of Earth into a time in which human social engagement with the production of environments is globally consequential from a time in which it is not flows strongly against contemporary understandings of both human-environment relations and the coupling of human activities with Earth systems from prehistory to present. It is time to put aside concerns for locating an Anthropocene divide. It is our concern that the Anthropocene narratives produced by the stratigraphic formalization of a new geological epoch will form a barrier to developing recognition of the history and diversity of social and environmental entanglements, as well as their contribution to the (re)production of undesirable conditions as the effects of global warming are differentially experienced. If the Anthropocene divide is to be dissolved, as we argue it should be, anthropology must provide theory, critique, and empirical accounts of the historical entanglements of social relationships, cultural practices, and material conditions that recursively shape socio-environmental outcomes embedded within the Earth system. To accomplish this, anthropology cannot walk alone but must work to teach, guide, and collaborate with other scholarly disciplines concerned with humanity and its role in shaping Earth’s past, present, and future.Acknowledgments

Conversations and collaborations with many friends and colleagues have shaped the thoughts and words expressed in this essay. Special thanks are owed to Mona Bhan, with whom we have long discussed many of the topics treated above. Mark Aldenderfer and two anonymous reviewers also provided careful feedback for improving the manuscript, and we are grateful for their guidance.

References Cited

Responses

Comments

Todd J. Braje

Department of Anthropology, San Diego State University, 5500 Campanile Drive, San Diego, California 92182-6040, USA (tbraje@mail.sdsu.edu). 20 VII 17

Although I generally agree with Bauer and Ellis and their supposition that the designation of an Anthropocene epoch obscures rather than clarifies our understanding of social-environmental change, I believe that the fundamental importance of recognizing an age of humans is lost in their argument. I am in favor of debate about the Anthropocene, as it produces dialogue across disciplines and with the public about how humans have helped create the global environmental crisis and why we need to do something about it.

Bauer and Ellis mirror the position of the Anthropocene Working Group (AWG) that the “anthropocene” and the “Anthropocene” (lowercase vs. uppercase) are very different concepts (Zalasiewicz et al. 2017:219). The AWG is concerned with the uppercase Anthropocene as potentially a formally designated unit of the Geological Time Scale. Their Anthropocene is a chronostratigraphic unit that must have a fixed point in time (with some error bar range, as is common with other chronostratigraphic boundaries), tied to hard rock stratigraphy or a golden spike. General discussions and debates centered on other “anthropocenes” (according to the AWG) are viewed through the disciplinary lenses of their authors (Zalasiewicz et al. 2017:219). These place different emphases on the motives, material evidence, human activities, Earth system processes, and so on, and the AWG argues that they are separate concepts. The anthropocene in regard to Earth system science (ESS), the identification of anthropogenic strata, historical events that propelled changes in Earth system functions, and environmental processes are, according to Bauer and Ellis, “the only Anthropocene designation that speaks directly to the concerns of humanities and social science scholars.” This position is presumably why Ellis can advocate for an Anthropocene focused on the social, political, and historical contingencies of human-environmental ecodynamics and argue that we should “put aside concerns for locating an Anthropocene divide” while at the same time coauthoring several high-impact manuscripts with AWG members supporting a recent Anthropocene boundary marker (e.g., Waters et al. 2016a; Zalasiewicz et al. 20152017). Bauer and Ellis argue that we need to put aside concerns for locating an Anthropocene boundary marker and propose that archaeologists and other social scientists should adopt the Capitalocene or the Plantationocene, focusing on the “historicity of nature.”

The mountain of Anthropocene publications over the last several years, in my opinion, has been both positive and negative. It has fostered conversations across academic disciplines about how different scientists think about natural versus anthropogenic, human-environmental ecodynamics, and the future of our planet. It has sparked interest and high-profile articles in numerous media outlets. The Anthropocene has become a powerful environmental education tool at a time when climate change and climate science are highly politicized, especially in the United States. The Anthropocene encompasses not only anthropogenic climate change but also exploding human populations, pollution, accumulations of plastics in our oceans, accelerating extinction rates, and much more, and perhaps offers talking points that may permeate the defenses of climate change deniers. Unfortunately, conversations about the Anthropocene in the scientific community seem to be turning to academic siloing, following arguments similar to those presented by Bauer and Ellis that the different Anthropocenes should be carved up and controlled by specific disciplines or that we need different terminology to describe, at the broadest level, the same problem—humanity’s impact on Earth (Zalasiewicz et al. 2017). What is lost is Crutzen’s underlying message (in my opinion the only one that really matters) in proposing an Anthropocene nearly 20 years ago, drawing attention to the accelerating modern environmental crisis and guiding “society toward environmentally sustainable management” (Crutzen 2002:23; Crutzen and Stoermer 2000). The Anthropocene, for the public at least, has become a rallying cry to raise awareness about the growing human footprint on Earth. We risk losing this as we quibble over boundary markers, anthropocenes, and the usefulness of the Anthropocene versus the Capitalocene or the Plantationocene. Must we fiddle while Rome burns?

As a historical scientist, I, for one, am comfortable with ambiguity. I realize that I will never be able to completely reconstruct the incredible complexity of the ancient human experience from the shell middens I excavate and analyze. It is past time that the larger scientific community becomes comfortable with, or at least accepts, some level of similar ambiguity with the Anthropocene. I agree with Bauer and Ellis that ESS and the historical processes that helped create the Anthropocene are of fundamental importance, but so is its adoption in our scientific lexicon and our communication with the public. Why replace the Anthropocene with another term or terms and lose all the momentum built toward educating the public and stimulating interdisciplinary dialogues? As I have proposed previously, a merged Holocene/Anthropocene epoch would force us to think about the long-term impacts of humans, which have been variable across time and space, and offer a clear message to scientists and the public about humanity’s role in our growing environmental crisis (Braje 2016). A Holocene/Anthropocene would offer no starting point for humanity’s significant influence on Earth systems but would recognize the long-term, variable processes at work. This turns the conversation from the effects to the causes of the Anthropocene, calls attention to the “historicity of nature,” and concentrates attention on the conceptual merits of the Anthropocene. The Holocene/Anthropocene would function similarly to other previously designated geological epochs (Zalasiewicz et al. 2011:837), as a way to frame interdisciplinary, scientific inquiry of coupled human-natural systems in a practical and meaningful way (Smith and Zeder 2013:12).

Stanley C. Finney

International Union of Geological Sciences and Department of Geological Sciences, California State University, Long Beach, California 90840, USA (stan.finney@csulb.edu). 24 VII 17

“The Anthropocene Divide” by A. M. Bauer and E. C. Ellis provides very cogent reasons for not formally defining a beginning to an “Anthropocene epoch” yet fails in its explanation of the formal basis for a new interval in the Geologic Time Scale. As with most presentations on the Anthropocene, it ignores the true nature, purpose, and history of the chronostratigraphic units (system, series, stage) approved by the International Commission on Stratigraphy (ICS) and ratified by the International Union of Geological Sciences, which serve as the material basis for the geochronologic units (period, epoch, age) of the Geologic Time Scale. The primary argument of “The Anthropocene Divide” is that the human impact on the Earth system has spread episodically over the Earth through space and time and that to demark the now global impact with the term Anthropocene ignores a long history of intensification and dispersal of human impact. The primary purpose was not to describe the nature of chronostratigraphic units. Nevertheless, the authors do, and they do so in a manner promoted in the publications of members of the Anthropocene Working Group of the ICS Subcommission on Quaternary Stratigraphy, for example, that of Zalasiewicz et al. (2015). Finney and Edwards (20162017) challenged the misrepresentation that only a lower stratigraphic boundary must be proposed, approved, and ratified for the Anthropocene epoch to be formally recognized. Yet, what ICS establishes are chronostratigraphic units, which are intervals of stratified rock. A boundary between successive units is materially defined as a stratigraphic horizon in a single stratigraphic section, what is called a Global Stratotype Section and Point. It serves as the global reference on which the boundary is correlated to other stratigraphic sections worldwide. But the key concept is that the boundary is used only to set stratigraphic limits to the chronostratigraphic unit. ICS, the commission on stratigraphy, defines stratigraphic units, specifically, global chronostratigraphic units that are the material basis for the units of the Geologic Time Scale. Numerous recent publications propose stratigraphic markers for the beginning of the Anthropocene, but none provides documentation of the proposed units itself, which would be the Anthropocene series. Waters et al. (2016b) do illustrate the Anthropocene in a lake core, but it consists of only 2 cm of unconsolidated organic matter. It is unfortunate that Bauer and Ellis chose to ignore the nature of the units approved by ICS and instead continue with the serious misrepresentation. Bauer and Ellis cite Waters et al. (2016a) and Zalasiewicz et al. (2015) as providing evidence that “humans’ global physical environmental impacts produce an unambiguous and permanent signature in Earth’s lithological and sedimentary records.” They seem to not realize that stratigraphic documentation, from stratigraphic logs with sample levels and analysis, is not presented in those publications whatsoever, except for the 2 cm of unconsolidated organic matter in a lake core.

Also most pertinent to any discussion of formalization of an Anthropocene epoch is consideration of the usefulness of the term, particularly its stratigraphic application. Since the beginning of recorded human history, many geologic events are recorded in and referred to by years in the Gregorian calendar, and timing and history of all human impact is expressed with the Gregorian calendar. This applies to the lava flows in Hawaii, where individual flows are referred to specific dates (Poland et al. 2016). In geology textbooks, notable volcanic eruptions and earthquakes are listed in tables by the year in which they occurred. The lahar that devastated Armero, Colombia, deposited a thick, extensive blanket of sediment filled with human debris. It is referred to as the Lahar of November 13, 1987. It overlies another extensive lahar deposit that is referred to as the 1845 Lahar. Referring to the Anthropocene and Holocene lahars would be of no value. Throughout southern Europe, human artifacts discovered in soils and on the surface are referred to as Roman. Referring to them as Holocene would be of no value. It is of concern that many who publish on the Anthropocene as a new unit of the Geologic Time Scale fail to understand the basis of the units of the Geologic Time Scale. It is of further concern that they do not realize that the human calendar has replaced the Geologic Time Scale when giving the ages of geologic events and human events (impact) that have long been recorded by humans as they occurred.

Although Bauer and Ellis state that the Anthropocene “designation has been taken up vociferously across the academy,” they fail to recognize that it has not been so within the geoscience and stratigraphic communities. Presentations on the Anthropocene are rare at national and international geoscience meetings, other than by repeated presentations by a few members of the Anthropocene Working Group.

Bauer and Ellis state that “the claim that humans are altering the functioning of Earth as a whole has now been confirmed,” yet they ignore the fact that major changes to the Earth system have been controlled by internal tectonic and magmatic processes and extraterrestrial processes over which humans have no impact and no control and that, in turn, can catastrophically change the Earth system.

Unfortunately with discussions of the Anthropocene, those who are not geological scientists and particularly those who are not stratigraphers too often misrepresent the nature of the Geologic Time Scale, appear ignorant on the nature of stratigraphy, and do not fully understand the Earth system. Further, they seem not to recognize that today we use the human time scale, not the Geologic Time Scale, when dealing with human impact on the Earth system as well as expressing the age and timing of geologic events. Thus, there is no geological/stratigraphic need for an Anthropocene series. And if not formalized as a unit of the Geologic Time Scale, “Anthropocene” can have whatever meaning one wants it to have.

The Importance of Reference Frame

Jed O. Kaplan

Max Planck Institute for the Science of Human History, 07745 Jena, Germany (kaplan@shh.mpg.de). 11 VII 17

The Anthropocene was not originally introduced as a stratigraphic concept (Crutzen and Stoermer 2000) but rather as a philosophical idea meant to highlight the magnitude of human action in the Earth system. Recently, a group of scientists led by stratigraphers has been considering whether or not it would be valuable to formalize a stratigraphic definition of the Anthropocene, and if so, when and how to define its formal beginning—this is a requirement of all geologic epochs. Such an uppercase “A” Anthropocene would be recognized only after a process of definition, consultation, and ratification of a body largely comprised of Earth scientists.

As colleagues and I argued earlier (Ruddiman et al. 2015) however, the uppercase Anthropocene is an unnecessary concept. The Geologic Time Scale was a triumph of nineteenth-century scientific endeavor but has been rendered largely obsolete by the advent of radiometric dating. Radiocarbon and other techniques allow us to precisely estimate when certain events took place and can in large part trace the diachronous evolution of human-environment interactions around the world since our emergence as a species. We argued then, and continue to argue, for a lowercase “a” anthropocene, a recognition that we live on a planet largely transformed by the actions of our species, even to the point where our actions have become as important as changes in the Earth’s orbit around the sun or plate tectonics in influencing the state of the Earth system. We are also well aware of the problem of a stratigraphic definition of the age of humans, precisely for the reasons cited in this paper: human influence on the Earth system is a process with a long and variable history that emerged with the dispersal and migrations of humans across the planet, had different expressions in different places and times, and was by no means a unidirectional process but rather one that is marked by accelerations, decelerations, and even reversals in the sign of human influences over time on landscapes, plants, animals, and even the chemical composition of the atmosphere.

Given this long and diverse history of the anthropocene, one of the major issues currently limiting our understanding of the processes is the lack of reference frame. The “great acceleration” of anthropogenic activity (Steffen et al. 2011) clearly distinguishes the late twentieth century from earlier periods in Earth and human history, but the period immediately prior to this era or even a few centuries beforehand was also indisputably distinct from the “world without us.” Identifying a world without us surely requires examining the period before the beginning of the Holocene, but as we look into the past Ice Age, the Earth system in its glacial state was so different from the contemporary era that it is extremely difficult to use, say, 50,000 BP as a point of comparison. The global, rapid, and massive climate and environmental changes that occurred during the Pleistocene-Holocene transition are one of the reasons why it is very difficult to disentangle anthropogenic from other factors in explaining the extinction of the Pleistocene megafauna. To identify a period with climate analogous to that of the last several millennia but without substantial human influence, we would need to consider the last interglacial era, around about 125,000 BP, although even at this time anatomically modern humans were present throughout Africa. Perhaps the penultimate interglacial, 200,000 years ago at the dawn of human evolution, would be an appropriate time to consider the “natural” state of the Earth system. Unfortunately, extremely few terrestrial paleoenvironmental archives such as lake sediments—it is on land where we expect to see human influence—have records that extend so far back in time. We are therefore faced with the problem of lack of direct evidence for the evolution of human influence on the Earth system over time.

By the end of the glacial period, at the beginning of the Holocene 11,700 years ago (Walker et al. 2009), humans had spread to occupy even the extremes of all of the continents except Antarctica. On the other hand, many oceanic islands, large and small, were occupied by people only later in the Holocene. While imperfect in many ways, we may use reconstructions and observations of human influence on islands as an analogy for what may have happened on the continents earlier in Earth history (e.g., Boivin et al. 2016; Rolett 2008). Another way to understand how, when, and where humans influenced the Earth system is to employ process models of coupled human-environment interactions; in a hypothesis testing mode, it is possible to contrast model simulations of “the world we had” with the “world without us” (e.g., Kaplan et al. 2016). While it might ultimately be difficult to unequivocally prove that human agency was the cause of changes to landscapes, flora, and fauna, modeling experiments illustrate what could have happened and provide a valuable impetus for further, targeted paleoenvironmental and archaeological investigations.

As Bauer and Ellis point out in this article, the social sciences and humanities are largely concerned with the process (Earth system science) definition of the anthropocene. Many Earth system scientists themselves, however, continue to perpetuate the myth of a planet largely free of human influence in the latest preindustrial Holocene, and this perspective has had a large influence on the discussion surrounding a formal stratigraphic definition of the anthropocene. On the other hand, it is obvious to many archaeologists and historians that the state of the Earth system one or two centuries ago was clearly modified through anthropogenic activities. There is, therefore, an urgent need for social scientists to be engaged in the discussion around the anthropocene and to bring their evidence more clearly in front of the global change community. For many practitioners, this requires a leap of faith; few archaeologists or historians are comfortable with drawing general conclusions beyond their locality or period of expertise. But their synthetic viewpoint is invaluable and, combined with process modeling, will provide a powerful illustration of the state of the Earth system and improve our ability to put things into perspective, that is, to provide a reference frame for the anthropocene.

