Lydia C. L. Teh’s research while affiliated with University of British Columbia and other places

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Publications (8)


Fig. 1 | Income per capita per day (in USD) by country income group. Countries where daily per capita income falls below the extreme poverty line income (USD 1.90/ person/day), indicated by the red horizontal line.
Cost of covering the gap between fishing income and the USD 1.90 and Minimum Living Wage poverty line incomes (millions real 2016 USD) per year
Poverty line income and fisheries subsidies in developing country fishing communities
  • Article
  • Full-text available

March 2024

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161 Reads

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10 Citations

npj Ocean Sustainability

Louise S. L. Teh

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Lydia C. L. Teh

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Eradicating poverty and harmful fisheries subsidies are two pressing challenges frequently addressed in international agendas for sustainable development. Here we investigate a potential solution for addressing both challenges simultaneously by asking the hypothetical question: to what extent can harmful fisheries subsidies provided by a country finance the cost of lifting fishers out of poverty? Focusing on 30 coastal least developed countries, we find that fishers in 87% of these countries do not earn sufficient income to satisfy the extreme poverty line income of USD 1.90/person/day, and that it would cost an estimated USD 2.2 to 2.6 billion to lift these fishers to different levels of poverty line incomes. Our analysis further suggests that at the country level, redirected harmful fisheries subsidies can cover the entire cost of covering the poverty income gap for between 37 to 43% of assessed countries. Our results provide quantitative evidence that can be used to support simultaneous progress towards achieving several Sustainable Development Goals, including those dealing with poverty reduction, food insecurity, and ocean sustainability.

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Reconstructed global fisheries employment 1950–2015
a, Global number of fishers (full-time equivalents) and contribution of each geographic region. The order of the regions from top to bottom matches the order in the legend. b, Number of fishers by income group (lower-, middle- and higher-income countries). The top line of the stacked area plot in a shows the total global number of fishers from the reconstruction, with the dashed lines showing upper and lower confidence bounds (Methods). The shaded areas in b show the confidence bounds for each income group.
FF (%) of total working population by income group 1950–2015
The FF is the number of fishers divided by the total working population. Shaded envelopes show the confidence bounds (Methods). Inset shows the global average.
Food production efficiency per fisher
Global average CPF peaked around 1980 and declined to about five tonnes per fisher in 2015. By contrast, global average agriculture production per farmer (green circles) tripled from 1960 to 2019. Shaded envelopes show the confidence bounds.
Change in fisheries labour indicators over time by country
a,b, Maps show the relative change (Δ) from the initial to final FF (a) and CPF (b), comparing the average values between 2005 and 2015 with those of 1950–1970. Shapefiles for maps from Natural Earth (https://www.naturalearthdata.com).
Diminishing returns on labour in the global marine food system

November 2023

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143 Reads

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8 Citations

Nature Sustainability

Kim J. N. Scherrer

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Lydia C. L. Teh

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Technological advances over the past century have greatly reduced the proportion of human labour required to produce the world’s food. On land, these advances have continually increased yields, feeding a growing human population even as the number of farmers has fallen. It has long been recognized that technological advances do not necessarily increase fishery yields in the same way; since the natural productivity of wild fish stocks puts a strong limit on capture fisheries, high labour inputs can lead to overfishing. However, the global evolution of labour in marine fisheries has not been assessed, leaving the overall interactions among technology, fishers and catches unknown. Here we reconstruct the global number of marine fishers from 1950 to 2015 and show that the total number of fishers grew with no sign of reversal despite mechanization, as large increases in lower- and middle-income countries overwhelmed an ~60% decrease in higher-income countries. As a result, the wild fish catch per fisher has declined since the 1990s despite major technological advances—a stark contrast to the 70% increase of the production per farmer over the same period. Our results show that, globally averaged, fisheries displayed diminishing—or even negative—returns on labour over 1950–2015, which has been detrimental for food production efficiency, marine ecosystems and fishing communities.


