Lucy Young’s research while affiliated with WWF United Kingdom and other places

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Publications (9)


Map of regional biomes. Solid coloured areas represent biomes. Black lines separate out biogeographic realms. Black dots represent sites in the PREDICTS database used in our global model (Hudson et al. 2017). Hashed coloured areas represent regional biomes that were not included in analysis due to data deficiency (see methods). Biome and biogeographic realm spatial data from (Olson et al. 2001).
Change in Akaike's information criterion (ΔAIC) for generalised linear mixed models (GLMMs) predicting change in a global dataset of (a) species richness and (b) total abundance consistently suggests models including regional biome have highest support when modelling response to land‐use change. Four GLMMs with differing fixed‐effect structures containing Land Use (LU) interacting with Regional biome (RB), Biome or Realm were compared using AIC values. A model with low AIC is considered to have higher support. ΔAIC is calculated as the difference in AIC from the lowest scoring model. The box and whisker plots represent a summary of ΔAIC values of 100 hold‐out models, where each iteration removed 10% of studies at random as a test of model robustness. Importantly, for a given dataset in this hold‐out analysis, LU:RB model had the lowest AIC in 100% of iterations. The PREDICTS dataset was subset to only include data from regional biomes with 25 data points per combination of regional biome and land‐use type. Land use is a discrete variable with primary vegetation, secondary vegetation, plantation forest, pasture and cropland as its categories (see the Supporting information for descriptions of land‐use types).
Responses of species richness to land‐use change across regional biomes. The results of a GLMM predicting the response of species richness to land‐use within regional biomes from tropical forest (a), temperate forest (b) and tropical grasslands and savannahs (c) across land‐use types when compared to primary vegetation (PV). Responses of species richness of plants and animals were predicted across land‐use types including secondary vegetation (SV), plantation forest (PF), pasture (Pa) and cropland (Cr). Each point represents mean prediction, with 75% confidence intervals (thick whiskers) and 95% confidence intervals (thin whiskers). Responses are considered significantly different from PV if the 95% confidence intervals do not overlap 0. To keep scales consistent, upper 95% CIs greater than 100 have been included as text instead.
Responses of total abundance to land‐use change across regional biomes. The results of a GLMM predicting the response of total abundance to land‐use within regional biomes from tropical forest (a), temperate forest (b) and tropical grasslands and savannahs (c) across land‐use types when compared to primary vegetation (PV). Responses of total abundance of plants and animals were predicted across land‐use types including secondary vegetation (SV), plantation forest (PF), pasture (Pa) and cropland (Cr). Each point represents mean prediction, with 75% confidence intervals (thick whiskers) and 95% confidence intervals (thin whiskers). Responses are considered significantly different from PV if the 95% confidence intervals do not overlap 0. To keep scales consistent, upper 95% CIs greater than 100 have been included as text instead.
Responses of species richness in individual taxa groups to land‐use change across regional biomes. The results of a GLMM predicting the response of species richness across land‐use types, regional biomes in three biomes (tropical forest, temperate forest and tropical grassland) and three taxon groups (vertebrate, invertebrate and plants) when compared to primary vegetation (PV). Responses of species richness were predicted across disturbed land‐use types including secondary vegetation (SV), plantation forest (PF), pasture (Pa) and cropland (Cr). Each point represents mean prediction, with 75% confidence intervals (thick whiskers) and 95% confidence intervals (thin whiskers). To keep scales consistent, upper 95% CIs greater than 100 have been included as text instead. Responses are considered significantly different if the 95% confidence intervals do not overlap 0.
Regional Biomes outperform broader spatial units in capturing biodiversity responses to land‐use change
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December 2024