Ontologies of Occlusion in the Anthropocene

Jesse Ribot

Departments of Geography, Anthropology, and Natural Resources and Environmental Studies, University of Illinois, Urbana-Champaign, Urbana, Illinois 61801, USA (ribot@illinois.edu). 26 VII 17

In this superb article, Bauer and Ellis explain how the “species” framing of “Anthropocene” occludes socially stratified causes and effects of climate change. Thus, it is logical that this framing also hides differentiated responsibilities for both cause and care. However, they later merge nature and culture in a manner that can also erase the very possibility of moral judgment and thus responsibility and response. They argue that “Anthropocene narratives … risk downplaying the many nonhuman materials, things, and organisms that people are entangled with and that also contribute to climate and other global environmental changes through a variety of relationships.” Indeed, climate-oriented explanations of weather-related damages are known to occlude the multiple causes of the vulnerabilities that place people at risk (Ribot 2014). Hazards (climate or otherwise) without vulnerability do not cause damage—they work together. With any given hazard, some people are damaged while others are not; that difference is vulnerability, not climate.

But the authors also evoke a different, Latourian-style occlusion—although their nature-culture discussions belie a more nuanced stance. Like Latour, they emphasize the need to attend to (ostensibly ignored) nonhuman things that shape outcomes, despite the fact that attention to these things is already present in any rigorous analysis of causality. Indeed, who ever said that the material world and material objects do not have effects? Was this ever in question? Thus, this object-oriented “turn” (ironically labeled “new materialism”) occludes the long history of analyses of social and material causes of climate crises. All thorough analysts—from Sen (1981) to Watts (1983) onward—bring in human and nonhuman factors.

Unfortunately, Latour goes further. He calls these nonhuman things “agents”—attributing this most-human quality to them. This introduces another occlusion, an occlusion of the role of agency in responsibility; by equating humans with objects, equating agency to any mere force, and thus flattening the relation between human and nonhuman influence—a flat ontology merging subject and object.

Objects can, of course, contain human agency. But they have no agency. Humans contribute to making the world. They influence it. They shape it. They are shaped by it. That relationship still does not give agency—a uniquely human attribute—to things. Things have force. Forces have effects. Effects have consequences. Consequences can, when humans are involved, have meaning. Human agency, like dead labor, is in things and shapes outcomes. This does not (without distinctly human fetishism) give things agency. Nevertheless, the forces that drive and shape things take on particular meaning when we can trace their origin back to humans. It is not agency of the objects that carry it. It is human agency that articulates through them. It is human agency that establishes blame, liability, and responsibility (see Calabresi 1975; Harte and Honoré 1959).

To attribute responsibility, a major reason that imagining an “Anthropocene” (of socially differentiated cause and effect) is worthwhile, we need to maintain the distinction between object and subject, nature and culture. For effective response (my goal), we need to know three things: (1) the human actions and nonhuman forces damaging the environment we depend on (whether or not we generate that environment or influence its nonhuman forces), (2) how we can reduce effects (regardless of their human or nonhuman origins) that undermine our environment, and (3) where to locate responsibility—what society judges can and should be done and who should do it. This responsibility—like blame or liability—cannot be located in the nonhuman forces. The force-agency distinction matters if response is to follow.

Since “should” shapes human action and thus outcomes, it must be within the scientific study of causality within any social system. Yet Latour (2014) tells us there is no history or theory (his irreducibility principle) nor therefore morality (due to his flat nonhierarchical ontology); this framing will miss those things that depend on “should”—social judgment that creates a hierarchy of value. Latour’s radical empiricism blinds us to all of the acts that did not happen (and are thus not visible) but that society judges as necessary or moral. These must be historicized and theorized to discern. In short, the normative is central to any scientific analysis of the multiple causes of disasters—such as the causes of vulnerabilities that turn climate events into crises (Ribot 2014).

“Shoulds” are necessary for the framing of any research that involves humans and that asks “why” something happened. This is because human (in)action is based on judgment. The inaction is visible only through knowledge of judgment—whereas action is manifest. Within a social world there is no asking why without asking about what is socially expected. Hierarchy (of human values), not flatness, guides action. We cannot know what was “not” done unless we know what could and “should” have been done.

This brings us full circle. “Should” is morality. It is located in the unique human characteristic called agency. It is in the will, predicated on the ability to think (à la Arendt 2003). If we view agency as everywhere, including objects, then everything, and therefore no one, is responsible. Tracing cause to an object’s force is fine. Yet, we must continue the search for agency, which is human, to establish the relations of responsibility and the possibility of response.

The Earth moves but is not moved. The Earth is a force without agency. Along with nonhuman forces, it carries in its movement the forces introduced by the agency of humans. That agency is part of causality. It leads us back to responsibility and basis for action—although responsibility can also come from mere knowledge of potential damages (knowledge, the apple, a good starting point for the Anthropocene?). The agency in the Earth is not of or from the Earth. It is ours, purely ours—no matter how it manifests and whether we can control it. True, “the traces of our action are visible everywhere” (Latour 2014:9). But it remains our agency since it is the antecedent that establishes responsibility for the movement that troubles us. We should be moved. We should consider what we do and how it affects others—the golden rule applies (see Arendt 2003).

Further, our being “subjected” to Earth’s vagaries does not give earth subjectivity (à la Latour 2014:9). The Earth remains object, shaped by our agency, but as much object as a table or chair. Placing it on the same plane with me, a subject, is tantamount to war—it is the objectification of humans. This flat ontological object-subject conflation is a frame of war that enables those of us who are subjects and have subjectivity to be reduced to the nongrievable equivalent of an object (Butler 2009). It is the equivalence, the erasure of difference, that reduces us. It is distinctly unethical. Humans are not equivalents of objects. Being is hierarchical—we live in a round world.

Once we distinguish humans from objects and recognize them as the locus of agency, then responsibility can be attributed and response can begin. I see no utility in asking whether humans are nature, since human nature, the ability to think and judge, is nature and is what distinguishes us from the remainder of the nature of which we are a part.

The Geological and Earth System Reality of the Anthropocene

Jan Zalasiewicz

Colin Waters

Martin J. Head

Will Steffen

J. P. Syvitski

Davor Vidas

Colin Summerhayes

Mark Williams

Department of Geology, University of Leicester, University Road, Leicester LE1, United Kingdom (jaz1@leicester.ac.uk; Zalasiewicz, Waters, and Williams)/Department of Earth Sciences, Brock University, 1812 Sir Isaac Brock Way, St. Catharines, Ontario L2S 3A1, Canada (Head)/Australian National University, Canberra, ACT 0200, Australia (Steffen)/University of Colorado Boulder, Boulder, Colorado 80309-0545, USA (Syvitski)/Marine Affairs and Law of the Sea Programme, Fridtjof Nansen Institute, Norway (Vidas)/Scott Polar Research Institute, University of Cambridge, Lensfield Road, Cambridge CB2 1ER, United Kingdom (Summerhayes). 26 VII 17

“A word means what I choose it to mean, no more and no less.” This pronouncement by Humpty Dumpty in Lewis Carroll’s Through the Looking Glass might be recalled in considering Bauer and Ellis’s contention that the “Anthropocene” as a sharply delineated geological term does not serve anthropology well and therefore should be more generally rejected. Their contention and accompanying assertions, though, are widely open to question.

Bauer and Ellis begin by saying that any such sharp delineation (“periodization”) is invalid because the relationship of humans to the Earth reflects a complex continuum (paradoxically, they do not reject the Holocene and Late Pleistocene even though these cut across the same continuum). We emphasize here that scientists working in the framework of geology and Earth system science (ESS) see all Earth history as comprising complex, continuous, and pervasively diachronous change and yet they regard the “periodization” given by formal geological time units as essential to their work. This is because these precise, synchronous, internationally agreed boundaries lead to unambiguous communication and enhance interpretation and understanding. They intermesh effectively with a wide and varied array of other time-related units (litho-, bio-, cyclo-, magnetostratigraphic, etc.) to build a detailed picture of Earth history. Earth system scientists find such “periodization” exceptionally useful because it provides a consistent way to discern and communicate significant changes in the structure and functioning of the Earth system from a very large amount of useful data, including data from archaeology and anthropology.

The Anthropocene concept and term indeed originated with Paul Crutzen (Crutzen 2002; Crutzen and Stoermer 2000) explicitly as a geological epoch/series to succeed the Holocene and was soon widely adopted by the ESS community. As interest in this concept grew, the term was also noticed by stratigraphers, with initial evaluation suggesting that it “had merit” as a potential formal geological time unit and should be investigated further, an extensive technical process initiated in 2009 by the Anthropocene Working Group (AWG) of the Subcommission on Quaternary Stratigraphy, part of the International Commission on Stratigraphy (ICS). In this context, the Anthropocene is being examined as a potential unit in the parallel chronostratigraphic/geochronologic “dual hierarchy” (i.e., as both a potential series and epoch) of the International Geological Time Scale.

This “dual” timescale is specific to geology but is just one of many means by which humans measure or subdivide time and is distinctive in simultaneously comprising synchronously bounded material units of strata (e.g., series) and their equivalent “pure” time units (e.g., epochs; Zalasiewicz et al. 2013). It is used to subdivide Earth history (not human history), which continues to the present and in recent times encompasses both human- and nonhuman-formed phenomena. We know of no equivalent timescale in anthropology, archaeology, history, or other cognate disciplines. It may of course be used in these or other disciplines when considered appropriate (see, e.g., Vidas, Zalasiewicz, and Williams 2016 regarding its relevance for international law), as with Bauer and Ellis’s use of Late Pleistocene and Holocene.

Key to the geological viability of the term is the distinctiveness of the stratal record, not least because this is the only means by which recent events can be related to the whole of Earth history. This record shows Holocene relative stability persisting even as substantial human civilizations rose and fell, leaving rich archaeological traces of their interaction with the environment. Plausibly, anthropogenic activities might have drip-fed greenhouse gases into the atmosphere for millennia to maintain CO2 levels and therefore Holocene climate stability (Ganopolski, Winkelmann, and Schellnhuber 2016; Ruddiman 2013). “Anthropogenic,” though, is not synonymous with “Anthropocene,” for which the key distinction is decisive and essentially synchronous impact at a geological scale.

Diverse stratigraphic markers indicate that strata from the mid-twentieth century onward can be clearly and widely distinguished from earlier strata (Waters et al. 2016a). These indicators belie Bauer and Ellis’s complaints (i) that the archaeological record has been ignored in the process, as they are commonly archaeological in nature (e.g., plastics, concrete, persistent organic pollutants, fly ash, artificial radionuclides), and (ii) that the currently suggested start of the Anthropocene represents “an arbitrary break.” The accompanying perturbation to sedimentation has been large and global, producing pervasive stratigraphic records. For instance, humans have placed large dams on the main stems of ∼2,500 rivers globally in less than a century, reducing sediment delivery to the coast such that coastal successions on every continent except Antarctica now record this near-synchronous event. Overall, since 1950, humans have been moving more sediment annually than wind, glaciers, and rivers combined. Earlier records of humans engaged in terracing, emplacing small check dams, or deforesting areas of Europe represent an important, indeed fundamental precursor to this phenomenon, but one that was patchy, diachronous over several millennia, and largely confined to land. These early records, for all their historical importance, cannot satisfactorily define a global and synchronous (chronostratigraphic) boundary that is geologically effective.

The stratigraphic record is congruent with the recognition of a major, ongoing perturbation of the Earth system (Steffen et al. 2016; Zalasiewicz, Waters, and Head 2017), including unprecedented change to the carbon, phosphorus, and nitrogen cycles and the biosphere, both marine and terrestrial. Energy consumption by humans since 1950 exceeds, by some 1.6 times, that of all of human history before 1950. One metric, the Anthropocene factor (Gaffney and Steffen 2017), over the last 65 years is orders of magnitude larger than for the entire Holocene interval prior to 1950. Such force multipliers show that humans have geologically very recently acquired the energy levels, the population, and the resource (engineering) application to significantly and globally change the Earth system: abundant evidence of this transformation now exists in the stratigraphic record (Waters et al. 2016a; see fig. 1).

Figure 1.
Figure 1. Geological identity of the Anthropocene: trends in key Earth system and stratigraphic indicators from the late Pleistocene to the present time. Note the largely gradual change (at this scale) across the Pleistocene/Holocene boundary, the general stability through the Holocene, the marked inflections, and the incoming of novel indicators that clearly demarcate a changed trajectory that we identify with the Anthropocene, most sharply defined from the mid-twentieth century. Adapted from Waters et al. (2016a) and sources therein. POPs = persistent organic pollutants.View Large ImageDownload PowerPoint

Whether ultimately formalized or not, this is a major change in our planet’s history, considerably sharper than most other boundary intervals of the Geological Time Scale and capable of being precisely defined stratigraphically. It is a phenomenon also sharply distinct from the first evidence of, or early trends in, anthropogenic traces on land. It would be obfuscatory to conceal this change under the cover of “a complex continuum.”

This stratigraphic record represents a precise, clear, and valid definition of “Anthropocene”—but it is not an exclusive one, and it may not be relevant to all fields of human-dimension scholarship. The interpretation of the Anthropocene as presented by Bauer and Ellis bears scant relation to the one we have described above. Rather, it resembles the Anthropocene proposal of Ellis et al. (2016; although they do not mention this proposal nor responses to it [e.g., Zalasiewicz, Waters, and Head 2017]); this former proposal by Ellis et al. was similarly nonviable as a Geological Time Scale unit and similarly obscured the post-mid-twentieth-century changes. Ellis et al. (2016) had argued that the Anthropocene should not be rejected but rather removed from the ICS mandate and recast in social science terms.

In the English language, many words bear multiple, distinct meanings (“nature,” for instance). Naturally, this risks confusion, but nevertheless we would not presume to “supplant” other interpretations of the Anthropocene. The remit of the AWG is understandably to frame the Anthropocene in a geological context.

If such terms as Capitalocene and Plantationocene are thought useful by social-science communities to describe human influence on Earth, then perhaps this will resolve the “many Anthropocenes” in current use. These terms do not, however, “supplant” the “geological” Anthropocene, as they represent different concepts, from different contextual backgrounds, with social science interest on the socioeconomic drivers of change rather than on resultant Earth system behavior and its petrified and strata-bound consequences. Social science investigations are not irrelevant to understanding Anthropocene stratigraphic and Earth system change; to the contrary, the dynamics of human/technology interactions are clearly crucial to this question. Similarly, the Ordovician-Silurian boundary may be satisfactorily and pragmatically defined in strata even as the Earth system dynamics that drove this period-scale change remain unresolved, intensely debated—and hugely important.

The main thrust of Bauer and Ellis’s paper is captured by their claim that the stratigraphic and ESS definitions of the Anthropocene are based on “distinguishing a recent time when the Earth system was external to or unaffected by humans from a more recent period in which it is not.” This is obviously not true. The ESS definition is based on the evidence that the planet is on a strong trajectory out of the Holocene (and indeed out of the glacial-interglacial cycling of the late Quaternary) and that human activities are the primary driver of this trajectory (Steffen et al. 2016). This does not imply that there was inconsequential human influence on the Earth system before the Anthropocene. Of course there was, as the Bauer and Ellis paper shows in some detail. However, it was only since the mid-twentieth century that Earth system scientists can say with some confidence that a trajectory out of the Holocene clearly began. For them, placing a Holocene-Anthropocene boundary there seems natural and incontrovertible given the evidence. This parallels the stratigraphic perspective, where the putative Anthropocene series, although clearly characterized by a range of novel proxy signals (e.g., Waters et al. 2016a), negates Bauer and Ellis’s argument that the Anthropocene somehow represents a black-white divide between no human influence and massive human influence. The Holocene already accommodates the rich evidence of human environmental imprint (Gibbard and Walker 2014).