Figure 2. Amount (USD/person/day) required to close the gap between fishing income and the
Average fishing poverty gap (USD/person/day) under each poverty line income measure for different country income groups. Countries are arranged with the largest poverty gap at the top.
Poverty line income and fisheries subsidies in developing country fishing communities

March 2023

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145 Reads

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2 Citations

Eradicating poverty and harmful fisheries subsidies are two pressing challenges frequently addressed in international agendas for sustainable development. Here we investigate a potential solution for addressing both challenges simultaneously by asking the hypothetical question: to what extent can harmful fisheries subsidies provided by a country finance the cost of lifting fishers out of poverty? Focusing on 30 coastal least developed countries, we find that fishers in 87% of these countries do not earn sufficient income to satisfy the extreme poverty line income of USD 1.90/person/day, and that it costs an estimated USD 2.2 to 2.6 billion to lift these fishers to different levels of poverty line incomes. Our analysis further suggests that at the country level, redirected harmful fisheries subsidies can cover the entire cost of covering the poverty income gap for between 37 to 43% of assessed countries. Our results provide quantitative evidence that can be used to support simultaneous progress towards achieving several Sustainable Development Goals, including those dealing with poverty reduction, food insecurity, and ocean sustainability.


Expected impacts of climate change on fisheries rebuilding depend on the scaling between stock biomass and global warming levels. (a) Loss of potential rebuilding benefits and lowered possibility of achieving rebuilding targets. (b) Gain in potential rebuilding benefits and increased possibility of achieving rebuilding targets. (c) No change in rebuilding benefits and possibility of achieving rebuilding targets. Rebuilding targets are computed by simulating changes in biomass under a specified reference target (RT) and different fishing mortality rates for rebuilding. Impacts of climate change on biomass rebuilding are indicated by (1) present‐day maximum potential biomass and scenarios of global warming levels under specified rebuilding reference targets, (2) loss of potential rebuilding benefits (in terms of biomass) relative to no climate change, (3) warming level at when all the benefits from rebuilding biomass are lost (TR0) and (4) warming level at when 50% of the benefits from rebuilding biomass are lost (TR0.5). [Colour figure can be viewed at wileyonlinelibrary.com]
Estimated slope of the relationship between unexploited biomass (B0) and global warming levels. (a) Frequency distribution of marine ecoregions with different projected slopes of B0/B0,T = 0 against global warming level. Red bars represent those marine ecoregions (121 out of 226) with estimated slopes that are significantly (at the 0.05 level) different from 0. (b) Map of marine ecoregions with the estimated slopes of the relationship between projected unexploited biomass relative to preindustrial levels (B0/B0,T = 0) and global atmospheric warming levels. [Colour figure can be viewed at wileyonlinelibrary.com]
Projected biomass relative to the current (2014–2018) level (BT,F/BT = 0,F = 0) for the studied marine ecoregions under different scenarios of global warming (T) and fishing levels (F/FMSY). Only marine ecoregions for which the slope of the relationship between biomass and global warming levels is significantly (at the 0.05 level) different from zero are included here (N = 121). Reference unexploited biomass does not include global warming (T = 0°C). Scenarios of global warming and fishing levels include (a) T = 0°C and F/FMSY = 0.5, (b) T = 0°C and F/FMSY = 0.75, (c) T = 0°C and F/FMSY = 1, (d) T = 0°C and F/FMSY = 1.5, (e) T = 1.5°C and F/FMSY = 0.75, (f) T = 2.6°C and F/FMSY = 0.75, (g) T = 3.5°C and F/FMSY = 0.75, (h) T = 3.5°C and F/FMSY = 1.5. Median values across marine ecoregions for each scenario are highlighted by red dashed lines and the annotated median values.
The maximum global warming levels at or above which we project we would not be able to rebuild biomass from current (average 2010–2014) levels for marine ecoregions of the world under the three rebuilding scenarios. (a) ‘Catch maximization’ scenario (F/FMSY = 1), (b) ‘sustainable target’ scenario (F/FMSY = 0.75), (c) ‘conservation focus’ scenario (F/FMSY = 0.5). PS indicates that the marine ecoregion has a positive relationship between biomass rebuilding and global warming levels or the relationship is insignificant at 0.05 level. NA indicates that no biomass rebuilding can be attained even without climate change (global warming = 0°C). [Colour figure can be viewed at wileyonlinelibrary.com]
Rebuilding fish biomass for the world's marine ecoregions under climate change