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Biogeographic context, such as biome type, has a critical influence on ecological resilience, as climatic and environmental conditions impact how communities respond to anthropogenic threats. For example, land‐use change causes a greater loss of biodiversity in tropical biomes compared to temperate biomes. Furthermore, the nature of threats impacting ecosystems varies geographically. Therefore, monitoring the state of biodiversity at a high spatial resolution is crucial to capture variation in threat–responses caused by biogeographical context. However such fine‐scale ecological data collection could be prohibitively resource intensive. In this study, we aim to find the spatial scale that could best capture variation in community‐level threat responses whilst keeping data collection requirements feasible. Using a database of biodiversity records with extensive global coverage, we modelled species richness and total abundance (the responses) across land‐use types (reflecting threats), considering three different spatial scales: biomes, biogeographical realms, and regional biomes (the interaction between realm and biome). We then modelled data from three highly sampled biomes to ask how responses to threat differ between regional biomes and taxonomic group. We found strong support for regional biomes in explaining variation in species richness and total abundance compared to biomes or realms alone. Our biome case studies demonstrate that there is variation in magnitude and direction of threat responses across both regional biomes and taxonomic group, although the interpretation is limited by sampling bias in the literature. All groups in tropical forest showed a consistently negative response, whilst many taxon‐regional biome groups showed no clear response to threat in temperate forest and tropical grassland. Our results provide the first empirical evidence that the taxon‐regional biome unit has potential as a reasonable spatial unit for monitoring how ecological communities respond to threats and designing effective conservation interventions to bend the curve on biodiversity loss.

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Biodiversity shows unique responses to land-use change across regional biomes

May 2024

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141 Reads

Biogeography has a critical influence on how ecological communities respond to threats and how effective conservation interventions are designed. For example, the resilience of ecological communities is linked to environmental and climatic features, and the nature of threats impacting ecosystems also varies geographically. Understanding community-level threat responses may be most accurate at fine spatial scales, however collecting detailed ecological data at such a high resolution would be prohibitively resource intensive. In this study, we aim to find the spatial scale that could best capture variation in community-level threat responses whilst keeping data collection requirements feasible. Using a database of biodiversity records with extensive global coverage, we modelled species richness and total abundance (the responses) across land-use types (reflecting threats), considering three different spatial scales: biomes, biogeographical realms, and regional biomes (the interaction between realm and biome). We then modelled data from three highly sampled biomes separately to ask how responses to threat differ between regional biomes and taxonomic group. We found strong support for regional biomes in explaining variation in species richness and total abundance compared to biomes or realms alone. Our biome case studies demonstrate that there is a high variation in magnitude and direction of threat responses across both regional biomes and taxonomic group, but all groups in tropical forest showed a consistently negative response, whilst many taxon-regional biome groups showed no clear response to threat in temperate forest and tropical grassland. Our results suggest that the taxon-regional biome unit has potential as a reasonable spatial and ecological scale for understanding how ecological communities respond to threats and designing effective conservation interventions to bend the curve on biodiversity loss.


Fig. 1 The number of publications per year citing the Living Planet Index between 1998 and 2020. The secondary Y-axis shows the cumulative total of publications. These 2152 citations are from academic and grey literature in English and non-English languages between the years 1998 and 2020 (as of 18th of January 2021). See Supplementary Methods 1 and Supplementary Table 1 for details on the methods and Supplementary Note 1, Supplementary Figs. 1-3 and Supplementary Tables 2-5 for further exploration of the citation data, and Supplementary Table 6 and Supplementary Fig. 4 for key LPI papers' citation impact.
Fig. 2 Growth in number of populations and species in the Living Planet Database (LPD) by region and taxa. a-d The cumulative number of new populations (a) and species (b) entered by region, and the cumulative number of populations (c) and species (d) entered by taxon. Please note 2b adds up to more than the individual number of species as some species occur in more than one region. See Supplementary Methods 2 for details how the figure was derived and Supplementary Fig. 6 for an overview.
Application of the LPI Corresponding biodiversity and sustainable development targets and other multilateral environmental agreements (MEAs)
Past, present, and future of the Living Planet Index