Bauer and Ellis fail to acknowledge the complex-system nature of our ocean-dominated planet and this importance for the Earth system definition of the Anthropocene. Complex systems have many definitions, but two features are common to all of them: (i) emergent properties at the level of the system as a whole that cannot be aggregated up from subsystems or individual components of the whole system and (ii) attractors or reasonably well-defined states that are characteristic of the system as whole. The Anthropocene is on a rapid trajectory away from the Holocene/interglacial attractor (or more appropriately, away from the glacial-interglacial limit cycle of the late Quaternary) but is not yet an attractor in its own right. Bauer and Ellis detail the rich background to human development and influence on the Earth system but do not acknowledge our planet’s shift as a complex system that began around the mid-twentieth century. The long anthropological story of human development occurred within the Pleistocene glacial-interglacial limit cycle (the Holocene being the latest interglacial) of the Earth system. In short, Bauer and Ellis confuse human influence on the Earth system with a change in state of the Earth system as a whole. This confusion has long surrounded the Anthropocene concept and is not unique to their paper.

We emphasize that all these various approaches are nonexclusive and complementary, and we are puzzled as to why Bauer and Ellis should regard them as some kind of battlefield, with the Anthropocene as a singular trophy to be fought over and won or lost. Anthropologists and archaeologists, who search for and map out the early evidence of human activities and their patterns, offer much to the stratigraphic/ESS study of the Anthropocene (and, we trust, vice versa). Without the evolving dynamics of human-Earth relations over the long term, the Anthropocene as we consider it here would not have happened. We note the genuine, wide-ranging, and generous interdisciplinarity that the Anthropocene has stimulated; this has been among the most positive features of this phenomenon. We dearly hope to see it continue and strengthen but note that interdisciplinarity does not mean an absence of disciplinary coherence.

Missing the Mark: On the Matter of Narrative and Social Difference

Reply

Andrew M. Bauer

Erle C. Ellis

We are grateful to the commentators for engaging our essay and contributing to this forum. Their diverse perspectives emphasize the many distinct ways that the Anthropocene is being imported across the academy. Some see its utility as a political label, others stress its utility as a neutral geological period, and still others question its usefulness as either. While there is much agreement among the positions offered and the views we expressed in our essay, there are also significant points of misunderstanding or avoidance of our principal critiques of the Anthropocene periodization that deserve clarification in the interest of fostering productive interdisciplinary discussion.

The commentary of Zalasiewicz and colleagues of the Anthropocene Working Group was ostensibly the most critical of our position. Yet they also miscast our argument, evaded the more significant critiques that we foregrounded, and failed to acknowledge that the main Anthropocene narrative to which we and others are responding was in fact generated by Earth system scientists who promote the designation. To be clear, our essay does not challenge whether the Earth system is undergoing a state shift related to recent human activities or whether the magnitude of human impact has significantly increased. Rather, our essay problematizes the way in which geological systematics and the scientific narratives produced by Earth system scientists in accounting for this state shift frame historical processes and how that framing has been taken up by scholars.

Zalasiewicz et al. argue that we confuse “anthropogenic” for the “Anthropocene” (despite our explicit discussion of a tipping point and a recent state shift) and that we fail to recognize Earth as a “complex system.” Here they seemingly misunderstand our usage of the term “assemblage.” Similar to how natural scientists define “complex systems,” social scientists conceptualize assemblages as complexes of heterogeneous elements that, through their historical configurations and dynamic interactions, produce emergent outcomes—in other words, the whole is greater than the sum of its parts (cf. Bennett 2010; DeLanda 2006; Thomas 2015). We are aware that human activities do not simply add up to systemic change (cf. Turner et al. 1990), and we are not denying that geological or historiographic periods have disciplinary utility—indeed, archaeologists make heavy use of periodizations, albeit primarily at regional scales (e.g., South Indian Iron Age). As Finney noted, our essay does not challenge the validity or usefulness of an Anthropocene chronostratigraphic unit to geological systematics, though as both Finney and Kaplan diligently point out, its utility remains far from certain (see also Ruddiman et al. 2015).

The thrust of our argument is that the Anthropocene divide, the separation of a pre-Anthropocene from the Anthropocene, neither represents a shift in human agency from being merely “ecological” to becoming fully “geophysical,” as many have argued (see below), nor helps us to understand the historical, cultural, and political processes through which humans contribute to and transform Earth’s functioning as a system. Zalasiewicz et al. reiterate the geological need for a globally isochronous marker for anthropogenic global change; our point is that such a marker would not capture the socially differentiated and diachronous character of historical human-environmental entanglements that have contributed to a state shift in the Earth system. While one might question the degree to which any periodization could reflect such historical processes—as Kaplan’s commentary lucidly addresses in considering the anachronism of the Geological Time Scale more generally—our concern is explicitly with how the Anthropocene periodization obscures connections between pre-Anthropocene/Anthropocene human-environmental relationships while also foreclosing socially differentiated understandings of human-environmental interactions with its emphasis on the species. Zalasiewicz et al. mistake our interests in the geophysical impacts of human activities in prehistoric periods and the previous call of Ellis et al. (2016) for broadening interdisciplinary discussion with an attempt to win the “Anthropocene as a singular trophy” and sidestep our actual concerns for how human-environmental relationships are understood and narrated, given the critical recognition that narratives, scientific or otherwise, have ideological and political consequences.

When Zalasiewicz et al. sardonically dismiss the variable “meanings” of the Anthropocene to claim that a geological Anthropocene references the period in which the Earth has undergone its most recent state shift and little more with respect to historical processes or different kinds of human agency, they are reinforcing disciplinary divides and blatantly ignoring that many of the Anthropocene’s principal advocates, including Earth system scientists responsible for promoting the term, have explicitly provided narratives of human history to accompany the geological designation. Steffen, Crutzen, and McNeill (2007), for instance, state that the Anthropocene is “the current epoch in which humans … have become a global geophysical force” and that their “objective” is to examine the “evolution of humans and our societies from hunter-gatherers to a global geophysical force” (614). Such historical claims imply that humans did not have (global) geophysical effects prior to the Anthropocene. Thus, as humanities scholars have taken up the Anthropocene as a period when humans transitioned from being ecological actors to being “geological” actors, or the “inception of humanity as a geophysical force” (cf. Chakrabarty 2009; Morton 2013:7), they are not “confusing” the writings of Earth system scientists on the Anthropocene; rather, they are carefully considering the implications for their respective disciplines, such as Chakrabarty’s (2012) lucid recognition of “disjunctive” forms through which historical agency might be understood.

A primary concern of our essay is how the Anthropocene periodization has been taken up in such terms (e.g., geophysical vs. biological) and the ways in which it may, as Kaplan cogently remarks, “perpetuate the myth of a planet largely free of human influence in the latest preindustrial Holocene,” a myth that has heavily influenced “discussion surrounding a formal stratigraphic definition of the anthropocene.” In contrast to the suggestions of others, we stressed that the Anthropocene periodization cannot be taken as the beginning of humans’ “geophysical” impacts, as Zalasiewicz et al. also acknowledged. Moreover, explanations for the recent state shift in the Earth system must address prior intervals, especially if we accept that many human-related landscape transformations of thousands of years ago, such as the creation of methane producing irrigated landscapes and widespread deforestation, continue to affect the functioning of Earth’s biosphere and climate system today.

We welcome calls for complementarity and collaborations with archaeologists. However, interdisciplinary collaborations on relationships between human activities and Earth’s systemic functioning should not only mean sharing data or borrowing models but also learning from the critical perspectives that others bring—and this is especially relevant to narratives of the Anthropocene periodization. As archaeologists and historians know well, historical narratives are powerful in what they affirm and silence, ideologically (re)produce, and constrain and allow in discursive practice. Archaeologists, for instance, have been actively concerned with how their claims risk naturalizing or perpetuating presentist ideological constructs, such as those of nation or individual, or framing some humans as passive objects of history and others as its active makers (e.g., Leone, Potter, and Shackel 1987; Meskell 1998; Trigger 1980). As Earth scientists begin to write human history with archaeologists (or without them), we hope that they will be similarly open to such critical introspection.

In this regard, we disagree with Braje’s comments that our critique of the Anthropocene is tantamount to “fiddl[ing] while Rome burns.” While Braje “generally agree[s]” with our assessment of the Anthropocene’s obscuring tendencies, he nevertheless embraces the Anthropocene for its political work and appears less concerned with its occlusions (aside from arguing that it be extended to all of the Holocene). Although the contemporary politics of climate change were not the primary concerns of our essay, we nonetheless suggested how an uncritical acceptance of the Anthropocene periodization might actually work against a more inclusive environmental politics to mitigate the deleterious environmental effects of human activities. To start with: it potentially naturalizes a recent state shift as a teleological outcome of human evolution; it silences social differences and responsibilities with its emphasis on the species; it risks denying forms of historical agency outside of recent Euro-American innovation; and it effectively reproduces a society versus nature ideology that paradoxically enables “deniers” to maintain the position that climate change is purely “natural.”

We have noted several of these concerns before (e.g., Bauer 2015b; Ellis et al. 2016), and one of us has expanded on the Anthropocene narrative’s complex implications for environmental politics in considerably greater detail through other collaborations and mediums (see Bauer and Bhan 2018 for discussion). Here we will simply stress that to cast our critique as superfluous “quibbling” is to overlook an important point: that a critical framing of the historical process might enable ways of shaping both social relationships and environmental outcomes other than what is made possible by an emphasis on the emergence of the species as a singular “geophysical force” that recently came to “dominate” those of nature. This is why we have stressed the need for a political ecology (e.g., Biersack and Greenberg 2006; Robbins 2012) and are sympathetic to calls for a Capitalocene and other sociopolitical orientations, even while acknowledging that a critical history of capitalism cannot be the entirety of our account or the only alternative (see Bauer and Bhan 2018). Braje seems less bothered by the political implications of the silences (sensu Trouillot 1995) in the received Anthropocene narrative. We disagree with him regarding their importance (see also Bonneuil and Fressoz 2017).

Ribot agrees with us that the Anthropocene’s generalizing tendencies, in focusing on “the species,” mask important questions about social differences and responsibilities. Yet he equates our framing of the functioning Earth system as a dynamic assemblage to a “Latourian-style” merging of nature and culture that may erase the possibility for “moral judgment and thus responsibility and response.” Ribot’s concerns that posthumanist approaches that “distribute” agency (sensu Bennett 2010) foreclose important questions of ethics and intentionality dovetail with the positions of many others (cf. Martin 2014; Van Dyke 2015). We share these concerns and stress that our calls for a political ecology and emphasis on inequalities in the production of socio-environmental conditions are hardly a charge for “flattened” agency or responsibility. However, not forgetting the range of materials and other-than-human organisms that also give shape to Earth and through which human actions are entangled and realized is important for recognizing how humans partly shape social and environmental conditions simultaneously. There are many good reasons for rejecting the hubris of Anthropocene narratives that suggest humans now “dominate” nature, as Finney also effectively points out. In response to Ribot’s principled concerns, recognizing the social effects of things or that the production of climate is ontologically distributed does not mean that everything is an equal actor or the same kind of actor or even that the same “thing” will have the same effects in different contexts (e.g., Bauer and Kosiba 2016; Kipnis 2015). Hence, it does not exclude important questions of ethics, intentionality, or responsibility in regard to climate change; rather, it calls them to the fore in political discussion (see Bauer and Bhan 2018).

As these commentaries exemplify, there are many reasons why interdisciplinary discussions on the concept and utility of the Anthropocene should continue. As most of us agree, there is need to understand the historical entanglements of social conditions, materials, nonhuman life, and Earth system functioning. Moreover, there is still much to clarify as scholars are progressively drawn into conversations that go beyond the comfortable confines of their home disciplines, given that human-related climate change and mass extinctions are increasingly recognized as some of the greatest political concerns of our time. We the authors (Bauer and Ellis) have different disciplinary training and research objectives and are not in full agreement about the usefulness of the Anthropocene (or an anthropocene) designation to our respective fields or social concerns. However, that has not stopped us from finding common ground and learning from the critical perspectives that we can offer each other.

Narratives matter. “That which is said to have happened” recursively affects that which happens (Trouillot 1995:2). And this is just as true for narratives written by anthropologists, archaeologists, ecologists, and historians as it is for those written by geologists and Earth system scientists.

Anthropocene anthropology: reconceptualizing contemporary global change

Amelia Moore

https://doi.org/10.1111/1467-9655.12332

Abstract

The Anthropocene is the scientific label given by earth scientists to the current epoch of unprecedented anthropogenic planetary change. The Anthropocene is also a political label designed to call attention to this change and evolving notions of agency and responsibility in contemporary life. This article critically explores what I call ‘the Anthropocene idea’ and the condition of ‘Anthropocene spaces’ through selected anthropological writing about recent planetary change and through analysis of current events in a specific ‘vulnerable’ location. By considering recent events in The Bahamas, I arrive at an orientation that I call simply Anthropocene anthropology. Rather than advocating for the creation of a new subfield of research, this mode of engagement offers an open-ended conceptual framework for the critical examination of the Anthropocene idea as it influences the symbolic and material realities of contemporary Anthropocene spaces.

This article is a critical exploration of a concept that is poised to breach the walls of academia and become an international buzzword: the Anthropocene. The term has been proposed as a designation for a new planetary epoch, encompassing the present and recent past, in which human processes drive all major earth systems. The Anthropocene idea has spread from the domain of the earth sciences into the realm of the social sciences, sparking conversations about the stakes and form of humanistic research. This article can be read as one possible approach to the anthropological engagement of the Anthropocene idea. I call this approach Anthropocene anthropology.

My goal in presenting this article is to orientate analysis around the Anthropocene as a concept that reflects the recent creation of a contemporary problem space.1 Ideas about global environmental change influence thought and action in a number of arenas, and I hope to see anthropologists tackle the breadth of this planetary imagination animating emergent cosmologies of anthroposbios, and geo. New frameworks are needed to keep pace with authoritative arguments about collectivity and responsibility in the face of a changing world. These arguments attempt to define the present (and therefore the future and the past) for ever-increasing numbers of people (and nonhuman beings). Such definitions enable new possibilities and processes while foreclosing others. By engaging the discourses and processes enabled by the Anthropocene idea as they help to transform practices of life and work, knowledge produced about place and space, infrastructural aesthetics, and the evolving language available for subjectivation, we also engage the Anthropocene on material and symbolic levels (Beirsack 2006).

The greater argument underpinning this article is that even in an era of rapid change, we still need critical analysis of the characterization of that change and responses to it. I conceptualize my own work as an anthropological awareness ‘of’ the Anthropocene (understanding the idea as a historically contingent manifestation of social, political, and material processes), as opposed to work that is un-reflexively ‘in’ the Anthropocene (taking the framing of the problem and responses to it for granted). We need anthropological analysis that can examine the characterizations of life and change that are being made within authoritative fields of power and that can follow these ideas as they affect institutional policies with real consequences for the everyday lives of the people we work with around the world. We need concepts that can both speak to and evolve with emergent trends. At the risk of being chastised for not acknowledging the stakes of anthropogenic change, I want to make sure that we continue to maintain a space for the untimely questioning of the present (Rabinow 2008) in a time when ‘the obvious’ is solidifying rapidly around us (Raffles 2002). This orientation is a necessary complement to all the work we anthropologists do as partners in the fight against unjust and deadly global change. The work I advocate here is a part of that fight.

This article is divided into five further sections. First, I provide a brief ethnographic introduction to one location with renewed relevance in light of the Anthropocene idea: the islands of The Bahamas. Second, I explain the Anthropocene in more depth, introducing the significance of the idea for both the sciences and humanities. Third, I explore different anthropological engagements with global environmental change, providing a brief discussion of select existing work. Fourth, I introduce a platform for an Anthropocene anthropology that might be applicable in ‘Anthropocene spaces’ like The Bahamas. I conclude with an appeal for continued open-ended analysis of contemporary life in any locale said to be marked by anthropogenic planetary change.2

While this piece is not an in-depth ethnographic exploration of The Bahamas, I have written about contemporary life in these islands elsewhere (Moore 2010a2010b20122015). In the following section, I use brief examples of current events in that location to introduce some of the ways in which experiences of and ideas about global change have come to influence the narratives, relations, and spatializations of human and nonhuman life. These Bahamian examples ground the following sections on current anthropological engagements with global change and the Anthropocene.