September 2022

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342 Reads

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33 Citations

Rebuilding overexploited marine populations is an important step to achieve the United Nations' Sustainable Development Goal 14—Life Below Water. Mitigating major human pressures is required to achieve rebuilding goals. Climate change is one such key pressure, impacting fish and invertebrate populations by changing their biomass and biogeography. Here, combining projection from a dynamic bioclimate envelope model with published estimates of status of exploited populations from a catch‐based analysis, we analyze the effects of different global warming and fishing levels on biomass rebuilding for the exploited species in 226 marine ecoregions of the world. Fifty three percent (121) of the marine ecoregions have significant (at 5% level) relationship between biomass and global warming level. Without climate change and under a target fishing mortality rate relative to the level required for maximum sustainable yield of 0.75, we project biomass rebuilding of 1.7–2.7 times (interquartile range) of current (average 2014–2018) levels across marine ecoregions. When global warming level is at 1.5 and 2.6°C, respectively, such biomass rebuilding drops to 1.4–2.0 and 1.1–1.5 times of current levels, with 10% and 25% of the ecoregions showing no biomass rebuilding, respectively. Marine ecoregions where biomass rebuilding is largely impacted by climate change are in West Africa, the Indo‐Pacific, the central and south Pacific, and the Eastern Tropical Pacific. Coastal communities in these ecoregions are highly dependent on fisheries for livelihoods and nutrition security. Lowering the targeted fishing level and keeping global warming below 1.5°C are projected to enable more climate‐sensitive ecoregions to rebuild biomass. However, our findings also underscore the need to resolve trade‐offs between climate‐resilient biomass rebuilding and the high near‐term demand for seafood to support the well‐being of coastal communities across the tropics.


Steps involved in estimating the economic contribution of BC’s ocean sectors.
Total (a) revenue; (b) GDP; (c) wages; and (d) number of FTE jobs by living and nonliving sectors, 2000–2015.
Total economic impact of ocean sectors averaged over five-year periods from 2000 to 2015 on (a) revenue; (b) GDP; (c) wages; and (d) number of jobs (FTE).
The proportional contribution of ocean sectors in 2015 to total (a) revenue; (b) GDP; (c) wages; and (d) employment (FTEs).
Assessing the Economic Contribution of Ocean-Based Activities Using the Pacific Coast of British Columbia as a Case Study

July 2022

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146 Reads

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9 Citations

Global obligations to achieve sustainable oceans by 2030 require countries to commit to solutions that balance ocean use and protection. To do so necessitates baseline understanding of the ocean’s contribution to socio-economic well-being, which we do by measuring the economic activity of ocean-related sectors. Economic assessments tend to be data intensive and are typically reliant on professional economists, yet they are increasingly relevant to non-economists who engage in ocean management and communication, where they are integral in facilitating trade-off analysis of future ocean change. Thus, there is a need to make ocean economic assessment more accessible to nonspecialists. We fill this need by providing a pragmatic framework for conducting an economic assessment using British Columbia’s ocean sector as a case study. Our results show the impact of the province’s ocean sectors on four economic indicators and indicate that the ocean contributed almost $5 billion (or about 2%) to provincial gross domestic product (GDP) and generated about 106,120 jobs (over 4% of the province’s total) in 2015. Of these, the marine transport sector made the highest overall contribution followed by cruise lines, with GDP impacts of 66% and 13%, respectively. It should be noted that this estimated economic value is not representative of the full value of the ocean as it excludes oil and gas, research and education, and other activities that do not meet our criteria for inclusion, and it does not account for cultural and ecological values. Nonetheless the study highlights the substantial number of economic benefits generated by the blue economy. More significantly, the framework provides a simplified procedure for quantifying economic benefits, and can be applied by nonspecialists to perform rapid economic assessments in a variety of contexts.