June 2023

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371 Reads

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34 Citations

npj Biodiversity

As we enter the next phase of international policy commitments to halt biodiversity loss (e.g., Kunming-Montreal Global Biodiversity Framework), biodiversity indicators will play an important role in forming the robust basis upon which targeted, and time sensitive conservation actions are developed. Population trend indicators are one of the most powerful tools in biodiversity monitoring due to their responsiveness to changes over short timescales and their ability to aggregate species trends from global down to sub-national or even local scale. We consider how the project behind one of the foremost population level indicators - the Living Planet Index - has evolved over the last 25 years, its value to the field of biodiversity monitoring, and how its components have portrayed a compelling account of the changing status of global biodiversity through its application at policy, research and practice levels. We explore ways the project can develop to enhance our understanding of the state of biodiversity and share lessons learned to inform indicator development and mobilise action.


Fig. 2. Three case-studies of regional biomes: distribution of data. The PREDICTS
Biodiversity shows unique responses to land-use change across regional biomes

March 2023

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1,195 Reads

Biogeography has a critical influence on how ecological communities respond to threats and how effective conservation interventions are designed. For example, the resilience of ecological communities is linked to environmental and climatic features, and the nature of threats impacting ecosystems also varies geographically. Understanding community-level threat responses may be most accurate at fine spatial scales, however collecting detailed ecological data at such a high resolution would be prohibitively resource intensive. In this study, we aim to find the spatial scale that could best capture variation in community-level threat responses whilst keeping data collection requirements feasible. Using a database of biodiversity records with extensive global coverage, we modelled species richness and total abundance (the responses) across land-use types (reflecting threats), considering three different spatial scales: biomes, biogeographical realms, and regional biomes (the interaction between realm and biome). We then modelled data from three highly sampled biomes separately to ask how responses to threat differ between regional biomes and taxonomic group. We found strong support for regional biomes in explaining variation in species richness and total abundance compared to biomes or realms alone. Our biome case studies demonstrate that there is a high variation in magnitude and direction of threat responses across both regional biomes and taxonomic group, but all groups in tropical forest showed a consistently negative response, whilst many taxon-regional biome groups showed no clear response to threat in temperate forest and tropical grassland. Our results suggest that the taxon-regional biome unit has potential as a reasonable spatial and ecological scale for understanding how ecological communities respond to threats and designing effective conservation interventions to bend the curve on biodiversity loss.


Past, present, and future of the Living Planet Index

June 2022

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74 Reads

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9 Citations

As we enter the next phase of international policy commitments to halt biodiversity loss (e.g. Post-2020 Biodiversity Framework), biodiversity indicators will play an important role forming the robust basis upon which targeted, and time sensitive conservation actions are developed. Population trend indicators are perhaps the most powerful tool in biodiversity monitoring due to their responsiveness to changes over short timescales and their ability to aggregate species trends from global down to at a sub-national or even local scale. We consider how the project behind the foremost population level indicator - the Living Planet Index - has evolved over the last 25 years, its value to the field of biodiversity monitoring, and how its components have portrayed a compelling account of the changing status of global biodiversity through its application at policy, research and practice levels. We explore ways the project can develop to enhance our understanding of the state of biodiversity and share lessons learned to inform indicator development and mobilise action.


