In light of continuing biodiversity loss globally, one ambitious proposal has gained considerable traction amongst conservationists: the goal to protect half the Earth. Our analysis suggests that at least 1 billion people live in places that would be protected if the Half Earth proposal were implemented within all ecoregions. Considering the social and economic impacts of such proposals is central to addressing social and environmental justice concerns, and assessing their acceptability and feasibility

Fastré, C

Sandbrook, C

Schleicher, J

Vira, B

Visconti, P

Zaehringer, JG

In light of continuing global biodiversity loss, one ambitious proposal has gained considerable traction amongst conservationists: the goal to protect half the Earth. Our analysis suggests that at least one billion people live in places that would be protected if the Half Earth proposal were implemented within all ecoregions. Taking into account the social and economic impacts of such proposals is central to addressing social and environmental justice concerns, and assessing their acceptability and feasibility

Schleicher, J.

Zaehringer, J.G.

Fastré, C.

Vira, B.

Visconti, P.

Sandbrook, C.

International Institute for Applied Systems Analysis (IIASA)

1  Protecting half the planet could directly affect over one billion people  1 Judith Schleichera,*, Julie G. Zaehringera,b, Constance Fastrec, Bhaskar Viraa, Piero Viscontid and 2 Chris Sandbrooka  3 a Department of Geography, University of Cambridge, Cambridge CB2 3EN, UK. 4 b Centre for Development and Environment, University of Bern, Bern, Switzerland. 5 c Institute of Zoology, Zoological Society of London, Regent's Park, London, NW1 4RY, UK. 6 d International Institute for Applied Systems Analysis (IIASA), Schlossplatz 1, 2361 Laxenburg, Austria. 7 * Corresponding author: Judith.Schleicher@cantab.net;   8 2  Abstract 9 In light of continuing biodiversity loss globally, one ambitious proposal has gained 10 considerable traction amongst conservationists: the goal to protect half the Earth. Our 11 analysis suggests that at least 1 billion people live in places that would be protected if the 12 Half Earth proposal were implemented within all ecoregions. Considering the social and 13 economic impacts of such proposals is central to addressing social and environmental justice 14 concerns, and assessing their acceptability and feasibility.  15  16 Main text  17 To halt the rapid loss of biodiversity globally, numerous conservation strategies have been 18 implemented. Member states of the Convention on Biological Diversity (CBD) have 19 committed to placing 17% and 10% of the world’s terrestrial and marine areas, respectively, 20 within protected areas (PAs) by 2020 (Aichi Biodiversity Target 111). Although meeting this 21 target is within reach in many countries2, rapid biodiversity loss continues3. As a result, 22 conservationists have responded with alternative and more ambitious goals. One prominent 23 proposal calls for the expansion of the global conservation estate to cover half the Earth4,5. 24 This Half Earth, or Nature Needs Half, proposal has gained strong momentum, and has the 25 potential to influence the post-2020 biodiversity targets and related processes6. Indeed, the 26 Global Deal for Nature (GDN), which aims for 30% protection by 2030 and 50% by 2050, has 27 been endorsed by a broad coalition of environmental organisations7.  28 Achieving the Half Earth objective could involve radical changes in land and sea use 29 across the planet. So far, the proposal has received some scrutiny with regards to 30 environmental considerations8 and its potential impacts on food production9. However, there 31 has been no empirical analysis of other social and economic impacts of Half Earth, and the 32 3  proposal itself has been ambiguous about the exact forms and location of new conserved 33 areas being called for. This is despite the fact that the proposal’s social and economic 34 impacts will influence its ability to deliver its conservation objectives and that there are 35 frequently trade-offs involved in meeting environmental, social and economic goals of 36 conservation and development interventions10,11. The reported impacts of existing PAs vary 37 widely from physical and economic displacement to positive socio-economic outcomes for 38 well-being or industry12. These impacts depend in part on the type of PAs, their governance 39 arrangements, and the restrictions they place on resource use. Where the impacts are 40 negative, they tend to disproportionally affect marginalised communities13. In light of this 41 evidence on existing PAs, the increase in conserved areas to 50% could have large 42 implications for the lives of those living inside these areas or in their vicinity14,15. 