Fig. 1. Diagram illustrating this study's methodological framework. It includes three components: (A) projections, (B) scenarios, and (C) models. MSY, maximum sustainable yield (see Materials and Methods). GDP, gross domestic product; GFDL-ESM2M, Geophysical Fluid Dynamics Laboratory Earth System Model 2M.
Fig. 3. Projected impacts of marine extreme high-temperature events and decadal-scale mean changes by 2041-2060 relative to 1986-2005, by fishing countries, under RCP8.5 and SSP3. (A) Projected average changes in fisheries revenue during an annual extreme high-temperature event. (B) Projected decadal-scale mean change in fisheries revenue per GDP. (C) Projected average changes in fisheries-related employment during an annual extreme high-temperature event. (D) Projected decadal-scale mean change in fisheries-related employment per capita. Grayed countries do not have a record of fishing on species included in this study.
Fig. 5. Comparison between observational-based estimated effects of hightemperature extremes with model projections for the 1951-2016 period. (A) The differences between observational-based estimated changes in annual catches from EEZs relative to the mean conditions subtracted by those using maximum catch potential projected from the dynamic bioclimate envelope model (DBEM) driven by the Earth system model large ensemble simulations. (B) A comparison between annual catch anomalies relative to mean conditions under the identified high-temperature extremes using observational-based catches and projected maximum catch potential from the model by EEZs. The solid dots in (B) represent those EEZs with significant (P < 0.05) differences in catches under high-temperature events relative to the mean conditions (see Materials and Methods). Red and blue labels indicate EEZs with effects of high-temperature events estimated from observational-based and projected catches that are consistent in the direction of impacts (red, negative impacts; blue, positive impacts), while green labels indicate those that have inconsistent direction of impacts. Only the solid dotted EEZs are labeled.
A P P L I E D E C O L O G Y Marine high temperature extremes amplify the impacts of climate change on fish and fisheries

October 2021

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475 Reads

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149 Citations

Science Advances

Extreme temperature events have occurred in all ocean basins in the past two decades with detrimental impacts on marine biodiversity, ecosystem functions, and services. However, global impacts of temperature extremes on fish stocks, fisheries, and dependent people have not been quantified. Using an integrated climate-biodiversity-fisheries-economic impact model, we project that, on average, when an annual high temperature extreme occurs in an exclusive economic zone, 77% of exploited fishes and invertebrates therein will decrease in biomass while maximum catch potential will drop by 6%, adding to the decadal-scale mean impacts under climate change. The net negative impacts of high temperature extremes on fish stocks are projected to cause losses in fisheries revenues and livelihoods in most maritime countries, creating shocks to fisheries social-ecological systems particularly in climate-vulnerable areas. Our study highlights the need for rapid adaptation responses to extreme temperatures in addition to carbon mitigation to support sustainable ocean development.


Small-scale fisheries in developed countries: Looking beyond developing country narratives through Japan’s perspective

November 2020

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170 Reads

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21 Citations

Marine Policy

Dialogue on improving small-scale fisheries for food security tends to centre on developing countries due to the generally more acute socio-economic problems these countries face in meeting global Sustainable Development Goals. Current management approaches to improve small-scale fisheries thus tend to cater specifically to the context of developing country fishers. This inadvertently excludes the small-scale fisheries of developed countries from international dialogue, which is a missed opportunity given the insights that can be drawn from understanding progressive challenges that emerge as small-scale fisheries evolve through different stages of socio-economic development. Japan is a developed country whose small-scale fisheries cannot be ignored- yet, most international dialogue about Japanese fisheries centre on its industrial fisheries. Against this backdrop, we stress that it is essential to raise the profile of Japanese and other developed country small-scale fisheries in order to ensure that challenges and potential solutions to their future ecological and socio-economic sustainability are heard and included in the global small-scale fisheries dialogue.