The Bahamas and global change

The Bahamas consists of over 700 islands and cays – an archipelago – in the western Atlantic stretching between eastern Cuba and southern Florida. The nation is a designated small island state under the Barbados Program of Action with a small, majority Afro-Caribbean population of approximately 320,000 and an economic dependency on the international tourism industry and foreign investment. The Bahamas is also increasingly described as home to the third largest reef system in the world, a large marine carbon sink, a number of endemic species, and several distinct island ecologies (The Islands of The Bahamas 2013a2013b; Westphal, Riegl & Eberli 2010). The nation has been internationally defined by its marine relations, from sponge trading and boat building in British colonial times to coastal development and beach vacationing today. Once known as the ‘isles of June’, the archipelago is now often characterized as the ‘ephemeral islands’ in an era of planetary crisis (Bell 1934; Campbell 1978).

I have travelled to The Bahamas for over a decade, exploring what it means to visit, study, and live in the ephemeral islands. The tourist industry of The Bahamas has been extremely successful in selling a brand of ‘tropicalized’ island ecology, from lush vegetation and palm-fringed beaches to azure waters and vibrant marinescapes (Thompson 2006), but the actual experience of these island ecologies is something else entirely. Spindly pine forests in the northern islands give way to dense coppice woodlands in the central islands and then to arid bush, bent by the winds, in the southern islands. The bedrock of the Bahama Banks is composed of porous limestone, an accretion of calcareous sediment deposited over millennia, and rain water (the only ‘natural’ source of fresh water) collects in fragile aquifers beneath the ground. Beaches range from white, powdery sand that swallows footprints to sand that takes on a delicate pink blush resulting from the build-up of tiny invertebrate shells. Other shores are rough and craggy, cutting like knives into bare feet.

I have learned from fishermen and ecologists that in the dense mangrove marls one is likely to come upon well-used middens (mounds of conch shells discarded by nearby fishers that are generations old at the bottom and freshly killed at the top) while navigating channels in a small boat. I have observed the way that buildings weather on the islands, responding to the sea air, heavy rains, and smoldering sun, revealing layers of pastel paint or the texture of brain coral mixed into the stuff of the building stones. I have stopped being surprised when stairways leading down sand dunes to the beach abruptly end in mid-air as the sands recede into the ocean after seasons of wave action and rising tides. And in Nassau, I fall asleep too often to the acrid smell of the perpetually burning city landfill mingled with the scent of local thyme left over from dinner.

What strikes me is that the islands are intensely alive, animated by anthropogenic and biogeochemical processes both in and out of the water, and this life is a central part of the social worlds of The Bahamas. The examples are never-ending: human waste and run-off lead to algal blooms offshore that affect the course of coral growth, inspiring novel restoration plans; hot pink shards of conch shell adorn roundabouts that direct traffic around the latest mega-resort; underwater, whip-like crawfish antennae wave from under artificial habitats laid by fishers; clouds of flying termites migrate through window screens during heavy downpours; tiny anole lizards hunt for insects in the dark corners of the house.

Bahamian ecologies shape and are shaped by those who live and work in The Bahamas and by multiple forms of anthropogenic change. These shifting ecologies are a large part of the materiality of Bahamian living, participating in the postcolonial contingencies of everyday life. I have experienced how the question of anthropogenic change affects the lives of Bahamians as well as the activities of regional environmental management communities along with national conversations around tourism and development. Multiple problems linked to the Anthropocene idea in The Bahamas include physical vulnerability to climate change, marine biodiversity loss, coastal erosion, fossil fuel dependency, and coral reef disappearance. These ‘Anthropocene problems’ are viscerally experienced by Bahamian island residents and increasingly called upon by the natural sciences and other industries to justify the speculative reorientation of local and regional geopolitics, interspecies relations, land- and marinescapes, field research, and travel markets.

In terms of geopolitical positioning, postcolonial arguments about regional distinction (in which The Bahamas is positioned by members of its government as unique in the Caribbean in terms of per capita wealth and sophistication in the tourism industry [Cleare 2007]) now sit side by side with arguments about impending anthropogenic disaster. The Bahamas, as a low-lying archipelagic nation, is imbricated in multi-scaled global change predictions that influence the creation of alliances centred on the small island (such as the Alliance of Small Island States [AOSIS] at the United Nations, of which The Bahamas is a member), and the small island is now institutionally defined by social, economic, and environmental fragility in the face of anthropogenic planetary change.3 Sea-level rise as a result of global warming is predicted to be a grave national threat within the very near future (Hamilton 2003; London 2004), sparking one Bahamian speaker at a recent conference at the national college to state, with a strong sense of irony, that ‘many of us will be environmental refugees’ who have to ‘head to the hills of Haiti’, and to ask: ‘Forty years after independence, will we have another forty years going forward?’4 These predictions are also debated privately after storms remove sections of coastline, flooding homes and roadways (a palpable inconvenience in terms of connectivity and cost), leading to conversational speculation over pub beers in Nassau about the sensibility of investing in coastal property or infrastructure.

Simultaneously, justifications for the country’s fisheries sector, following themes in international marine conservation, have switched from exhortations for growth and expansion to precautionary tales of declining numbers of commercial species and poor reef health as just some of the detrimental impacts of overfishing in recent decades (Buchan 2000; Chaplin 2006; Chiappone, Sluka & Sullivan-Sealey 2000; Clark, Danylchuk & Freeman 2005; Moore 2012). One of the ways this framing has manifested in The Bahamas has been through government partnership with local and international environmental NGOs to obtain Marine Stewardship Council (MSC) certification for the harvest of Spiny Lobster, the country’s main fisheries export. Fishers are worried that without product greening via international MSC certification, important lobster markets in the European Union and United States will soon be closed to Bahamian exports as consumers demand a sustainable stamp for their imported seafood (Smith 2011; World Wildlife Fund 2013). One Bahamian woman with a family history of fishing in the island of Eleuthera explained to me that lobster used to be so abundant that their bodies were used as pineapple fertilizer, but the value of these species drastically changed over time as the Bahamian pineapple market dried up and lobster became a global luxury food item, making lobster a million-dollar fishery. MSC certification was now necessary she said, ‘so we can continue to sell to Walmart’, registering the irony that the promotion of sustainable fisheries is increasingly central to international commodity chains linking large-scale commercial fishing and the mass consumption of marine products.

Similarly, the recognition of anthropogenic biodiversity loss has led to re-imaginations of space in the archipelago. The number of existing and proposed marine protected areas (MPAs) in The Bahamas dramatically increased in the last decade owing to the country’s commitment to international conservation plans. For example, The Bahamas has committed to the Nature Conservancy’s Caribbean Challenge Initiative (CCI) to enclose 20 per cent of its marine and coastal space within protected areas by 2020. The CCI justifies its regional plans with the argument that ‘the Caribbean contains some of the world’s richest marine biodiversity … 10% of the world’s coral reefs, 1,400 species of fish and marine mammals and mile after mile of mangrove forests … Alarmingly, the Caribbean is increasingly threatened by development, pollution, overfishing and climate change’ (The Nature Conservancy 2013). However, these NGO arguments are complicated by some Bahamian fishers, in the Berry Islands, for example, who fear that there will soon be more restricted space than open space for local fishing, ‘more red dots on the map’, and that MPA restrictions exacerbate ongoing transitions of land and reef from the generational use of islanders descended from colonial slave populations to real estate leased to foreign development companies (Stoffle 2013).

Finally, it is important to realize that engagement with global change in The Bahamas includes actions within industries and markets outside of conservation. In a 2013 speech given in observation of The Bahamas’ fortieth anniversary of independence, the Prime Minister reminded citizens that ‘tourism is the lifeline to The Bahamas’. Marketing The Bahamas has always been an effort in place-making, and the islands of the country are considered by its Ministry of Tourism to be ‘tourist products’ in competition for global travellers (Cleare 2007; Jefferson & Lickorish 1991; Moore 2015). I have witnessed the rise of the ‘sustainable tourism destination’ as an emergent product appearing alongside the mainstay postcolonial paradise model of tourism (Strachan 2002). In addition to calls for regional ‘carbon neutral destinations’ (Moore 2010b), some developers in The Bahamas are designing, building, and marketing self-sufficient travel destinations using island-based principles to keep resource use to a minimum (Schooner Bay Ventures Limited 2008). The tourist product has long influenced the basic life-ways of the islands in terms of building codes, community social relations, racialized spatialities, and household aesthetics, so it is no surprise that plans for sustainable tourism spill over into local thoughts about daily life. Yet for some younger Bahamians working in the island of Abaco and thinking about starting families, sustainability also means trying to maintain a ‘Bahamian style of community’ – living next to your neighbour in dense settlements and looking out for one another – as opposed to the prevailing model of private, segregated enclave development. For many Bahamians, knowledge about sustainable living in the face of global environmental change will always be linked to travel markets, experienced as debates over life-style and the quotidian details of community life.

These examples represent some of the ways in which the physical spaces and socioecological relations of the country continue to be transnationally framed as fragile, vulnerable, and in need of redesign within the networks of knowledge and governance concerning global change. These are simultaneously some of the ways the experience of global change and its rhetorics come to affect the everyday lives of those who reside in the islands. Bureaucratic discourse is framed around events in the archipelago as exemplary of global concerns, but the results are felt close to home. These examples are neither exhaustive nor unique to The Bahamas. However, they represent the kinds of complex emergent conjunctures that have coalesced around the Anthropocene idea and the experience of The Bahamas as an Anthropocene space.

These examples also raise a number of interrelated questions that require further anthropological engagement as ethnographic problems: How do we characterize this process of political creation that leads to geopolitical alliance, rearticulated subjectivities for island residents, and transformations of the value of landscape and infrastructure? What forms of reason hold projects like MSC and the CCI together, and how is this Anthropocene logic materialized in social relations, relations with other life-forms, and experiences of space and place? How do we understand human life in the context of lively anthropogenic ecologies informed by an awareness of global change? What kinds of stories do experts and laypeople tell in order to locate themselves in global change narratives and enroll others in planning for change? Who designs the mental and material models that inform the experience of life in an Anthropocene space?

In order to begin to approach these questions – perhaps better characterized as an anthropological puzzle for the Anthropocene – I have compiled a select collection of recent work and useful concepts that I think move us closer to an Anthropocene anthropology. However, before I delve into those compilations, I must further explain the Anthropocene idea.

The Anthropocene idea

Despite the fact that there have been a number of international conferences and even a journal dedicated to the subject, the term ‘Anthropocene’ is of very recent origin. The idea was formally introduced to the scientific community in 2000 by the atmospheric chemist Paul Crutzen and the biologist Eugene Stoermer in the back pages of the International Global Change Newsletter (Crutzen & Stoermer 2000), published by the International Geosphere-Biosphere Program (IGBP). Since then it has been popularized by Crutzen and others, who have campaigned for the term to label a new geological epoch encompassing the earth’s present, recent past, and indefinite future, signifying the influence of the human population on the stratigraphy of the planet as well as on earth’s primary biogeophysical systems (Crutzen 2002; Crutzen & Schwagerl 2011; Crutzen & Steffen 2003).

The campaigning has paid off – though not without controversy. The International Commission on Stratigraphy (ICS), appointed by the International Union of Geological Sciences (IUGS), has a designated Anthropocene Working Group who must determine:

  1. if the Anthropocene, as a geological time unit, makes stratigraphic sense (can we actually see a record of human influence in the sedimentary layers of the planet now, and will we still see it many, many years from now?);
  2. if it is a useful category for earth scientists as well as other disciplines, and if this conceptual utility should also be considered in its designation (could the term’s rhetorical use be as important as its scientific use?);
  3. when its beginning should be placed in the historical record (at the evolution of Homo sapiens, the advent of agriculture, the Industrial Revolution, post-Second World War, or at some point in the future?);5
  4. how it should be formally designated (as a ‘golden spike’ or by numerical date?);
  5. if it is best considered an age, epoch, period, era, or aeon (adapted from Waters & Zalasiewicz 2013).6

Prior to the advent of the Anthropocene idea, geologists generally agreed that the planet had been residing in the post-glacial Holocene epoch for approximately 11,000 years. Formal adoption of the Anthropocene would replace the Holocene as the category defining the earth’s present geological condition. The International Geological Congress has delayed ruling on the formal adoption of the Anthropocene until at least 2016 while scientists conduct further analyses (Waters & Zalasiewicz 2013).7

To heighten the anthropogenic aspect, scientific proponents of the Anthropocene idea claim that as a result of population growth and resource use, humans are now a geological force in and of themselves, driving planetary change at an unprecedented rate. Beyond climate change and biodiversity loss (leading to what some have called the Sixth Great Extinction [Kolbert 2014]), scientists point out that domesticated animals are now the majority of living vertebrates, and measured by global weight, only 5 per cent of all vertebrates are ‘wild’. Some stress that human activities have even changed the shape of the tectonic plates. Supporters of the idea therefore believe that the overarching context for all life on earth is now the Anthropocene. In other words, the controversial event is this: humans have been so influential as to necessitate a change of epochal categorization in the life history of the planet. For many earth scientists, this categorization matters because at stake is the morality of contemporary environmentalism and the hope for real political recognition of planetary change and uncertainty (Osborne, Traer & Chang 2013).

The Anthropocene idea has further significance for the social sciences and humanities, inspiring arguments across several fields about the shifting meaning of multiple forms of life and earth processes. For the postcolonial historian Dipesh Chakrabarty (200920122013), the Anthropocene idea itself (specifically climate change) represents a challenge to the primacy of the human in that the consequences of human activity can no longer be explained in terms of social theories of difference or political economy alone. He now sees the human as irrefutably bound up in the natural world through the collective effects of the species as a geological force. The human is therefore a tense figure within the narratives of the Anthropocene, doubly human and natural, and Chakrabarty argues that postcolonial historians and other humanists can no longer focus on the merely human aspects of human lives, and must instead accept that humanity is not ‘free’ from the vital realities of planetary existence.

In a distinct but sympathetic argument, the science studies scholar Bruno Latour makes the ironies of the Anthropocene idea explicit. He writes, ‘[W]hat makes the Anthropocene a clearly detectable golden spike way beyond the boundary of stratigraphy is that it is the most decisive philosophical, religious, anthropological and, as we shall see, political concept yet produced as an alternative to the very notions of “Modern” and “modernity”’ (Latour 2013: 77). He sees the Anthropocene as a confession of sorts of the fallacy that various forms of humanity and earth’s biogeochemical processes can each be examined in vacuums that do not contain the other.

The geographer Jamie Lorimer (2012) also speculates that the idea of the Anthropocene represents the nail in the coffin for the modern dichotomy between nature and culture that has been so central to Western environmentalism (but see also Crist 2013). He contends that the idea of ‘pure Nature’ has not gone quietly from the sciences; instead it has left a trail of confusion in its wake, what Robbins and Moore (2013) have labelled ‘ecological anxiety disorder’. Lorimer contends that there are a multiplicity of natures at play that stem from the variety of political-ecological scenarios in the world, and that these scenarios involve integrations of the human and nonhuman that cannot be uniformly described in an a priori fashion and that require radically new research approaches (see, e.g., Holm et al2013).

When it comes to taking up the provocations of the Anthropocene idea in scholarly depictions of the world, Irvine and Gorji note that the turn towards ‘Writing Culture in the Anthropocene’ is part of a broader move in the academy (2013; following Kirksey & Helmreich 2010). The environmental historian William Cronon is one well-known early exemplar of this Anthropocene turn in the humanities. His work, exemplified in publications like Nature’s metropolis (1992), explores historical socioecological relationships shaped by market institutions in the American Midwest using a methodological blend of ecological and economic history. He has argued that it would have been problematic to reinforce the boundary between human and nonhuman in his investigation of the growth of Chicago because neither city nor country can be understood as solely natural or unnatural.