Bending the curve of terrestrial biodiversity needs an integrated strategy

September 2020

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5,020 Reads

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732 Citations

Nature

Increased efforts are required to prevent further losses to terrestrial biodiversity and the ecosystem services that it provides1,2. Ambitious targets have been proposed, such as reversing the declining trends in biodiversity³; however, just feeding the growing human population will make this a challenge⁴. Here we use an ensemble of land-use and biodiversity models to assess whether—and how—humanity can reverse the declines in terrestrial biodiversity caused by habitat conversion, which is a major threat to biodiversity⁵. We show that immediate efforts, consistent with the broader sustainability agenda but of unprecedented ambition and coordination, could enable the provision of food for the growing human population while reversing the global terrestrial biodiversity trends caused by habitat conversion. If we decide to increase the extent of land under conservation management, restore degraded land and generalize landscape-level conservation planning, biodiversity trends from habitat conversion could become positive by the mid-twenty-first century on average across models (confidence interval, 2042–2061), but this was not the case for all models. Food prices could increase and, on average across models, almost half (confidence interval, 34–50%) of the future biodiversity losses could not be avoided. However, additionally tackling the drivers of land-use change could avoid conflict with affordable food provision and reduces the environmental effects of the food-provision system. Through further sustainable intensification and trade, reduced food waste and more plant-based human diets, more than two thirds of future biodiversity losses are avoided and the biodiversity trends from habitat conversion are reversed by 2050 for almost all of the models. Although limiting further loss will remain challenging in several biodiversity-rich regions, and other threats—such as climate change—must be addressed to truly reverse the declines in biodiversity, our results show that ambitious conservation efforts and food system transformation are central to an effective post-2020 biodiversity strategy.


Bending the Curve of Global Freshwater Biodiversity Loss – An Emergency Recovery Plan

January 2020

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3,620 Reads

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873 Citations

BioScience

Despite their limited spatial extent, freshwater ecosystems host remarkable biodiversity, including one third of all vertebrate species. This biodiversity is declining dramatically: globally, wetlands are vanishing three times faster than forests, and freshwater vertebrate populations have fallen more than twice as steeply as terrestrial or marine populations. Threats to freshwater biodiversity are well documented but co-ordinated action to reverse the decline is lacking. We present an Emergency Recovery Plan to “bend the curve” of freshwater biodiversity loss. Priority actions include: 1) accelerating implementation of environmental flows; 2) improving water quality; 3) protecting and restoring critical habitats; 4) managing exploitation of freshwater ecosystem resources, especially species and riverine aggregates; 5) preventing and controlling non-native species invasions; and 6) safeguarding and restoring river connectivity. We recommend adjustments to targets and indicators for the Convention on Biological Diversity and the Sustainable Development Goals, and roles for national and international state and non-state actors. *** This paper has been accepted for publication in BioScience. A link to the BioScience version will follow in due course ***


Fig. 1. (A) Impact of Cerrado-sourced soy on endemic biodiversity (as a percentage of global impacts of soy in the Cerrado), plotted against embedded consumption of Cerrado-sourced soy (as a percentage of global Cerrado-sourced soy consumption) for the 7 AD countries, Brazil, the countries of the European Union (EU28), China (including Hong Kong and Taiwan), India, North America, South America, and the rest of the world (RoW). Gray line indicates mean global impact per unit of soy consumption. (B) Spatial pattern of our endemic biodiversity loss index within the Cerrado during the period 2000 to 2010. (C) Difference (tons) between production for domestic consumption (all Brazil) and Chinese consumption. Negative values (blue) are municipalities where production for Chinese consumption exceeds production for Brazil. Positive values (orange/red) are municipalities where production for Brazilian consumption exceeds production for China. (D) Comparison of the relative soy-attributed biodiversity impact that is directly imported to AD countries and impact that is attributed to final consumption within those countries (i.e., the latter accounts for both reexports and embedded consumption). (E) Sectoral and countrywise differences for AD countries showing the relative impact of 3 key soy-linked sectors as a percentage of each country's consumption of soy across all sectors combined. The value above the bar indicates the relative importance of each country to global biodiversity impacts of Cerrado-sourced soy.
Fig. 2. Chord diagrams showing impacts on likelihood of persistence due to soy expansion between 2000 and 2010 for 2 charismatic species (Top) and for all endemics (Bottom Left). Losses are calculated for each municipality according to the total embedded flows of soy and then aggregated to state level for visualization. Chords show the flow from states on the left-hand side (BA = Bahia, dark blue; DF = Distrito Federal, gray; GO = Goiás, red; MA = Maranhão, cyan; MG = Minas Gerais, light green; MS = Mato Grosso do Sul, purple; MT = Mato Grosso, dark green; PI = Piauí, pink; PR = Paraná, dark olive green; RO = Rondônia, brown; SP = São Paulo, dark gray; TO = Tocantins, gold) through to the country or region of final consumption on the right-hand side (Brazil, South America, North America, European Union, India, China, and the rest of world). The proportion of remaining suitable habitat within the Cerrado for the 2 species (Bottom Right) and the mean for all endemic species. Light gray: suitable habitat lost from the preindustrial era to the year 2000; red: losses during the 2000 to 2010 study period (as represented in the chord diagrams); medium gray: losses between 2010 and 2014; dark gray: remaining suitable habitat in 2014.
Fig. 3. Alignment of government commitments with sustainability goals of key traders. Chord diagram representing direct soy trade from the Brazilian Cerrado to the 7 countries of the Amsterdam Declaration from the largest traders in 2011 (companies shown were among the top 3 traders in 2011 for at least one of the countries; companies trading smaller volumes are aggregated and shaded gray). Green shaded chords indicate exports via companies with zero-deforestation commitments; orange and brown shades indicate no such commitment (data from company websites as of December 2018).
Linking global drivers of agricultural trade to on-the-ground impacts on biodiversity

