James A. Estes’s research while affiliated with University of California, Santa Cruz and other places

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Publications (177)


Map of the Aleutian archipelago with labels for study islands and major oceanic passes that separate island groups from west to east: Near Islands (Attu, Agattu, and Semichi Islands), Rat Islands (Kiska, Hawadax, and Amchitka), Delarof and Andreanof Islands (Ogliuga, Tanaga, Adak, and Atka), Islands of Four Mountains (Seguam, Yunaska, and Chuginadak), and Fox Islands (Umnak and Unalaska). Nearshore bathymetry (gray shading) shows continental shelf area, where depth≤200 m [93].
Boxplots of sea urchin density (a) and biomass (b) per 0.25 m², averaged by island (each facet) for each time period of sea otter status: predecline, end of decline, postdecline 1, and postdecline 2. N indicates no data. Barred lines denote passes that separate the island groups shown in Figure 1.
Proportional sea urchin size frequency distributions with sizes averaged by island (from west to east) and time period of sea otter status. y-axis for each plot is from 0 to 100%. No data available to show for predecline: Atka; end of decline: Hawadax, Ogliuga, Tanaga, Atka, Seguam, Yunaska, Chuginadak, Umnak, and Unalaska; and postdecline 2: Seguam. Horizontal dashed lines denote major passes that separate island groups.
Sea urchin recruitment index means by island from west to east, with (closed) and without (open) sea otters. Points represent the predecline period and mean of the two postdecline (open) periods, and end of decline period is not shown. Error bars show standard deviation. Letters a, ab, b, and c denote pairwise significant among islands by PERMANOVA (pperm<0.05) during postdecline periods. Dashed lines denote island groups. No data for Atka predecline period.
Metric MDS plot of sea urchin size distribution by island and time period of sea otter status. Bubble size depicts the average recruitment index (proportion of sea urchins≤20 mm per 0.25 m⁻²) for each island period. Arrows sequentially connect the periods from predecline to end of decline to postdecline 1 to postdecline 2, except where only 3 points are connected and end of decline data were not available. Some islands were excluded due to no predecline data (Atka) or limited sample size (Umnak and Unalaska).

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Changes in Abiotic Drivers of Green Sea Urchin Demographics following the Loss of a Keystone Predator
  • Article
  • Full-text available

July 2023

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225 Reads

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1 Citation

Journal of Marine Sciences

B. P. Weitzman

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B. Konar

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[...]

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J. A. Estes

Sea urchin population demographics can respond to changes in keystone species abundances, with the magnitude of these responses varying depending on environmental influences. In this study, sea urchin populations were surveyed across 15 Aleutian archipelago islands over a 30-year period to understand how patterns of sea urchin demography (density, biomass, and size structure) varied through different ecological regimes that were caused by changes in the abundance of sea otters, a keystone species in this system. To examine long-term changes in sea urchin demographics, four time periods across the recent decline of sea otters were examined: during sea otter presence (1987-1994), nearing absence at the end of the decline (1997-2000), 10 years postdecline (2008-2010), and 15-20 years following the loss of sea otters from the ecosystem (2014-2017). Our results show that when sea otters were broadly present, sea urchin demographics were generally similar across the archipelago, with few urchins that had large-sized bodies. During this time, bottom-up environmental controls were muted relative to top-down forces from keystone predation. However, as sea otters declined and remained absent from the system, abiotic factors became more influential on sea urchin biomass, density, and size structure. In particular, differences among island groups during these periods were correlated with variation in ocean temperature, bathymetric complexity, and habitat availability. Sea urchin recruitment also varied among island groups, corresponding to ecoregions delineated by oceanic passes across the archipelago. The functional extinction of sea otters revealed an increasing influence of abiotic forcing in the absence of top-down control. This study further highlights the importance of understanding how keystone predators regulate herbivore demographics.