43 We investigated the human implications of Half Earth by assessing the number and 44 distribution of people that would be directly affected if half of Earth’s land mass was 45 protected. Since there is no consensus among those calling for a 50% protection target 46 regarding which additional areas to protect, we based our analysis on the ecoregion 47 approach proposed by Dinerstein and colleagues78. This approach is based on 846 48 ecoregions, to ensure protection of the full range of ecosystems and their associated species, 49 to adequately conserve all elements of biodiversity. Dinerstein et al.8 classify the ecoregions 50 into four categories: those that already have 50% protection, those that could achieve 50% 51 protection as sufficient natural habitat remains, those where 50% could be possible with 52 substantial restoration efforts, and those with at most 20% of their natural habitat remaining 53 and where achieving 50% protection of habitat is therefore unrealistic. To calculate the 54 minimum number of people who would live in the conserved areas, and hence, would be 55 directly affected by Half Earth, we selected areas (~5x5 km pixels) to be added to the existing 56 4  PA network within each ecoregion from lowest to highest human footprint value16 until 50% 57 coverage was achieved under two scenarios: (a) within all ecoregions and (b) only in 58 ecoregions where Dinerstein and colleagues consider Half Earth reachable8. To achieve this 59 we combined the global data layers of ecoregions, PAs (from the World Database of 60 Protected Areas17) and human footprint with a global human population layer for 201718.  61 Our approach assumes a protection strategy designed to minimise key impacts on 62 society, including avoiding areas with high population density and agricultural land. It 63 ignores effects of conserved areas on people living beyond their boundaries, such as 64 constrained access to resources. For these reasons our approach generates a conservative 65 (lower bound) estimate of the potential number of people affected. Indeed, areas with higher 66 human footprint values, and higher population density, would have to be protected if 67 additional ecological criteria were applied to design the protection strategy, such as ensuring 68 connectivity between conserved areas, setting minimum size thresholds of conserved areas, 69 or seeking to protect land with highest biodiversity regardless of ecoregion. Hence, the 70 number of people affected would likely be higher, especially in poorer countries which tend 71 to have higher concentrations of biodiversity19.  72 We find that over 1 billion people currently live in areas that would be protected 73 under Half Earth if the proposal were applied to all ecoregions (Fig. 1). This is four times the 74 number of people estimated by our approach to be living in PAs today (247 million) and 75 includes 760 million people living in additional areas to be protected beyond existing PAs to 76 meet the 50% target. If we only consider the ecoregions where Dinerstein et al. suggest 50% 77 protection is feasible8, 28% of the ecoregions’ area (Supplementary Figure 2), currently home 78 to 170 million people, must be newly protected. This is roughly equivalent to the population 79 of the UK, Thailand and Morocco combined. The majority of people living in new areas to be 80 5  protected live in middle-income countries and ~10% in low income countries, regardless of 81 whether we include all, or only less impacted, ecoregions (Table 1). 82 The majority of the additional conserved areas have human footprint values within 83 the lowest 20% (Supplementary Figure 3). However, the global network of conserved areas 84 necessary to achieve Half Earth would comprise areas with human footprint values within the 85 top 20% under both scenarios, covering all ecoregions or only less impacted ones. At the 86 upper end of this spectrum, these include highly developed areas, such as London, UK (Fig. 1 87 and Supplementary Figure 2). Implementing Half Earth at the ecoregion level in this way 88 would clearly be in conflict with human use, raising questions about the feasibility and 89 diverse social implications of this strategy. 90 We recognise the importance of conserved areas for the future of life on Earth, and 91 the fundamental need for radical action in the face of unfolding environmental crises. 92 However, our findings highlight the crucial importance of taking into account the human 93 impacts of Half Earth, GDN, or other ambitious (area-based) conservation targets. Even with 94 our conservative approach a very large number of people would be affected by 95 implementing Half Earth. Therefore, any such proposals need to explicitly consider and 96 seriously engage with their social and economic consequences. Considering these 97 implications is not only central to concerns about social and environmental justice, but will 98 also determine how realistic their implementation is in terms of achieving their intended 99 conservation outcomes.  