Citations (7)


... Fishermen are among the most commonly associated groups with poverty [9][29] [30][32] [35] [36]. Poverty among coastal fishermen has been widely studied by many previous researchers. ...

Reference:

Navigating The Barriers: Social Cohesion and Inclusion Towards Entrepreneurial Culture in Coastal Fishing Communities
Poverty line income and fisheries subsidies in developing country fishing communities

npj Ocean Sustainability

... Recent research has explored the potential connection between the environmental decline of fisheries, labour productivity and the degrading of working conditions for crew (Sparks and Hasche 2019;Scherrer et al. 2023;Clark and Longo 2021). Yet, this work does not address why and how species dynamics, ecology and the environmental conditions of production in particular fisheries are articulated with working conditions on specific types of fishing vessels. ...

Diminishing returns on labour in the global marine food system

Nature Sustainability

... Since the early 1990s, excessive fishing capacity has surged due to a decade of fleet expansion and technological advancements in the high seas (Newton and Greboval 1999;Watson and Tidd 2018), impacting fisheries globally (Rousseau et al. 2019). This phenomenon is attributed to inadequate management (Ye and Gutierrez 2017), subsidies (Sumaila et al. 2021), and high-seas access to foreign fisheries (Tickler et al. 2018). According to Hilborn et al. (2020), excess fishing pressure results in about a 3-5% loss in potential yields from 50% of the world's potential catch, leading to overfishing in many fish stocks (FAO 2018). ...

WTO must ban harmful fisheries subsidies

... Moreover, understanding how fisheries influence ecosystem processes, especially resilience and recovery, through nutrient supply and storage will provide important insights to inform fisheries policy and strengthen support for ecosystem-based fisheries management 60 . As fisheries policy and management aims to rebuild depleted stocks and ensure sustainable fisheries for the future 26,61,62 , supporting the restoration of essential nutrient pathways could simultaneously improve ecosystem health and stability. ...

Rebuilding fish biomass for the world's marine ecoregions under climate change

... Secondly, in reality, a sustainable ocean economy has a significant impact on GDP through various ocean-based activities, as evidenced in some recent studies. For instance, according to Teh et al. (2022), in British Columbia, the ocean contributed almost $5 billion to the provincial GDP. The study of Sepponen (2021) showed that in Iceland, fishing along with fish processing accounted for 8.1% of GDP, and for Faroe Islands, this number was 20% of GDP in 2019. ...

Assessing the Economic Contribution of Ocean-Based Activities Using the Pacific Coast of British Columbia as a Case Study

... MHWs nearshore likely facilitated the rapid intensification of the typhoon. Current understanding of MHWs predominantly focuses on their dynamic drivers [17,[25][26][27][28][29][30][31][32][33][34], with limited insight into their ecological feedbacks on phytoplankton communities. ...

A P P L I E D E C O L O G Y Marine high temperature extremes amplify the impacts of climate change on fish and fisheries

Science Advances

... There are several reasons for its popularity, including geography and accessibility. Because they are closer and need less capital, coastal resources are more easily accessed in low-income and even highincome nations ( (Simmance, 2022), (Teh, 2020) ). In addition to having easier access to nearshore resources than offshore fishing, coastal fishing doesn't necessitate significant ship and equipment investment (Teh, 2020). ...

Small-scale fisheries in developed countries: Looking beyond developing country narratives through Japan’s perspective
  • Citing Article
  • November 2020

Marine Policy