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Use of vertebrates by humans and other predators
a Number and percent of vertebrate species with documented human use, and b number for which use is considered a threat, including the subset facing extinction (Vulnerable, Endangered, or Critically Endangered status on the IUCN Red list). c Prey diversity (number of species; logarithmic scale) of humans and comparable predators (i.e., those that prey on vertebrates for which range-wide data were available) across equivalent geographic ranges, with percentages indicating human prey overlap with each predator.
Diversity of uses by human predators
Number and overlap of species in each IUCN ‘use and trade’ category for A terrestrial and aquatic realms and B six vertebrate classes with the most species. Images depict examples of exploited species in use categories along with their IUCN status (LC: Least Concern, NT: Near Threatened, VU: Vulnerable, EN: Endangered, CR: Critically Endangered). Taxonomic information available in Supplementary Information (Supplementary Table 2). C African lion, Panthera leo (photo: Antony Trivet via Pixabay). D Arctic char, Salvelinus alpinus (photo: Reinhard Thrainer via Pixabay), E Atlantic Bluefin Tuna, Thunnus thynnus (photo: Marko Steffensen via Alamy). F Violet-capped Woodnymph, Thalurania glaucopis (photo: Wilfred Marissen via iStock). G White-lipped viper, Trimeresurus albolabris (photo: Mark Kostich via iStock). H Rainford’s butterflyfish, Chaetodon rainfordi (photo: Biosphoto via Alamy). I Philippine pangolin, Manis culionensis (photo: Vicky Chauhan via iStock). J Northern rhinoceros, Ceratotherium simum cottoni (photo: Adele Dobler via iStock). K Asiatic black bear, Ursus thibetanus (photo: Volodymyr Burdiak via Shutterstock). L Blue shark, Prionace glauca (photo: Howard Chen via iStock). M American bison, Bison bison (photo: WikiImages via Pixabay). N Golden poison frog, Phyllobates terribilis (photo: Hippopx.com). O Sockeye salmon, Oncorhynchus nerka (photo: Eduardo Baena via iStock). P American crocodile, Crocodylus acutus (photo: Pixabay). Q Resplendent quetzal, Pharomachrus mocinno (photo: Mikhail Dudarev via iStock). R Helmeted hornbill, Rhinoplax vigil (photo: Craig Ansibin via Shutterstock). S Rhesus macaque, Macaca mulatta (photo: Donyanedomam via iStock.com).
Spatial patterns of vertebrate use by human predators
a Number of species used. b Number of species used after accounting for variation in species richness (standardization process described in Mapping section of Methods; Fig. 5). Percent of used species that are exploited as c food and d pets. Patterns relate to the distribution of species (assessed across their entire range), not necessarily where capture, consumption or other end use occurs.
Human use of birds and mammals across trait space
a Position of 16,413 terrestrial bird and mammal species across ecological and morphological trait space—colored by use, threat and extinction risk; contours indicate 50% probability contours. Comparisons of b total volume and c unique volume between observed and randomized trait spaces; squares indicate medians, and bars indicate 95% confidence intervals. ‘Extinction risk’ refers to species assessed as Vulnerable, Endangered, or Critically Endangered by the IUCN. d Prey volume of comparable predators and humans across equivalent geographic ranges. Only ‘Human-all uses’ is visualized; estimates for ‘Human-food’ are approximately equivalent, due to the non-linear scaling of volume with the number of species. See Ecological trait space section of Methods for details.
Residuals data underlying mapping in Fig. 3
a Species used by humans (log(x + 0.01)) as a function of species present (log) in each 110 km² grid cell across the planet (n = 71,566). b Relationship between Pearson residuals from b and raw counts of species present in grid cells.
Humanity’s diverse predatory niche and its ecological consequences

June 2023

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791 Reads

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16 Citations

Communications Biology

Although humans have long been predators with enduring nutritive and cultural relationships with their prey, seldom have conservation ecologists considered the divergent predatory behavior of contemporary, industrialized humans. Recognizing that the number, strength and diversity of predator-prey relationships can profoundly influence biodiversity, here we analyze humanity’s modern day predatory interactions with vertebrates and estimate their ecological consequences. Analysing IUCN ‘use and trade’ data for ~47,000 species, we show that fishers, hunters and other animal collectors prey on more than a third (~15,000 species) of Earth’s vertebrates. Assessed over equivalent ranges, humans exploit up to 300 times more species than comparable non-human predators. Exploitation for the pet trade, medicine, and other uses now affects almost as many species as those targeted for food consumption, and almost 40% of exploited species are threatened by human use. Trait space analyses show that birds and mammals threatened by exploitation occupy a disproportionally large and unique region of ecological trait space, now at risk of loss. These patterns suggest far more species are subject to human-imposed ecological (e.g., landscapes of fear) and evolutionary (e.g., harvest selection) processes than previously considered. Moreover, continued overexploitation will likely bear profound consequences for biodiversity and ecosystem function.


History's legacy: Why future progress in ecology demands a view of the past

July 2022

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399 Reads

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11 Citations

History has profoundly affected the composition, distribution, and abundances of species in contemporary ecosystems. A full understanding of how ecosystems work and change must therefore take history into account. We offer four well‐studied examples illustrating how a knowledge of history has strengthened interpretations of modern systems: the development of molluscan antipredatory defenses in relation to shell‐breaking predators; the North Pacific kelp ecosystem with sea otters, smaller predators, sea urchins, and large herbivores; estuarine ecosystems affected by the decline in oysters and other suspension feeders; and the legacy of extinct large herbivores and frugivores in tropical American forests. Many current ecological problems would greatly benefit from a historical perspective. We highlight four of these: soil depletion and tree stunting in forests related to the disappearance of large consumers; the spread of anoxic dead zones in the ocean, which we argue could be mitigated by restoring predator and suspension‐feeding guilds; ocean acidification, which would be alleviated by more nutrient recycling by consumers in the aerobic ecosystem; and the relation between species diversity and keystone predators, a foundational concept that is complicated by simplified trophic relationships in modern ecosystems.