In a more politically explicit vein, the geographer Nahan F. Sayre argues that ‘the key points to draw from the Anthropocene have less to do with when it began than how it affects the underlying assumptions that scientists make about understanding the world’ (2012: 63) and how these assumptions affect policy. He cautions that declaring the age of anthropogenesis should not lead to an assumption of a transhistorical ‘anthropos’ with no attention to the uneven distribution of Anthropocene responsibilities and impacts. Therefore, the Anthropocene necessitates questions of ‘socioenvironmental justice’ (2012: 67). Sayre’s work and my own are aligned in that he recognizes that the Anthropocene cannot be reduced to climate change alone and that the idea presents a number of opportunities for anthropological participation. He states, ‘[T]he challenge is to rebuild our conceptual scaffolding to reflect these novel realities’ (2012: 63).

The last few years have seen solidifications of scholarship around climate change, the proliferation of political ecology, and the rise of social studies of nature. The social sciences and humanities have begun to discuss the Anthropocene, engaging with the idea and its challenges and invitations for scholarship. But what about specifically anthropological engagements with the Anthropocene? What orientations are needed to explore anthropological puzzles like those I have begun to follow in The Bahamas? My hope is that we can craft new frameworks that will open doors for such an engagement, expanding the scope of the political ecology of global change.8

Anthropology and global change

In this section, I show some of the diverse ways that anthropologists already approach the discursive and material realities of global anthropogenic change. Of course, anthropologists have long been interested in various phenomena of global environmental degradation (Bodley 2002), and, of course, environmental change depends on ‘how we see evidence of change and the stakes at play in the perceptions of environments as natural or cultural’ (Cameron 2013: 105). Many scholars accept the planetary scaling of late twentieth-century environmental science, asking how local communities are involved with degradation as a locally enacted global phenomenon.

Since the Rio Convention on Biological Diversity in 1992, a broad-reaching topic in the anthropological investigation of global change has been biodiversity loss, and studies centred on biodiversity are still an important example of anthropology in the Anthropocene. Anthropologists have documented the knowledge and practices of rural and indigenous peoples that affect crop diversity and the existence of rare species. They have also shown how local people relate to biodiversity protection in ways that differ from mainstream international conservation efforts (Haenn, Schmook, Reyes & Calmé 2014; Orlove & Brush 1996; West 2006). Importantly, anthropologists have also had a great deal to say about the social production and material manifestations of biodiversity (Hayden 2003; Lowe 2006; Nazarea 2006; West 2006). This work delineates biodiversity as one of the most influential political forms of the 1990s, reshaping idioms of value, exchange, development paradigms, material realities, and rights in ways that have transformed North-South relations to this day. Further, anthropologists have shown that the scientific designation of biodiverse nature has salience for the circulation of multiple forms of capital. This work suggests that the way anthropogenic change is imagined, defined, and experienced has crucial implications for transnational flows of capital, knowledge, and social recognition.

Anthropogenic climate change has possibly surpassed biodiversity loss as the most widely recognized form of global transformation. The anthropology of climate change, as envisioned by Crate and Nuttall (2009), stresses protecting and respecting local cultures in the face of this phenomenon when it comes to adaptations, unpreventable impacts, and disasters. These scholars exemplify an action-orientated stance towards change, calling for anthropological engagement that can make local challenges visible aspects of international policy. Within this mode of research, also known as ‘climate ethnography’, anthropologists have a responsibility to explicate the local effects of global transformation in order to fill in gaps in Western scientific knowledge about anthropogenic change (Crate 20082011).

In a related vein, scholars like Lazrus and Rudiak-Gould have helped carve out a niche for an anthropological engagement with small island communities in the context of anthropogenic climate change. Lazrus (2012) argues persuasively that climate change has altered conditions for life in small islands, affecting islanders through a number of key environmental shifts, but also through the enactment of adaptive policies that circumscribe the sovereignty of affected peoples. For Lazrus, anthropological responsibility lies in reconfiguring international institutional understandings of island vulnerability so that islanders are not assumed to be inherently vulnerable. For Rudiak-Gould (20102013), climate change in small island states is both an issue of translation between international scientists and island citizens and a question of seeing the material consequences of change in islander environments. He argues that scientists can learn from island people when they examine how the information they present has been reinterpreted in local idioms. Scientists are then forced to see the ‘humanistic dimensions of this geophysical phenomenon’ (2010: 53) and to respond to material realities of change that may not be readily visible from their data sets or regional climate models (2013). For both scholars, the anthropologist’s task is to help find meaning in forms of change that combat scientific hegemony and colonial legacies.

Continuing the discussion, many scholars have advocated for more of a second-order perspective for the study of climate change (Lahsen 2005; Moore 2010b; Tsing 2005; Whitington 2012). For example, Lahsen (2008) is adamant that anthropologists should study those who populate the centres of power and generate knowledge and policy about the phenomenon itself. She argues that scientists, administrators, journalists, and officials do as much to shape climate change as an idea, discourse, and powerful frame for thought and action as do the marginalized peoples of the world. Along these lines, Barnes et al. (2013) have argued that engagements at this level allow for an understanding of the cultural dimensions and micro-dynamics of decision-making about climate processes and policies, and therefore for anthropological influence to be felt amongst people in positions of power.

Other topics for the anthropology of global change have included work on the scientific rationales and social realities of invasive species eradication strategies (Fortwangler 2009; Moore 2012); the critical analysis of spatial productions in the name of environmental change such as protected areas (West, Igoe & Brockington 2006); criticism of the crisis rhetoric of global change as an excuse to appropriate land and resources in carbon trading strategies (Fairhead, Leach, & Scoones 2012), and arguments about the nexus between ecological knowledge production and market-based extractive practices (Davidov 2012). Although this is by no means an exhaustive collection, these examples show the scope of recent anthropological work that takes on the idea of anthropogenic change in an era of planetary framing. But what about anthropological work (including sympathetic disciplines) that explicitly engages the Anthropocene idea as a social fact and material reality?

Anthropological writing that explicitly tackles the idea of the Anthropocene itself is relatively few and far between (though rapidly growing), but Carrithers, Bracken, and Emery (2011) use the term to label a ‘master narrative’ of endangerment, extinction, and crisis that helps dictate the social placement of species in the world of species protection and valuation. Sympathetically, Ogden et al. (2013) argue that it is crucial to study geopolitical outcomes tied to the transnational institutionalization of discourse and practice in the name of the Anthropocene, what they call global socioecological assemblages (following Ong & Collier 2005). They use the concept of global assemblages to describe market-driven, transnational environmental governance emerging as a means of managing life processes. Also emphasizing governance, Lovbrand, Stripple, and Wiman view the Anthropocene as a ‘central system of thought mediated by Earth System Science’ (2009: 10) new forms of research such as coupled natural and human systems. These projects then become ‘new political space(s) for government intervention’ (2009: 11). Going further, Howe (2014) describes (in the context of industrial alternative energy farms) how both experts and local people assert authoritative and ethical claims in the context of Anthropocene futures. ‘Anthropocenic ecoauthority’ therefore consists of ‘experiential, scientific and managerial truth claims’ about environmental knowledge (2014: 383).

As this work on various aspects of global transformation shows, anthropologists are situated to observe how the Anthropocene idea amalgamates multiple forms of anthropogenic change into an argument about the distinction of the contemporary world. Anthropology also shows that we must remain conscious of the multiple materialities entangled in this emergent cosmological ordering of reality. For example, Larkin (2013) points us towards the infrastructures that materially mediate much of the human relation to the nonhuman world. According to him, infrastructures are more than technical objects – they are poetic, semiotic, and aesthetic, constituting subjects and citizens while embodying the ‘collective fantasy of society’ (2013: 329). An anthropology for the Anthropocene would be attuned to the ‘politics and poetics’ of the material interventions made in the name of global change along with the political ecologies, discursive productions, modes of governance, justice, authority, and expertise that combine to constitute our planetary present.

Anthropocene anthropology

I see the Anthropocene as the most recent iteration of the positive feedback cycle producing ideas about planetary change: the more researchers and policy-makers promote anthropogenesis as a global issue with political stakes and the more transnational action takes place in its name, the more we will see shifts in understandings of global transformation, sociality, ecology, and landscape (or marinescape) formations on multiple levels. These will in turn inspire new alliances and materializations. We require frameworks that allow us to recognize the components and effects of this Anthropocene feedback cycle while they help reproduce locations like the Bahama Islands.

Returning to my anthropological puzzle in The Bahamas, I would like to propose concepts for the exploration of ‘Anthropocene spaces’ – the complex conjunctures that I hope will become the subject of an Anthropocene-aware anthropology. The puzzle of The Bahamas requires analytical categories and concepts – a framework – that can reframe global change and the Anthropocene idea as an anthropological object. For starters, global change predictions, driven by the work of scientists from the Intergovernmental Panel on Climate Change (IPCC) and others, have had far-reaching influence in the creation of political alliances for the Anthropocene. As I mentioned above, The Bahamas is a member of AOSIS at the United Nations. The forty-four AOSIS member nations come from all the ocean regions of the world, and the group now describes itself as ‘a coalition of small island and coastal countries that share similar development challenges and concerns about the environment, especially their vulnerability to the adverse effects of global climate change’ (Alliance of Small Island States 2013). The milieu in question within AOSIS is the small island, now thought of as an object about which it is possible to make a number of truth claims about its social, economic, and environmental fragility in the face of anthropogenic planetary change. Anthropocene political objects are scalable in the Bahamian context from particular islands, to the island nation, to the Caribbean island region, to the planet itself as a fragile ‘earth island’. Further, the forms of subjectivation available for island residents in The Bahamas now include the climate change refugee, facing the future possibility of ‘heading for the hills of Haiti’9 as the everyday experience of coastal erosion and sand replenishment is publicly linked to global change. AOSIS is one example of an alliance that hopes to promote small island subjectivity while facilitating transnational island adaptation measures.

To approach these political moves, the anthropological engagement of the Anthropocene requires a scope beyond the molecularization of recent work on bioscience (Rose 2006) and the sovereign anthropocentrism of concepts like biopower and biopolitics (Povinelli 2014; Rabinow & Rose 2006). These concepts must be remediated to speak to the Anthropocene as a social category that positions the nonhuman and biogeochemical processes as integral to the political understanding of life. To do this I borrow from Olson (2010), who coined ‘ecobiopolitics’, a concept acknowledging techniques of knowledge production and governance that focus on the milieu between environmental and human processes for the optimization of the milieu itself. Ecobiopolitics focuses attention on scientific and political strategies towards anthropogenic change that manage the idea of planetary ‘habitable space’ across scales and methodologically elide human and ecological research. Anthropogenic planetary change then becomes a form of global environmental imaginary within which it is possible for Olson’s understanding of ecobiopolitics to function through ‘truth claims based on knowledge of milieu processes, power relations that take milieus as their object, and the modes of subjecthood and subjectification that designate subjects as milieu elements’ (2010: 181, modifying Rabinow & Rose 2006). The Bahamas’ self-positioning as an AOSIS member signifies the positioning of its islands within an ecobiopolitical mode of knowledge and governance, subjectivation and development.

In light of the country’s commitments to Anthropocene alliances and projects designed to combat its fragility, The Bahamas is increasingly considered a ‘rich source of research’, in the words of a visiting marine scientist at a recent public meeting of the Bahamas National Trust. This means that emergent forms of reason can now be tested there through field research projects enacted by visiting researchers who are commonly conducting integrated ecological and socioeconomic studies about environmental change. One such project I participated in was the Bahamas Biocomplexity Project (BBP), an interdisciplinary amalgamation of researchers studying the archipelago’s marine biodiversity and species connectivity, the distribution of marine habitats, and the socioeconomics of fishing communities to ‘improve the design of networks of marine protected areas’ (American Museum of Natural History 2013). This kind of policy-focused, interdisciplinary work is indicative of the research paradigms attached to the Anthropocene idea in which methodologies are consciously designed to speak to ‘big picture’ issues of anthropogenic global change within ‘linked human and natural systems’ as opposed to studies of molecular or genetic processes in isolation (Colwell 1998). My time with the BBP was spent administering surveys to members of Bahamian fishing communities, catching answers as-catch-can on boats, dock benches, car rides, and at kitchen tables. As a member of the social science arm of the project, I had no field interactions with the biological teams collecting oceanographic, biological, and spatial data elsewhere in the archipelago. I came to realize that, methodologically, such teamwork often follows different patterns in space and time depending on the target of research: human or nonhuman, living or nonliving physical processes.

How should we characterize the forms of reason that anchor such ‘big picture’ research methodologies? I argue that within projects such as the BBP or the CCI (mentioned above), socioecological forms of institutional reason – what I label ‘socioecologics’ – frame human/environmental/nonhuman relations as coupled systems united in explanations of earth system dynamics and resource management planning. Some examples of socioecologics include complex adaptive systems theory (Holling 2001) and socioecological systems theory (Anderies, Janssen & Ostrom 2004; Berkes 2003). Popular socioecologics reframe research scope and method, creating novel interdisciplinary projects, but the form of socioecological projects can amplify or ameliorate disciplinary disparities and divides between researchers and the human and nonhuman others who inhabit the field. In other words, investigations of the Anthropocene idea must be aware of the form of socioecological reason that delineates thought and action around specific Anthropocene projects within a particular ecobiopolitical milieu.

In terms of other modes of human/nonhuman relation such as the process of reproducing a Bahamian export product through MSC certification, we must remember that commodity certification transforms the relationships of production between groups of people and between people and the things they produce (Bestor 2001; West 2010). These processes alter human and nonhuman beings in ways that make them amenable to recent Anthropocene markets. Sea creatures with a mottled carapace that are known as ‘crawfish’ in The Bahamas and sold as generic (but luxurious) white-fleshed ‘lobster’ in the United States and Europe are being moulded into ‘Spiny Lobster’, becoming scientifically measured and assessed as ‘stock’ that can be studied and rebranded at national and global levels.10 Fishers, too, are moulded into ‘stakeholders’ within the MSC system, continuing a process of fishery reorganization under the sign of global conservation begun in the 1980s and 1990s. The president of the Bahamas Marine Exporters Association has said that ‘with major supermarket chains in the US and Europe committed to buying only from countries that can prove their fisheries are sustainable, we realized MSC certification would be required to maintain market access for the Bahamian Spiny Lobster. This led to the rapid and wholehearted transition of the fishery’ (cited in Isaacs 2011).

An analytic beyond the human is useful here for understanding more than the co-constitution of biogeochemical processes and research project design. Anthropological attention to the emergent objects of knowledge, governance, and forms of reason adapted to the Anthropocene idea must also acknowledge the embodied relations that produce fisheries and creatures like Spiny Lobster and fishers. Tsing argues that the idea of human exceptionalism blinds us to the interspecies connections that make up our own lives within our bodies and in our surroundings (Tsing 2012; in homage to Haraway 20032008; and Kirksey & Helmreich 2010). Human species-being (the sense of human nature that concerns Chakrabarty [2009] in the Anthropocene) is not autonomous but is instead comprised of relations with other organisms moving within geochemical processes held together by diverse forms of dependency and love. Anthropocene ecobiopolitical and socioecological configurations (such as alliances based on geography, global science, resource management, etc.) manage humanity, geology, and biology in multiply produced landscapes that affect notions of value and relations of production and reproduction stretching from global markets to the state to the locality. Tsing refers to these networks as interspecies relations, but I call them ‘earthly relations’, as a reminder that there are ‘non-living’ components to consider when thinking about life (e.g. planetary geophysical processes, the ‘resonance’ of stones, and the movement of water [Ingold 2011; Kohn 2014; Raffles 2012]).

Within the assemblages and markets animated by the Anthropocene idea, there are myriad circulating stories that deserve anthropological attention. Examples of Anthropocene stories include the IPCC global change narratives that bind AOSIS members or the narratives of overfishing that link all fisheries in a global saga of anthropogenic decline. And, arguably, the task of the Anthropocene Working Group (see above) is to construct a plausible story about planetary change. Authoritative stories frame protagonists, perpetrators, and victims (human and nonhuman), and they help lay the groundwork that makes economic ventures like MSC certification or sustainable tourism viable in places like The Bahamas. While an attention to narrative may appear to abandon a commitment to material processes, I argue that such stories help constitute ecologies and socialities by bringing them into new kinds of socioecological and ecobiopolitical (earthly) relation.