100 Based on our findings we make three recommendations. Firstly, Half Earth 101 proponents should be explicit about the types, and location, of conserved areas they are 102 calling for, to allow for more in-depth assessments of their social, economic and 103 environmental impacts in the future. Secondly, the advocates of all area-based conservation 104 6  measures should recognise and take seriously the human consequences, both negative and 105 positive, of their proposals. Thirdly, the Parties to the CBD, tasked with negotiating and 106 implementing the post-2020 conservation framework, should apply more holistic, 107 interdisciplinary approaches that take into account social and economic implications across 108 scales14,20. Such approaches should consider important broader issues such as environmental 109 justice, the plural values people attribute to nature, and the need for action to tackle the 110 ultimate economic consumption and production drivers of biodiversity loss10,14,21. 111  112 Methods  113 To determine the number and distribution of people living in areas that would be protected 114 under two Half Earth scenarios (50% protection within all ecoregions, and 50% protection of 115 those ecoregions with more than 20% natural habitat remaining), we combined the following 116 global datasets: terrestrial ecoregions8, human footprint16, the World Database of PAs 117 (WDPA, version July 201817) and LandScan 2017 global population distribution18. We focused 118 on ecoregions because (a) Half Earth targets have been judged achievable, or already 119 reached, in ~49% of all ecoregions8, (b) they have been widely used as a proxy to capture 120 biodiversity for conservation planning, and (c) they are the basis for the GDN  proposal7 and 121 for assessing Half Earth’s impacts on food production9. We grouped ecoregions into 122 Dinerstein et al.’s8 four categories according to their percentage protection and the amount 123 of natural habitat remaining. We selected new areas for protection (here referred to as 124 ‘conserved areas’) based on the human footprint, which combines a diversity of human 125 impacts, including human population density, agricultural land, infrastructure and transport 126 routes. While it does not capture some less intensive human influences, it is the most 127 comprehensive global index of its kind. To determine the distribution of people within 128 7  countries of different income-status, we joined a Global Administrative Areas (GADM) layer 129 at country level22 with the World Bank’s (WB) income classification23 of low, low-middle, 130 upper-middle and high income countries. Disputed territories and countries without WB 131 income codes were excluded from the analysis (n=6). 132 We pre-processed datasets in ArcGIS version 10.4.1. We rasterized all datasets, projected 133 them to Mollweide equal area at a spatial resolution of ~5x5 km, and set them to a common 134 extent. Through this pre-processing very small ecoregions, covering less than 50% of any 135 pixel, were removed, resulting in 818 remaining ecoregions. We excluded Antarctica because 136 it is not included in the human footprint dataset nor in the analysis conducted by Dinerstein 137 and colleagues8. As Antarctica is not permanently settled, excluding it does not affect our 138 population count results.  139 We imported, stacked and analysed the raster datasets in R version 3.5.124. To determine the 140 area to be protected in each ecoregion to meet the 50% target, we divided the total area of 141 each ecoregion by two and subtracted the area currently protected per ecoregion according 142 to WDPA17. Under the first scenario, we then ordered pixels in each ecoregion according to 143 ascending human footprint values and selected the number of pixels with the lowest human 144 footprint values to meet the 50% target within each ecoregion from pixels not under 145 protection. We calculated the number of people living in the selected areas by summing up 146 the population count value18. Additionally, we calculated the number of people living within 147 existing PAs by combining the WDPA with the population distribution data layer. Under the 148 second scenario, we repeated this analysis while only selecting pixels to be protected from 149 ecoregions where over 20% of natural habitat remains. Finally, we calculated the number of 150 people living inside the conserved areas under each of these two scenarios per country, 151 according to the WB income classification23.  152 8  Data availability. The R Code to reproduce the results is provided in the Supplementary 153 Information. The datasets used in this study are all publically available or available to 154 educational institutions for non-commercial purposes, but not distributable by the authors. 155 Details of each dataset and download links are provided in the Supplementary Information.  156  157 References 158 1. The Strategic Plan for Biodiversity 2011–2020 and the Aichi Biodiversity Targets (CBD, 159 2010). 160 2. Tittensor, D.P. et al. Science 346, 241–245 (2014). 161 3. Global Assessment Preview (IPBES, 2019). 162 4. Locke, H. George Wright Forum 31, 359–371 (2014). 163 5. Wilson, E.O. (Liveright, New York, 2016). 164 6. Dinerstein, E. et al. Sci. Adv. 5, eaaw2869 (2019). 165 7. Synthesis of Views of Parties and Observers on the Scope and Content of the Post-2020 166 Global Biodiversity Framework (CBD, 2019). 167 8. Dinerstein, E. et al. Bioscience 67, 534–545 (2017). 168 9. Mehrabi, Z., Ellis, E.C. & Ramankutty, N. Nat. Sustain. 1, 409–412 (2018). 169 10. Ellis, E.C., Pascual, U. & Mertz, O. Curr. Opin. Environ. Sustain. 