October 2019

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711 Reads

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145 Citations

Proceedings of the National Academy of Sciences

Consumption of globally traded agricultural commodities like soy and palm oil is one of the primary causes of deforestation and biodiversity loss in some of the world’s most species-rich ecosystems. However, the complexity of global supply chains has confounded efforts to reduce impacts. Companies and governments with sustainability commitments struggle to understand their own sourcing patterns, while the activities of more unscrupulous actors are conveniently masked by the opacity of global trade. We combine state-of-the-art material flow, economic trade, and biodiversity impact models to produce an innovative approach for understanding the impacts of trade on biodiversity loss and the roles of remote markets and actors. We do this for the production of soy in the Brazilian Cerrado, home to more than 5% of the world´s species. Distinct sourcing patterns of consumer countries and trading companies result in substantially different impacts on endemic species. Connections between individual buyers and specific hot spots explain the disproportionate impacts of some actors on endemic species and individual threatened species, such as the particular impact of European Union consumers on the recent habitat losses for the iconic giant anteater ( Myrmecophaga tridactyla ). In making these linkages explicit, our approach enables commodity buyers and investors to target their efforts much more closely to improve the sustainability of their supply chains in their sourcing regions while also transforming our ability to monitor the impact of such commitments over time.


Figure 1-Illustration of the overall approach to generating land-use projections able to bend the curve of biodiversity trends as affected by human land use.
Figure 2-Illustration of the construction of the potential protected areas layer. We combined a) the World Database of Protected Areas (IUCN and UNEP-WCMC 2017), b) the World Database of Key Biodiversity Areas (BirdLife International 2017), and c) the 2009 Wilderness Areas (Watson et al 2016) into d) a single potential protected areas layer. Colours on the map display the share of land under any of the respective layer.
Figure 3-Illustration of the BII coefficients estimated from the PREDICTS database, providing a measure of the relative impact of 10 land-use classes on the integrity of ecological assemblages (as compared to pristine conditions).
Table 3 (continued)
Figure 4-Illustration of the original input (range size rarity based on IUCN range maps, upper panel) and of the final regional restoration priority layer (after normalization by biome and continent combination, log transformation and rescaling to [0-1]).
Towards pathways bending the curve of terrestrial biodiversity trends within the 21st century

May 2018

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2,298 Reads

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8 Citations

Unless actions are taken to reduce multiple anthropogenic pressures, biodiversity is expected to continue declining at an alarming rate. Models and scenarios can be used to help design the pathways that sustain a thriving nature and its ability to contribute to people. This approach has so far been hampered by the complexity associated with combining projections of pressures on, and subsequent responses from, biodiversity. Most previous assessments have projected continuous biodiversity declines and very few have identified pathways for reversing the loss of biodiversity without jeopardizing other objectives such as development or climate mitigation. The Bending The Curve initiative set out to advance quantitative modelling techniques towards ambitious scenarios for biodiversity. In this proof-of-concept analysis, we developed a modelling approach that demonstrates how global land use and biodiversity models can be combined to can shed light on pathways able to bend the curve of biodiversity trends as affected by land-use change, the biggest current threat to biodiversity. In order to address the uncertainties associated with such pathways we used a multi-model framework and relied on the Shared Socioeconomic Pathway/Representative Concentration Pathway scenario framework. This report describes the details of this modelling approach.