The narrative power of what Latour (2013) has called ‘geostories’ is a useful analytic with which to tackle these circulating tales. Geostories reflect socioecological arguments about global change in narratives that stem from the teleologies of the earth sciences. They are meant to be accessible tales about the stakes and exceptionalism of the Anthropocene. Geostories simultaneously perpetuate ecobiopolitical discourses around global change – discourses that attempt to ‘reframe Anthropos’ (Palsson et al2013: 4) by narrating the Anthropocene as an effect of human species-being. Often these kinds of geostories can, in the words of Malm and Hornborg, obscure attention to the owners of the means of production who came to power out of a ‘constellation of a largely depopulated New World, Afro-American slavery, the exploitation of British labor in factories and mines, and the global demand for inexpensive cotton cloth’, which led to the rise of the steam engine and from there to our fossil-fuel-based economies (2014: 63). Even Chakrabarty (2013) contends that speaking about the collective ‘we’ of humanity should not imply that ‘we’ are politically one. As Latour (2013) points out, geostories are not harmonious tales but are instead tumultuous and crisis-ridden, steeped in the unknown.

Finally, I have observed that building models for living (and for tourist visitation) in locales such as The Bahamas involves struggle and negotiation between authorities and between authorities and marginalized groups. For example, the spread of marine reserve networks and the rebranding of Bahamian islands in speculative sustainable development markets align the country with global trends: transforming landscapes, infrastructures, and built environments to conform more obviously with prevailing concerns over greening and global change. Such Anthropocene worlding experiments (Roy 2011) can deepen social inequalities by appropriating space from coastal communities, and design models can also be misappropriated. An attention to designers and their plans for development, to resource management, scientific research, exploration projects, to the technologies that enable us to ‘see’ global change, and to various green markets and products will help open Anthropocene assemblages to scrutiny and intervention when necessary.

Therefore, I think an attention to design should be a major component of analysis as the thread that unites the interrelated themes of this framework and points us towards action. If, as proponents of the Anthropocene idea argue, the recognition of anthropogenic planetary change calls for the refashioning of human and nonhuman life on earth, then extreme care must go into redesigning ecobiopolitical configurations, socioecological forms of reason, and viable earthly relations on multiple levels (Latour 2008). The Anthropocene commitments of scientists, governments, and developers are already leading to emergent geostories and brand platforms that designers must draw together in their (co-)creations.

The interrelated concepts that I have chosen to help me explore my Bahamian anthropological puzzle – ecobiopolitics, socioecologics, earthly relations, geostories, and design – represent an amalgamation of environmental anthropology, critical science studies, and political ecology applicable to the evolving twenty-first-century concern with global change known as the Anthropocene. Such analytic reorientations help anthropologists explore events animated by the Anthropocene idea, from emergent political alliances and spatializations to modes of subjectivity and citizenship, from forms of scientific objectification and naturalization to shifting research methods and narratives, from green markets, products, and flows of capital to the materialization and embodiment of these ideas in spaces, places, bodies, and earthly relations. I contend that such recognition helps us identify how emergent ideas contribute to asymmetries and pervasive inequities, allowing anthropologists to intervene in arenas that were previously unavailable for thought. Further, recognizing the ways these conceptual arenas interrelate allows us to grasp the creativity and generativity of contemporary global change assemblages.

Conclusion

The International Geological Congress still has some time to deliberate before it rules on the ‘official’ designation of the Anthropocene. Official agreement on the existence of the Anthropocene as a geological category will not instantly change the way most of us think about planetary anthropogenesis. However, I believe it will spark further debate over the parameters of contemporary global change, inspiring more institutional initiatives and scientific engagement with policy. In other words, the Anthropocene feedback cycle could grow even more acute.

As these events unfold, anthropologists will certainly continue to respond to the social and material realities of global change, and, critically, to the Anthropocene idea itself as an important contemporary object and problem. I have argued that The Bahamas is one example of an emergent ethnographic area within the problematic of an ‘Anthropocene space’. Despite the fact that this seems to fly in the face of the Anthropocene as a planetary and temporal imaginary, it is now clear that global imaginaries and categories have powerful material and symbolic implications, contributing to the reproduction of particular locations, places, and scales. As Tsing has stated, ‘[W]e can investigate globalist projects and dreams without assuming that they remake the world just as they want’ (2000: 330). Anthropocene spaces like small islands are but one position from which anthropologists can begin to think the Anthropocene. And these spaces need not only be geographical locations, but they can also be locations of novel conservation interventions and laboratory situations, such as experiments in geoengineering, re-wilding, or de-extinction. I believe my conceptual bundle could handily be applied in these situations, with a great deal of room for modification and addition.

The work of an Anthropocene anthropology is needed in order to counter and complement the sciences of the earth system and global change research. Following Lovbrand et al., I think it is anthropology’s responsibility to ‘investigate the new forms of power, authority, and subjectivity formed within everyday practices of its own scholarship’ (2009: 12) as anthropologists are integrated further into interdisciplinary and transdisciplinary global change studies. Towards that end, frameworks like the one presented here can ground ethnographic engagement and collaboration and inform the task of reflexively ‘Writing Earthly Relations’ in the Anthropocene.

My research is slanted towards the products of travelling scientists, elite authorities, and green designers who mediate, circulate, and sell the Anthropocene idea in The Bahamas, and indeed these have been my primary informants over the years. However, I think this framework could be attuned towards less overtly ‘authoritative’ events and instantiations of Anthropocene ideas. Further, I hope I have shown that it is not only anthropogenic change that has material effects, as has been so thoroughly demonstrated by the sciences, but that the politics, forms of reason, relations, and narratives that the Anthropocene idea inspires are also materialized in ways that must be acknowledged and explored.

As I stipulated in the introduction, the background argument of this article has been that anthropology must retain its critical stance when confronted by institutional framings of global change. Again, along with Sayre, I call for a continued attention to science-based policy prescriptions that seek to limit the conceptualization of and possible responses to global environmental change. In other words, we must not participate in the erasure of real opportunities for justice and ethical awareness.

In closing, I ask, how ephemeral are the ideas that constitute today’s ‘ephemeral islands’? Despite the fact that there are anthropologists who consider the Anthropocene to be a trend-of-the-moment buzzword, I think that the Anthropocene idea as a problem space that configures locations around evolving notions of global change and human/nonhuman relations will stay with us for some time to come. There is too much political urgency and institutional attention attached to the idea for it to go quietly. I hope an Anthropocene anthropology will be there to help explore the multiplying puzzles of the epoch.

NOTES

1 Following Rabinow (2003) and Rabinow & Marcus (2008) on problematization and the contemporary.2 The Anthropocene idea is of recent origin, but the arguments leading up to its coining and conceptual coalescence have deep roots in transnational events of the last forty years and beyond with the creation of ‘the environment’ as a political category and its subsequent globalization. Parsing this history is not the goal of this article (but see Fortun 2001; Worster 2008).3 The Bahamas is also a British Commonwealth country and member of the Caribbean Community (CARICOM).4 The irony comes from the fact that Bahamians publicly debate the ‘Haitian problem’ of the illegal immigration of Haitians to The Bahamas.5 For more on the ‘start date’ controversy, which is beyond the scope of this article, see Ruddiman (2013).6 In general geochronology, an age is defined as an interval of several million years, an epoch is tens of millions of years, a period is somewhere between an epoch and an era, an era is several hundred million years, and an aeon is at least an interval of a half a billion years.7 The International Geological Congress (IGC) has been meeting since 1878 in three- to five-year intervals (IUGS 2009). The next meeting is in South Africa, in 2016, where the latest evidence for the existence of the Anthropocene will be marshalled by the Anthropocene Working Group to be voted on by the International Commission of Stratigraphy (ICS), the keepers of the geological timeline. The Anthropocene Working Group of the International Union of Geological Sciences and ICS is made up of approximately twenty-nine member scientists from fourteen countries (the United States, Spain, Germany, the United Kingdom, Switzerland, Brazil, Kenya, France, South Africa, Australia, Norway, Austria, Canada, and China). The disciplinary background of members includes archaeology, chemistry, geology, earth systems, and the earth sciences.8 Anthropologists have long concerned themselves with the impacts of humans on their environments as a historical and evolutionary question, and this is far too expansive a conversation to describe here. In this article, I am focusing on the Anthropocene idea as it is used by scientists today and as it is becoming popularized in the social sciences. This is a culturally specific idea of recent origins, and I am interested in investigating its current uses, implications, and materializations.9 For a discussion of climate refugees, see Collectif Argos (2010), McAdam (2009), and McKee (2011).10 The Bahamian lobster industry is many decades old, but MSC certification is a new iteration. MSC certification also comes with increased licensing requirements and the ability to trace catch back to specific fishing boats, allowing for greater ‘transparency’ in the market.

Biography
  • Dr Amelia Moore is a sociocultural anthropologist with interests in environmental anthropology, Caribbean anthropology, science and technology studies, and the anthropology of tourism.  She currently works in The Bahamas, with a focus on the socioecological worlds of small island life in an era of global anthropogenic change.
REFERENCES

Artificial Stupidity and Artificial Intelligence in the Anthropocene


Bernard Stiegler

23 November 2018, Institute of Ereignis, Shanghai

For anyone wanting a precise analysis of what we refer to today as artificial intelligence, which seems now to have become the horizon of everyday life (and I will return to this question), it is necessary to begin from the following postulate: all noetic intelligence is artificial. This implies that there is such a thing as non-noetic intelligence. And it also implies that, generally speaking, noetic life is intelligent in a specific way, which is that of artifice.

I claim that there is non-noetic intelligence in the sense implied when Marcel Détienne and Jean-Pierre Vernant talk about metis, but also in the sense invoked by Kevin Kelly when he wrote an article that presented forms of life, of whatever kind, as forms of intelligence, where each of these forms has evolved in a different way over the last three billion years or more. Speaking in this way is for Kelly a matter of opposing what he calls the myth of super-intelligence, but it is also to speak against Descartes: it is to posit that life is never just machinic – and here we should also mention Georges Canguilhem’s ‘Machine and Organism’.1

Intelligence, here, whether in its ‘natural’ or ‘artificial’ forms, but I prefer to say in its organic or organological forms (I will clarify this a bit later on), is the accomplishment of a goal or an aim. There is no necessity at all for this goal to be a conscious representation, as Francisco Varela shows in a drawing in which he ridicules this kind of ‘representational’ hypothesis. What is involved with noetic intelligence, however, is, in principle, access to consciousness, insofar as it has the capacity to access what Heidegger called the as such – Heidegger being himself someone who deconstructs the metaphysics of representation. Intelligence, whether noetic or otherwise, is in a general way what orients behaviour: it constitutes an animation, as Aristotle will say in On the Soul, in which vegetative, sensible and noetic souls draw intelligence from what he calls the ‘first unmoving mover’, and where the intelligence that is the soul is above all movement, which is also to say, phusis.

In order to precisely distinguish (without opposing) the organic (vegetative and sensible) forms of intelligence from the organological (noetic) forms, we must firstly recall what Aristotle remained unaware of, namely that, some three million or so years ago, there arose the conditions for what would later, some forty thousand years ago, become noetic intelligence, in which Georges Bataille would recognize himself, and in relation to which he said: here it is we who begin, those who painted these animals are our ancestors, our father, this is evidently so, it is obviously so, and recognizing this evidence is a key feature of noesis itself. Here is exactly what he writes in Lascaux, or The Birth of Art:

It is ‘Lascaux man’ about whom we can surely say, and for the first time that, making works of art, he evidently resembled us, he was one of us, our fellow man.2

Bataille will go on to say that the kind of intelligence involved in the work of art is the intelligence of play – I will not develop this point now, but it is fundamental in order to understand what it means for the question of noetic imagination (and I will discuss this next year in Hangzhou). Having said this, we can begin to understand why what we today refer to as artificial intelligence is a continuation of the process of the exosomatization of noesis itself, such as it begins firstly with fabricating exosomatization, making things by hand, and continues with hypomnesic exosomatization, as that which makes it possible to access lived experiences of memory and imagination, which have accumulated since the origin  of the play of works, as Bataille considers them, and which engender, in passing through writing, instruments of observation, calculating machines whose principles were established by Leibniz, and analogue technologies, which form the basis of the culture industries – and here the question of their role in the ‘post-truth era’ arises as never before. All of this then, writing, telescopes, calculating machines and the analogue recording technologies of the culture industries, all of this has generated a perpetual and techno-logical evolution of what Kant called the faculties – whether they are lower, that is, functions of noesis, or whether they are higher, and thereby constitute faculties in the sense we refer to them in universities, and which regularly enter into conflict.

Why do such conflicts arise? Because there are exosomatic evolutions of the hypomnesic supports of noesis, and this generates tensions – which can be social as well as noetic.

Two years ago in Nanjing, I tried to show (and I will come back to this next year) that what Kant called the lower faculties – intuition, understanding, imagination and reason, which are put to work by the higher faculties that are those of knowing, desiring and judging – are functions that are produced through the process of their exteriorization, which Hegel was already able to see, but without truly seeing it. It is Marx who will be the first to understand this, and it will then be reformulated by Lotka, who will do so from a biological standpoint and by coining a new term: exosomatization, or exosomatic evolution and exosomatic organs. Here, the intelligence of the body is produced in being supplemented, inasmuch as it makes possible an exteriorization of experience, and the constitution of what I call (using Husserlian terminology) collective secondary retentions: the latter are retained in individual memories, but they are retained there collectively, forming what we also refer to as knowledge, which can be transmitted from generation to generation, and which metastabilizes the conditions of life – these conditions of life being negentropic, that is, struggling against the entropic effects of human behaviour, which is something we discover in the Anthropocene, through the analysis of what the IPCC calls anthropogenic forcings, which fundamentally threaten life, and in particular noetic life – life that is worthy of being lived by a noetic soul. All of this is what leads to a life that is unworthy of noesis – and ultimately becomes incompatible with life as a whole, as the 15364 signatories of a recent scientific text declare.

It is in this context, at the end of the Anthropocene – and these scientists indeed tell us that it is reaching its end, which must then also be ours – that we see the advent of artificial intelligence as an ordinary reality of everyday life. What then should be the function of what is today called ‘artificial intelligence’, where this refers to a technology of reticular, ubiquitous super-computing that automates the majority of processes by which behavioural flows are managed, where this has fundamental effects on both modes of production and modes of exchange in all their forms, and where, in its current stage, these have been transformed into functions of consumption?

What we today call artificial intelligence is not what was on the horizon of the Macy conferences, the project of which was formulated in Dartmouth by Marvin Minsky with Claude Shannon, Allen Newell, Herbert Simon, and so on. It is a reticular AI, based on what Clarisse Herrenschmidt has called reticular writing, which is linked to the networking together of three and a half billion individuals – via an apparatus that becomes exosopherical, constantly evolving, and now based on the ‘platform capitalism’ described by Benjamin Bratton – and that makes possible the production and exploitation of what I call ‘digital pheromones’.

The possibility of such digital pheromones was in a way already raised by Norbert Wiener in 1948, when he worried about the possibility that cybernetics could give rise to what he called a ‘fascist ant-state’.3 That the human could regress to the stage of the ant is a possibility contained in the fact that this human abandons his knowledge – his knowledge being the path by which he must struggle against entropy. That such a possibility exists, that is, that cybernetic exosomatization can generate an industrial artificial stupidity, is the question that must guide us here. As soon as intelligence becomes artificial, that is, as soon as it is made possible by artefacts and makes these artefacts possible – due to that astonishing faculty of dreaming which, according to the palaeo-anthropologist Marc Azéma, characterizes the human being: he posits that man dreams, as do animals, but that he also does so by producing, drawing and writing, by day-dreaming, such an ex-pression being the beginning of a process of exo-somatization by which man realizes his dreams. The faculty of dreaming is, then, here the faculty of the realization of dreams, and such is noetic intelligence according to Paul Valéry.