38, 86–94 (2019). 170 11. Brockington, D. & Wilkie, D. Philos. Trans. R. Soc. B Biol. Sci. 370, 20140271 (2015). 171 12. Oldekop, J.A., Holmes, G., Harris, W.E. & Evans, K.L. Conserv. Biol. 30, 133–141 (2016). 172 13. West, P., Igoe, J. & Brockington, D. Annu. Rev. Anthropol. 35, 251–277 (2006). 173 14. Büscher, B. et al. Oryx 51, 407–410 (2017). 174 15. Kopnina, H. Biol. Conserv. 203, 176–185 (2016). 175 16. Venter, O. et al. Nat. Commun. 7, 12558 (2016). 176 9  17. World Database on Protected Areas (UNEP-WCMC & IUCN, 2018). 177 www.protectedplanet.net 178 18. Rose, A.N., McKee, J.J., Urban, M.L. & Bright, E.A. Landscan 2017 (2018).  179 19. Balmford, A. et al. Science 291, 2616–2619 (2001). 180 20. Visconti, P., Bakkenes, M., Smith, R.J., Joppa, L. & Sykes, R.E. Philos. Trans. R. Soc. B Biol. 181 Sci. 370, 20140284 (2015). 182 21. Ten Brink, B. et al. (Netherlands Environmental Assessment Agency, 2010). 183 22. Database of Global Administrative Areas (GADM, 2018). www.gadm.org 184 23. Country Classification (World Bank, 2018). 185 24. R Core Team R: A language and environment for statistical computing (2018). 186 25. Google Earth (2019). 187  188 Corresponding Author. Correspondence to Judith Schleicher. 189  190 Acknowledgements 191 J.G.Z. undertook this work whilst a Visiting Scholar in the Department of Geography, 192 University of Cambridge (May 2018–April 2019), and was supported by the Swiss Programme 193 for Research on Global Issues for Development (r4d programme), which is funded by the 194 Swiss National Science Foundation (SNSF) and the Swiss Agency for Development and 195 Cooperation (SDC), under grant number 400440 152167. This product was made utilizing the 196 LandScan (2017)™ High Resolution global Population Data Set copyrighted by UT-Battelle, 197 LLC, operator of Oak Ridge National Laboratory under Contract No. DE-AC05-00OR22725 198 with the United States Department of Energy.   199 10  Author contributions  200 J.S., J.G.Z., C.F., B.V., P.V., and C.S. designed the analyses. J.S. and J.G.Z. compiled the data 201 and conducted the analyses. J.S. wrote the paper with input from J.G.Z., C.F., B.V., P.V., and 202 C.S. 203 Competing interests. The authors declare no competing interests. 204  205 Supplementary Information. The Supplementary Information contains Supplementary 206 Notes, Methods and Figures, including the full R Code to reproduce the results.  207  208 Figure captions: 209 Table 1: Number of people (million) living in additional areas protected to meet Half Earth 210 targets within each ecoregion, according to the World Bank classification of low, lower-211 middle, upper-middle and high income countries and according to whether (a) all ecoregions 212 are included, or (b) only less impacted ecoregions, where more than 20% of natural habitat 213 remains. Percentage values of the total population are given for these two scenarios. 214   215 Fig. 1: Additional areas to be protected to meet Half Earth 50% protection targets within 216 each ecoregion, on a colour scale of increasing human footprint value. A to D illustrate 217 additional conserved areas (~5x5 km) with the highest human footprint within each World 218 Bank income class: (A) High: London, UK; (B) Upper-middle: St Lucia; (C) Lower-middle: 219 Egypt; (D) Low: Nepal25. 220 Table 1: Number of people (million) living in additional areas protected to meet Half Earth targets within each ecoregion, according to the World Bank classification of low, lower-middle, upper-middle and high income countries and according to whether (a) all ecoregions are included, or (b) only less impacted ecoregions, where more than 20% of natural habitat remains. Percentage values of the total population are given for these two scenarios.   All ecoregions Less impacted ecoregions Low 75 (10%) 16 (9%) Lower-middle 403 (53%) 64 (37%) Upper-middle 234 (31%) 65 (38%) High 47 (6%) 25 (15%)  ABCDABCDHuman footprintHigh : 45.36Low : 00 2,600 5,200 km

English

Protecting half of the planet could directly affect over one billion people

In  light  of  continuing  global  biodiversity  loss,  one  ambitious  proposal has gained considerable traction amongst conserva-tionists:  the  goal  to  protect  half  the  Earth.  Our  analysis  sug-gests that at least one billion people live in places that would be  protected  if  the  Half  Earth  proposal  were  implemented  within all ecoregions. Taking into account the social and eco-nomic  impacts  of  such  proposals  is  central  to  addressing  social and environmental justice concerns, and assessing their acceptability and feasibility

Schleicher, Judith

Zaehringer, Julie G.

Fastré, Constance

Vira, Bhaskar

Visconti, Piero

Sandbrook, Chris

Bern Open Repository and Information System (BORIS)

Apollo (Cambridge)

http://pure.iiasa.ac.at/id/eprint/16178/1/Half%20Earth%20Paper_SubmitedProof.pdf

Protecting half of the planet could directly affect over one billion people

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International Institute for Applied Systems Analysis (IIASA)

Bern Open Repository and Information System (BORIS)

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