Citations (6)


... terrestrial, freshwater) has been demonstrated on a global scale and a similar approach could be used for urban habitats (WWF, 2022(WWF, , 2024. In addition to population of vertebrates, it may also be extended to include data on invertebrates, fungi, and/or plants (Ledger et al., 2023), as long as they are collected in a standardised and continuous manner. However, robust, long-term monitoring data for taxa to be monitored are to be ensured. ...

Reference:

From coverage to extension: Evaluating indices for biodiversity monitoring in cities to reflect global and EU biodiversity targets
Past, present, and future of the Living Planet Index

npj Biodiversity

... The 2022 LPR acknowledges that "polar regions...showed the highest impact probabilities for climate change, driven in particular by impacts on birds" (page 41, Almond et al. (2022)), but there is no specific mention of the Antarctic in the report. Though the rate of new Antarctic time series added to the LPI database has accelerated in recent years (Ledger et al. 2022), the data within MAPPPD has not been integrated into the LPI database and the LPI's coverage of Antarctica remains inadequate. ...

Past, present, and future of the Living Planet Index
  • Citing Preprint
  • June 2022

... This includes commitments to halt human-driven extinctions, reduce the extinction rate and extinction risk of all species 10-fold, and increase the abundance of wild species to healthy and resilient levels. Urgent conservation actions are necessary to achieve these outcomes [4,5]. ...

Bending the curve of terrestrial biodiversity needs an integrated strategy

Nature

... Spatial and temporal variations in animal population sizes and community structure are natural phenomena, but those caused or exacerbated by anthropogenic activities have increased in prevalence and magnitude in the last two centuries, with freshwater ecosystems particularly impacted (Tickner et al., 2020). Some of the most widespread, significant and persistent pressures are overexploitation, habitat loss, invasive species and pollution, but many others, including climate change, novel contaminants and interactive effects, have emerged or increased in severity in recent decades (Birk et al., 2020). ...

Bending the Curve of Global Freshwater Biodiversity Loss – An Emergency Recovery Plan

BioScience

... The Cerrado is the second largest ecoregion in South America, covering around 2 million km², and the world's most biodiverse savanna, holding 5% of global animal and plant biodiversity, including many endemic species 20,21 . However, half of its area has been converted to agricultural LU ( Supplementary Fig. 1), accounting for 62% of Brazil's cotton, orange, sugar cane, maize, soybeans, beans, potato, coffee and eucalyptus production and 40% of the country's heads of cattle 22 . ...

Linking global drivers of agricultural trade to on-the-ground impacts on biodiversity

Proceedings of the National Academy of Sciences

... Scenario analysis are useful tools for strategic policy planning and implementation, helping to screen and set achievable targets with alternative policy and management options on different drivers that affect nature and people (Cloudy crystal balls, 2000;IPBES, 2016). Models quantify relationships between a range of socio-economic (e.g., population, economy, energy demand, technology) and environmental (e.g., land use, climate change mitigation and adaptation, natural resource use, pollution control) drivers to inform decision options for sectoral policies (Huppmann et al., 2019;Leclere et al., 2018;Obersteiner et al., 2016;Stehfest et al., 2014). These models can quantify alternative future scenarios by setting different assumptions and goals on policy or management options (e.g., land-use planning, fishery management) based on a range of environmental trajectories (e.g. ...

Towards pathways bending the curve of terrestrial biodiversity trends within the 21st century