But as soon as it becomes artificial, such intelligence can also generate an artificial stupidity: the pharmakon that is the artifice thereby engendered can lead to regression and to self-destruction. Such artificial stupidity is what Alvesson and Spicer describe as ‘functional stupidity’, in a well-known article that has since become a book – and it also generates what Tijman Shep describes as ‘social cooling’, which John Pfaltz describes as an increase in the rate of entropy in social networks. This artificial stupidity, therefore, is also a technique for the production of lures and traps to in some way deceive humans, but here, beyond stupidity, we must also refer to the necessity of putting faults or accidents into music, as was the case with software created by IRCAM, which produced only absolutely ‘right’ notes – for example for the Queen of the Night aria in Mozart’s The Magic Flute – but the ‘music’ this produced was unbearable.

And this is an issue we also see with trading software – which raises the question of vertus and of the necessity of imperfection, that is, the necessity of negentropic locality – which we must interpret via John Stuart Mill and the necessity of diversity. Artificial stupidity also means cognitive overflow syndrome, that is, the functional destruction of attention, or, again, it is what worries Adam Smith in 1776 in The Wealth of Nations.

The possibility of artificial stupidity is what characterizes artificial intelligence, which, as we have already said with Kevin Kelly, can be distinguished from natural intelligence. Natural intelligence cannot commit acts of stupidity: it can only fail, which means, ultimately, to die. Taking up a thesis of Nick Bostrom – but we could also refer here to Bergson, who thinks intelligence in terms of a relation to action – Kelly himself argues that life in general amounts to a series of conquests of intelligence. He argues this while criticizing the perspective of those he calls ‘singularitans’, who maintain five assumptions which, when examined closely, are not based on any evidence.4

The first of these ‘misconceptions’, and the most common, begins with the common misconception about natural intelligence. This misconception is that intelligence is a single dimension. Most technical people tend to graph intelligence the way Nick Bostrom does in his book, Superintelligence – as a literal, single-dimension, linear graph of increasing amplitude. At one end is the low intelligence of, say, a small animal; at the other end is the high intelligence, of say, a genius – almost as if intelligence were a sound level in decibels […] with fish evolving into reptiles, then up a step into mammals, up into primates, into humans, each one a little more evolved (and of course smarter) than the one before it.

So the ladder of intelligence parallels the ladder of existence. But both of these models supply a thoroughly unscientific view. […] A more accurate chart of the natural evolution of species is a disk radiating outward, like this one first devised by David Hillis at the University of Texas and based on DNA. […] Every one of these species has undergone an unbroken chain of three billion years of successful reproduction, which means that bacteria and cockroaches are as highly evolved as humans.

Into this ‘mandala’, however, we must also introduce the perspective of Alfred J. Lotka, for whom ‘natural’ intelligence becomes ‘artificial’, which is also to say, discovers the possibility of its own stupidity, as highlighted by Arnold Toynbee – when the morphogenesis that is endosomatic organogenesis continues outside wet tissue, and does so as exorganogenesis. The latter generates exosomatic organs that modify the trajectory of motor acts, such as occurs with the flint tool, some of which are arrows capable of travelling at 350 kilometres per hour, and today’s rockets, which launch themselves to escape velocity – twenty-eight thousand kilometres per hour – are the continuation of this capacity in a direction that opens up exospherical spaces. But in addition, these exosomatic organs also engender accumulations of psychic retentions, which thereby become collective and constitute what Roger Bartra calls an ‘exocerebrum’ and what Karl Popper calls World Three and objective knowledge.

This third world, however, is the world of what I call hypomnesic tertiary retentions, a world composed not just of exosomatic organs but of retentional accumulations, and where Lotka shows that these are orthogenetic, that is, bearers of non- Darwinian selection processes, making possible the establishment of scalar relations between different orders of magnitude, something completely different from, for example, relations between cells, organs, bodies, milieus and so on. Here we should really turn to Durkheim and to his book, The Elementary Forms of the Religious Life, in which he studies totemism, but I no longer have time to do so now. But we should also note that échelle as ladder, which is also the ladder dreamed of by Jacob, who has a primordial role in Judaeo-Christian monotheism, then becomes échelle as scale, and technologies of scalability are at the heart of those ‘economies of scale’ characteristic of the industrial and capitalist stage of exosomatization. Furthermore, platforms that utilize and develop reticulated artificial intelligence are based on specific technologies of scalability, managing multi-scale data ranging from infra-organic medical ‘nanomachines’ to exospherical infrastructures capable of handling medical data at the scale of the technosphere.

It is worth noting that it is on the basis of totemic classification that Durkheim posits that the Aristotelian and Kantian theory of the categories should be completely rethought. Now, the biosphere may be one scale located within the cosmos. But to this we must add the fact that, from the moment such changes of scale and arrangements of orders of magnitude arise, which is something that occurs with the exosomatic organs that are technical objects in all their forms (including language), from this moment, this biosphere becomes a technosphere. Within this technosphere, moreover, entropy, negentropy and anti-entropy, whose local equilibriums had metastabilized over the course of three or four billion years, find themselves totally overthrown by those exosomatic organs that are pharmaka, that is, organs that can as easily increase entropy as contain it, defer it and transform it through the ‘art of living’, as Alfred Whitehead put it. And the function of artificial intelligence is to in this way minimize entropy and increase negentropy and anti-entropy.

Artificial stupidity, then, is what persists in accelerating entropy instead of deferring it, and does so by destroying knowledge, which, alone, is capable of generating positive bifurcations. It would be entirely possible to take advantage of the analytical possibilities of algorithms in order to defer entropy. But in order to do so, it would be necessary to modify data structures, to press algorithms into the service of the constitution of deliberative scales reconstituting neganthropic knowledge, that is, dialogically transindividuated knowledge, and to make automation serve disautomatization within the framework of a new macro-economy in which value would be defined according to the increase of negentropy. In the current model, however, the criteria of value are entropic.

Behind this question, there are those of the relationships between calculability, locality, incalculability and deliberation – which is equally to say, those of the relationships between understanding, imagination and reason. In Automatic Society, I have argued that algorithms constitute a hypertrophy of the understanding – and that the latter is always artificial, and based on tertiary retentions inasmuch as they configure the schematism and the categories. These questions of epistemology and technology, of the industrial future and new macro-economic models, must all be brought together. It is precisely in order to do so that a program is currently under development in the Plaine commune territory, in the northern suburbs of Paris. And in terms of the question of macro-economics – which is also a question of the function of knowledge and therefore of the episteme in Foucault’s sense and of epistemology in Bachelard’s sense – it is an attempt, in the epoch of algorithmic and articulated artificial intelligence, to draw conclusions from Marx’s statements about fixed capital and the general intellect in the Grundrisse.

I argued earlier that with Kelly’s model, inspired by Hillis, it is necessary to specify the conditions of the passage from natural intelligence to artificial intelligence. I would like to conclude by adding some further remarks on this point.

  1. We must think this passage both with Whitehead and with Canguilhem, with respect to biology for example, and more generally with respect to the role of knowledge in the technical form of life, and as a vital function that can be thought only starting from biology, but precisely as what requires that which is no longer only biological, and which leads Georges Canguilhem to make statements that are quite close to being post- Darwinian and very close to those of Lotka concerning orthogenesis.
  2.  We must specify the question of metis and distinguish it from noesis: cognition, in the sense that this word has in the so-called ‘cognitive sciences’, is not knowledge in Popper’s sense. The passage from cognition to knowledge requires an exosomatic exteriorization and the constitution of what Leroi-Gourhan calls a third kind of memory, very close to what Popper calls World Three, and what I myself call the epiphylogenesis that forms with the accumulation of tertiary retentions. It is this question of exosomatization that Kelly completely ignores when he writes that:

We contain multiple species of cognition that do many types of thinking: deduction, induction, symbolic reasoning, emotional intelligence, spacial logic, short-term memory, and long-term memory. The entire nervous system in our gut is also a type of brain with its own mode of cognition. We don’t really think with just our brain; rather, we think with our whole bodies. These suites of cognition vary between individuals and between species. A squirrel can remember the exact location of several thousand acorns for years, a feat that blows human minds away. So in that one type of cognition, squirrels exceed humans. And yet:

Your calculator is a genius in math; Google’s memory is already beyond our own in a certain dimension. We are engineering AIs to excel in specific modes.

But these specific modes are only functions. It is not just a question of functions, but of faculties – if we take it as given that we must rethink the concept of faculty from the exosomatic perspective.

… the faculties are social, and not just psychic, and that is the whole issue involved in the conflict of the faculties.

Here we should read Ignace Meyerson’s Les fonctions psychologiques et les oeuvres, along with Vernant. Now, when Kelly writes that:

In the future, we will invent whole new modes of cognition that don’t exist in us and don’t exist anywhere in biology. When we invented artificial flying we were inspired by biological modes of flying, primarily flapping wings. But the flying we invented – propellers bolted to a wide fixed wing – was a new mode of flying unknown in our biological world.

When Kelly writes this, what he describes is precisely exosomatization, but he does not see it as such, and he does not see in what way it stems from the works produced during the Upper Palaeolithic, upon whose appearance Bataille meditates. ‘To build machines capable of beating humans’: this is the very goal of exosomatization. Why would we bother to make an automobile – or a bow and arrow – if these exosomatic organs were not quicker than humans? Here, however, the question is of noetic functionality. What indeed is noesis? It is what struggles against the perverse effects generated by exosomatization, but always by generating other processes of exosomatization. This is what Freud describes in Civilization and Its Discontents.

But in that case, it is not just a matter of the exosomatization of the exosomatic organisms that we have been ever since the dawn of hominization: it is also a matter of social organizations. And the latter amount to complex exorganisms, composed of the simple exorganisms that we are, which together form social groups of longer duration than the individuals who form them, as is the case for all civilizations. Such complex exorganisms are, however, prone to becoming massively anthropic, and they can therefore collapse, and today, more than ever, the role of politics consists in struggling against this pharmacological tendency.

Kelly eventually points out that the ‘Turing machine’ and ‘the Church-Turing hypothesis’ are misleading:

no computer has infinite memory or time. When you are operating in the real world, real time makes a huge difference, often a life-or-death difference. Yes, all thinking is equivalent if you ignore time.

But this indicates that what matters here are scales of time – as well as scales of space, and hence of speed.

The only way to have equivalent modes of thinking is to run them on equivalent substrates. [The] only way to get a very human-like thought process is to run the computation on very human-like wet tissue.

What is at stake in the organic tissues of humans, that is, what is at stake in their bodies, is, however, their relationship to death, where the locus of this relationship does not just reside within this body, but, precisely, within what I call the noetic necromass, that is, within what Popper called World Three, which means for example the Trinity College library in Dublin, which is being shifted onto new substrates that require a total reconsideration of the conditions of a new era of exosomatic noesis, themselves fundamentally composed of organizations – without which it will be impossible to avoid collapse.

No thought that in fact thinks thinks like any others, and this is what points to the real challenge: anti-anthropic bifurcation is what exceeds all calculation – and the question is the function of calculation and its limit in a neganthropic field, that is, a localized field, whereas the generalization of calculation, and the totalizations to which this generalization gives rise in this or that locality, destroys this locality5 – and this locality is the biosphere itself, in its relation to the cosmos, a question that was opened in these terms by Vernadsky in 1926.

The biosphere is the condition of biodiversity. Today, the question is how to make the technosphere the possibility of a new noodiversity.

Translated by Daniel Ross.

1 Georges Canguilhem, Knowledge of Life, trans. Stefanos Geroulanos and Daniela Ginsburg (New York: Fordham University Press, 2008), ch. 4.

2 Georges Bataille, Prehistoric Painting: Lascaux, or The Birth of Art, trans. Austryn Wainhouse (Geneva: Skira, 1955), p. 11, translation modified.

3 Norbert Wiener, The Human Use of Human Beings: Cybernetics and Society (London: Free Association Books, 1989), p. 52.

4 Kevin Kelly, ‘The Myth of a Superhuman AI’, Wired (25 April 2017), available at: <https://www.wired.com/2017/04/the-myth-of-a-superhuman-ai/&gt;.

5 The question is: where is the limit of intelligence? Is it not clear that this is a matter of entropy – and of entropy within a finite locality? The limit is not quantitative, according to Kevin Kelly: for example, it is ‘not on a Moore’s law rise. AIs are not getting twice as smart every 3 years, or even every 10 years’. And to shift these limits, Kelly posits that ‘we should engineer friendly AIs and figure out how to instill self-replicating values that match ours’. But the question is here the categorization that is accomplished along with the algorithmic => a new ‘transcendental deduction’ of algorithmically generated categories.

The deep Anthropocene

A revolution in archaeology has exposed the extraordinary extent of human influence over our planet’s past and its future

Lucas Stephens

is a senior research analyst at the Environmental Law and Policy Center in Chicago. He was a specialist researcher at the ArchaeoGLOBE project.

Erle Ellis

is a professor of geography and environmental systems at the University of Maryland, Baltimore County. He is a member of the Anthropocene Working Group, a fellow of the Global Land Programme, a senior fellow of the Breakthrough Institute, and an advisor to the Nature Needs Half movement. He is the author of Anthropocene: A Very Short Introduction (2018).

Dorian Fuller

is professor of archaeobotany at University College London.

Edited by Sally Davies

Humanity’s transition from hunting and gathering to agriculture is one of the most important developments in human and Earth history. Human societies, plant and animal populations, the makeup of the atmosphere, even the Earth’s surface – all were irreversibly transformed.

When asked about this transition, some people might be able to name the Neolithic Revolution or point to the Fertile Crescent on a map. This widespread understanding is the product of years of toil by archaeologists, who diligently unearthed the sickles, grinding stones and storage vessels that spoke to the birth of new technologies for growing crops and domesticating animals. The story they constructed went something like this: beginning in the Near East some 11,000 years ago, humans discovered how to control the reproduction of wheat and barley, which precipitated a rapid switch to farming. Within 500 to 1,000 years, a scattering of small farming villages sprang up, each with several hundred inhabitants eating bread, chickpeas and lentils, soon also herding sheep and goats in the hills, some keeping cattle.

This sedentary lifestyle spread, as farmers migrated from the Fertile Crescent through Turkey and, from there, over the Bosporus and across the Mediterranean into Europe. They moved east from Iran into South Asia and the Indian subcontinent, and south from the Levant into eastern Africa. As farmers and herders populated new areas, they cleared forests to make fields and brought their animals with them, forever changing local environments. Over time, agricultural advances allowed ever larger and denser settlements to flourish, eventually giving rise to cities and civilisations, such as those in Mesopotamia, Egypt, the Indus and later others throughout the Mediterranean and elsewhere.

For many decades, the study of early agriculture centred on only a few other regions apart from the Fertile Crescent. In China, millet, rice and pigs gave rise to the first Chinese cities and dynasties. In southern Mexico, it was maize, squash and beans that were first cultivated and supported later civilisations such as the Olmecs or the Puebloans of the American Southwest. In Peru, native potato, quinoa and llamas were among species domesticated by 5,000 years ago that made later civilisations in the Andes possible. In each of these regions, the transition to agriculture set off trends of rising human populations and growing settlements that required increasing amounts of wood, clay and other raw materials from the surrounding environments.

Yet for all its sweep and influence, this picture of the spread of agriculture is incomplete. New technologies have changed how archaeology is practised, from the way we examine ancient food scraps at a molecular level, to the use of satellite photography to trace patterns of irrigation across entire landscapes. Recent discoveries are expanding our awareness of just how early, extensive and transformative humans’ use of land has been. The rise of agriculture was not a ‘point in time’ revolution that occurred only in a few regions, but rather a pervasive, socioecological shifting back and forth across fuzzy thresholds in many locations.

Bringing together the collective knowledge of more than 250 archaeologists, the ArchaeoGLOBE project in which we participated is the first global, crowdsourced database of archaeological expertise on land use over the past 10,000 years. It tells a completely different story of Earth’s transformation than is commonly acknowledged in the natural sciences. ArchaeoGLOBE reveals that human societies modified most of Earth’s biosphere much earlier and more profoundly than we thought – an insight that has serious implications for how we understand humanity’s relationship to nature and the planet as a whole.

Just as recent archaeological research has challenged old definitions of agriculture and blurred the lines between farmers and hunter-gatherers, it’s also leading us to rethink what nature means and where it is. The deep roots of how humanity transformed the globe pose a challenge to the emerging Anthropocene paradigm, in which human-caused environmental change is typically seen as a 20th-century or industrial-era phenomenon. Instead, it’s clearer than ever before that most places we think of as ‘pristine’ or ‘untouched’ have long relied on human societies to fill crucial ecological roles. As a consequence, trying to disentangle ‘natural’ ecosystems from those that people have managed for millennia is becoming less and less realistic, let alone desirable.

Our understanding of early agriculture derives mostly from the material remains of food – seeds, other plant remains and animal bones. Archaeologists traditionally document these finds from excavated sites and use them to track the dates and distribution of different people and practices. Over the past several decades, though, practitioners have become more skilled at spotting the earliest signatures of domestication, relying on cutting-edge advances in chemistry, biology, imaging and computer science.

Archaeologists have greatly improved their capacity to trace the evolution of crops, thanks to advances in our capacity to recover minute plant remains – from silica microfossils to attachment scars of cereals, where the seeds attach to the rest of the plant. Along with early crops, agricultural weeds and storage pests such as mice and weevils also appeared. Increasingly, we can identify a broader biotic community that emerged around the first villages and spread with agriculture. For example, weeds that originated in the Fertile Crescent alongside early wheat and barley crops also show up in the earliest agricultural communities in places such as Germany and Pakistan.

Collections of animal bones provide evidence of how herded creatures changed physically through the process of domestication. Butchering marks on bones can help reconstruct culling strategies. From the ages and sizes of animals, archaeologists can deduce the populations of herds in terms of age and sex ratios, all of which reveals how herding differed from hunting. Herding systems themselves also vary, with some focused only on producing meat, and others on milk and wool too.

The British Isles were transformed by imported crops, weeds and livestock from millennia earlier

Measurements of bones and seeds have made great strides with technologies such as geometric morphometrics – complex mathematical shape analysis that allows for a more nuanced understanding of how varieties evolved and moved between regions. Biomolecular methods have also multiplied. The recovery of amino acid profiles from fragmented animal bones, for example, has allowed us to discern which animals they came from, even when they’re too degraded for visual identification. The increasingly sophisticated use and analysis of ancient DNA now allows researchers to track the development and distribution of domesticated animals and crops in great detail.

Archaeologists have also used mass spectrometry, a technique involving gas ions, to pinpoint which species were cooked together based on the presence of biomolecules such as lipids. Stable isotopes of carbon and nitrogen from animal bones and seeds give insight into where and how plants and animals were managed – allowing us to more fully sketch out ancient foodwebs from soil conditions to human consumption. Strontium isotopes in human and animal bones, meanwhile, allow us to identify migrations across a single organism’s lifetime, revealing more and earlier long-distance interconnections than previously imagined. Radiocarbon dating was already possible in the 1950s – but recent improvements that have reduced sample sizes and error margins allow us to build fine-grained chronologies and directly date individual crops.

With all these fresh data, it’s now possible to tell a much richer, more diverse story about the gradual evolutions and dispersals of early agriculture. By 6,000 years ago, the British Isles were being transformed by an imported collection of crops, weeds and livestock that had originated millennia earlier in the Near East. Similarly, millet, rice and pigs from central China had been spread as far as Thailand by 4,000 years ago, and began transforming much of the region’s tropical woodland to agricultural fields. New stories are constantly emerging too – including that sorghum, a grain crop, was domesticated in the savannahs of eastern Sudan more than 5,000 years ago, before the arrival of domesticated sheep or goats in that area. Once combined with Near Eastern sheep, goats and cattle, agropastoralism spread rapidly throughout most of sub-Saharan Africa by 2,000 years ago.

Advances in the study of plant silica micro-fossils (phytoliths) have helped trace banana cultivation from the Island of New Guinea more than 7,000 years ago – from where it spread through Island Southeast Asia, and eventually across the Indian Ocean to Africa, more than a millennium before Vasco da Gama navigated from Africa to India. These techniques have also revealed unforeseen agricultural origins – such as the forgotten cereal, browntop millet. It was the first staple crop of South India, before it was largely replaced by crops such as sorghum that were translocated from Africa. Many people might be surprised to learn that the early farming tradition in the Mississippi basin relied on pitseed goosefoot, erect knotweed and marsh elder some 3,000-4,000 years ago, long before maize agriculture arrived in the American Midwest.

Archaeologists don’t just study materials painstakingly uncovered in excavations. They also examine landscapes, patterns of settlement, and the built infrastructure of past societies to get a sense of the accumulated changes that humans have made to our environments. They have developed a repertoire of techniques that allow them to study the traces of ancient people on scales much larger than an individual site: from simply walking and documenting the density of broken pottery on the ground, to examining satellite imagery, using lidar (light and laser) and drones to build 3D models, even searching for subsurface magnetic anomalies to plot out the walls of buried cities.

There was usually a long continuum of exploitation, translocation and management of ecosystems

As a result, new revelations about our deep past are constantly emerging. Recent discoveries in southwestern Amazonia showed that people were cultivating squash and manioc more than 10,000 years ago, and maize only a few thousand years later. They did so living in an engineered landscape consisting of thousands of artificial forested islands, within a seasonally flooded savannah.

Some of the most stunning discoveries have come from the application of lidar around Maya cities, buried underneath the tropical canopy in Central America. Lasers can penetrate this canopy to define the shapes of mounds, plazas, ceremonial platforms and long causeways that were previously indistinguishable from the topography of the jungle. A recent example in Mexico pushed back the time period for monumental construction to what we used to consider the very beginning of Maya civilisation – 3,000 years ago – and suggests the monuments were more widespread than previously believed.

These transitions were not linear or absolute. It’s now clear that there was usually a long continuum of exploitation, translocation and management of plants, animals, landforms and ecosystems well before (and often after) domestication occurred. This makes it harder to draw solid lines between hunter-gatherer and farmer societies, or between societies who practised different subsistence strategies. Over archaeological timescales spanning hundreds to thousands of years, land use can be thought of instead as a tapestry of ever-evolving anthroecosystems with higher or lower degrees of transformation – more or less human-shaped, or ‘domesticated’ environments.

In 2003, the climatologist William Ruddiman introduced the ‘early anthropogenic hypothesis’: the idea that agricultural land use began warming Earth’s climate thousands of years ago. While some aspects of this early global climate change remain unsettled among scientists, there’s strong consensus that land-use change was the greatest driver of global climate change until the 1950s, and remains a major driver of climate change today. As a result, global maps of historical changes in land use, and their effects on vegetation cover, soils and greenhouse gas emissions, are a critical component of all contemporary models for forecasting Earth’s future climate.

Deforestation, tilling the land and other agricultural practices alter regional and global climate because they release greenhouse gases from vegetation and soils, as well as altering the exchange of heat and moisture across Earth. These effects reverse when land is abandoned and vegetation recovers or is restored. Early changes in agricultural land use therefore have major implications in understanding climate changes of the past, present and future.

The main global map of historical land use deployed in climate models is HYDE (the History Database of the Global Environment), combining contemporary and historical patterns of land use and population across the planet over the past 12,000 years. Despite this huge span of space and time, with notable exceptions, HYDE is based largely on historical census data that go back to 1960, mostly from Europe.

HYDE’s creator, a collaborator in ArchaeoGLOBE, has long requested help from historians, scientists and archaeologists to build a stronger empirical basis for HYDE’s global maps – especially for the deep past, where data are especially lacking. The data needed to improve the HYDE database exist, but reside in a format that’s difficult to access – the expert knowledge of archaeologists working in sites and regions around the world. The problem is that no single archaeologist has the breadth or time-depth of knowledge required.

Archaeologists typically study individual regions and time periods, and have only background knowledge on wider areas. Research methods and terminology also aren’t standardised worldwide, making syntheses difficult, rare and subjective. To construct a comprehensive global database of past land use, you need to gather information from hundreds of regional specialists and collate it, allowing this mosaic of individual studies to emerge as a single picture. This was exactly what we did for ArchaeoGLOBE.

Earth’s terrestrial ecology was already largely transformed by hunter-gatherers, farmers and pastoralists

In 2018, we surveyed more than 1,300 archaeologists around the world, and synthesised their responses into ArchaeoGLOBE. The format of our questionnaire was based on 10 time-slices from history (from 10,000 years ago, roughly the beginning of agriculture, to 1850 CE, the industrial era in Europe); 146 geographic regions; four levels of land-use prevalence; and five land-use categories (foraging/hunting/gathering/fishing; pastoralism; extensive agriculture; intensive agriculture; urbanism).

We ended up receiving 711 regional assessments from 255 individual archaeologists – resulting in a globally complete, if uneven, map of archaeological knowledge. After synthesis and careful analysis, our results (along with 117 other co-authors) were published in 2019 in Science. We also made all our data and analysis available online, at every stage of the research process – even before we had finished collecting it – in an effort to stimulate the culture of open knowledge-sharing in archaeology as a discipline.

The resulting data-trove allows researchers to compare land-use systems over time and in different regions, as well as to aggregate their cumulative, global impacts at different points over the past 10,000 years. When we compared ArchaeoGLOBE results with HYDE, we found that archaeological assessments showed much earlier and more widespread agricultural land use than HYDE suggested – and, therefore, more intensive land use than had been factored into climate change assessments. Indeed, the beginnings of intensive agriculture in ArchaeoGLOBE were earlier than HYDE’s across more than half of Earth’s current agricultural regions, often by 1,000 years or more.

By 3,000 years ago, Earth’s terrestrial ecology was already largely transformed by hunter-gatherers, farmers and pastoralists – with more than half of regions assessed engaged in significant levels of agriculture or pastoralism. For example, the Kopaic Basin in the Greek region of Boeotia was drained and converted from wetland to agricultural land in the 13th century BCE. This plain – roughly 1,500 hectares (15 sq km) in size – surrounded by steep limestone hills, had been a large, shallow lake since the end of the last Ice Age. Late Bronze Age residents of the area, members of what we call the Mycenaean culture, constructed a hydraulic infrastructural system on a massive scale to drain the wetland and claim it for agriculture. They channelised rivers, dug drainage canals, built long dikes and expanded natural sinkholes to direct the water off what would have been nutrient-rich soil. Eventually, when the Mycenaean civilisation collapsed at the end of the Bronze Age, the basin flooded again and returned to its previous wetland state. Legend has it that Heracles filled in the sinkholes as revenge against a local king. The area was not successfully drained again until the 20th century.

These examples highlight a general trend we found that agriculture and pastoralism gradually replaced foraging-hunting-gathering around the world. But the data also show that there were reversals and different subsistence economies, from foraging to farming, operating in parallel in some places. Moreover, agriculture and pastoralism are not the only practices that transform environments. Hunter-gatherer land use was already widespread across the globe (82 per cent of regions) by 10,000 years ago. Through the selective harvest and translocation of favoured species, hunting (sometimes to extinction) and the use of fire to dramatically alter landscapes, most of the terrestrial biosphere was already significantly influenced by human activities, even before the domestication of plants and animals.

ArchaeoGLOBE is both a cause and a consequence of a dramatic change in perspective about how early land use produced long-term global environmental change. Archaeological knowledge is increasingly becoming a crucial instrument for understanding humanity’s cumulative effect on ecology and the Earth system, including global changes in climate and biodiversity. As a discipline, the mindset of archaeology stands in contrast to earlier perspectives grounded in the natural sciences, which have long emphasised a dichotomy between humans and nature.

In the ‘pristine myth’ paradigm from the natural sciences, as the geographer William Denevan called it, human societies are recent destroyers, or at the very least disturbers, of a mostly pristine natural world. Denevan was reacting against the portrayal of pre-1492 America as an untouched paradise, and he used the substantial evidence of indigenous landscape modification to argue that the human presence was perhaps more visible in 1492 than 1750. Recent popular conceptions of the Anthropocene risk making a similar mistake, drawing a thin bright line at 1950 and describing what comes after as a new, modern form of ecological disaster. Human changes to the environment are cumulative and were substantial at different scales throughout our history. The deep trajectory of land use revealed by ArchaeoGLOBE runs counter to the idea of pinpointing a single catalytic moment that fundamentally changed the relationship between humanity and the Earth system.

The pristine myth also accounts for why places without contemporary intensive land use are often dubbed ‘wilderness’ – such as areas of the Americas depopulated by the great post-Columbian die-off. Such interpretations, perpetuated by scientists, have long supported colonial narratives in which indigenous hunter-gatherer and even agricultural lands are portrayed as unused and ripe for productive use by colonial settlers.

The notion of a pristine Earth also pervaded the thinking of early conservationists in the United States such as John Muir. They were intent on preserving what they saw as the nobility of nature from a mob of lesser natural life, and also those eager to manage wilderness areas to maintain the trophy animals they enjoyed hunting. For example, the governor of California violently forced Indigenous peoples out of Yosemite Valley in the 19th century, making way for wilderness conservation. These ideas went hand-in-hand with a white supremacist view of humanity that cast immigrants and the poor as a type of invasive species. It was not a great leap of theorising to move from a notion of pristine nature to seeing much of humanity as the opposite – a contaminated, marring mass. In both realms, the human and the natural, the object was to exclude undesirable people to preserve bastions of the unspoilt world. These extreme expressions of a dichotomous view of nature and society are possible only by ignoring the growing evidence of long-term human changes to Earth’s ecology – humans were, and are still, essential components of most ‘natural’ ecosystems.

A clear-eyed appreciation for the deep entanglement of the human and natural worlds is vital

Humans have continually altered biodiversity on many scales. We have changed the local mix of species, their ranges, habitats and niches for thousands of years. Long before agriculture, selective human predation of many non-domesticated species shaped their evolutionary course. Even the relatively small hunter-gatherer populations of the late Pleistocene were capable of negatively affecting animal populations – driving many megafauna and island species extinct or to the point of extinction. But there have also been widespread social and ecological adaptations to these changes: human management can even increase biodiversity of landscapes and can sustain these increases for thousands of years. For example, pastoralism might have helped defer climate-driven aridification of the Sahara, maintaining mixed forests and grassland ecosystems in the region for centuries.

This recognition should cause us to rethink what ‘nature’ and ‘wilderness’ really are. If by ‘nature’ we mean something divorced from or untouched by humans, there’s almost nowhere on Earth where such conditions exist, or have existed for thousands of years. The same can be said of Earth’s climate. If early agricultural land use began warming our climate thousands of years ago, as the early anthropogenic hypothesis suggests, it implies that no ‘natural’ climate has existed for millennia.

A clear-eyed appreciation for the deep entanglement of the human and natural worlds is vital if we are to grapple with the unprecedented ecological challenges of our times. Naively romanticising a pristine Earth, on the other hand, will hold us back. Grasping that nature is inextricably linked with human societies is fundamental to the worldview of many Indigenous cultures – but it remains a novel and often controversial perspective within the natural sciences. Thankfully, it’s now gaining prominence within conservation circles, where it’s shifting attitudes about how to enable sustainable and resilient stewardship of land and ecosystems.

Viewing humans and nature as entwined doesn’t mean that we should shrug our shoulders at current climatic trends, unchecked deforestation, accelerating extinction rates or widespread industrial waste. Indeed, archaeology supplies numerous examples of societal and ecosystem collapse: a warning of what happens if we ignore the consequences of human-caused environmental change.

But ecological crises are not inevitable. Humans have long maintained sustainable environments by adapting and transforming their societies. As our work demonstrates, humans have shaped the ecology of this planet for thousands of years, and continue to shape it.

We live at a unique time in history, in which our awareness of our role in changing the planet is increasing at the precise moment when we’re causing it to change at an alarming rate. It’s ironic that technological advances are simultaneously accelerating both global environmental change and our ability to understand humans’ role in shaping life on Earth. Ultimately, though, a deeper appreciation of how the Earth’s environments are connected to human cultural values helps us make better decisions – and also places the responsibility for the planet’s future squarely on our shoulders.

Original essay here