Genomic basis for skin phenotype and cold adaptation in the extinct Steller’s sea cow

February 2022

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559 Reads

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18 Citations

Science Advances

Steller’s sea cow, an extinct sirenian and one of the largest Quaternary mammals, was described by Georg Steller in 1741 and eradicated by humans within 27 years. Here, we complement Steller’s descriptions with paleogenomic data from 12 individuals. We identified convergent evolution between Steller’s sea cow and cetaceans but not extant sirenians, suggesting a role of several genes in adaptation to cold aquatic (or marine) environments. Among these are inactivations of lipoxygenase genes, which in humans and mouse models cause ichthyosis, a skin disease characterized by a thick, hyperkeratotic epidermis that recapitulates Steller’s sea cows’ reportedly bark-like skin. We also found that Steller’s sea cows’ abundance was continuously declining for tens of thousands of years before their description, implying that environmental changes also contributed to their extinction.


Figure 4. Functional relationships between urchin biomass density (a) and kelp density (b) as a function of the probability of seeing an otter in Sitka Sound in 2018. (Online version in colour.)
Southeast Alaskan kelp forests: inferences of process from large-scale patterns of variation in space and time

January 2022

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243 Reads

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8 Citations

Humans were considered external drivers in much foundational ecological research. A recognition that humans are embedded in the complex interaction networks we study can provide new insight into our ecological paradigms. Here, we use time-series data spanning three decades to explore the effects of human harvesting on otter–urchin–kelp trophic cascades in southeast Alaska. These effects were inferred from variation in sea urchin and kelp abundance following the post fur trade repatriation of otters and a subsequent localized reduction of otters by human harvest in one location. In an example of a classic trophic cascade, otter repatriation was followed by a 99% reduction in urchin biomass density and a greater than 99% increase in kelp density region wide. Recent spatially concentrated harvesting of otters was associated with a localized 70% decline in otter abundance in one location, with urchins increasing and kelps declining in accordance with the spatial pattern of otter occupancy within that region. While the otter–urchin–kelp trophic cascade has been associated with alternative community states at the regional scale, this research highlights how small-scale variability in otter occupancy, ostensibly due to spatial variability in harvesting or the risk landscape for otters, can result in within-region patchiness in these community states.


Fig. 1. Digging by otters changes eelgrass meadows. (A) Otters absent; (B) otters established; and (C) an otter-foraging pit.
Fig 2. Eelgrass populations and locations. Meadow locations with sea otters absent (pale blue circles), recent (<10 years; dark blue circles), and established (20 to 30 years; red circles). STRUCTURE analyses identified two eelgrass populations (K = 2); genetic divergence is likely driven by distance. Pale and dark green bars show the probability of individual population assignment.
Physical disturbance by recovering sea otter populations increases eelgrass genetic diversity

October 2021

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277 Reads

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18 Citations

Science

The importance of disturbance Work in sea otters over the last few decades has transformed our understanding of the importance of specific species, or keystones, as drivers of community structure and stability. Foster et al . took the next step and tested whether otter foraging might influence genetic diversity in an eelgrass ecosystem (see the Perspective by Roman). The authors found that eelgrass genetic diversity was significantly higher where otters were present and that the impact was related to time: Longer otter presence was associated with higher genetic diversity. These results illustrate how the actions of a predator can affect the diversity of a producer in a tropic system. —SNV


Sea otter population collapse in southwest Alaska: assessing ecological covariates, consequences, and causal factors

August 2021

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1,040 Reads

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18 Citations

Sea otter (Enhydra lutris) populations in southwest Alaska declined substantially between about 1990 and the most recent set of surveys in 2015. Here we report changes in the distribution and abundance of sea otters, and covarying patterns in reproduction, mortality, body size and condition, diet and foraging behavior, food availability, health profiles, and exposure to environmental contaminants over this 25‐yr period. The population decline, which resulted in densities on the order of 5% of environmental carrying capacity, ranged from Attu Island in the west to about Castle Cape (on the south side of the Alaska Peninsula) in the east. Remaining sea otters moved closer to shore and into shallow, protected habitats. Reproductive rates appeared unchanged with the decline. Although the demographic cause of the decline was clearly elevated mortality, stranded carcasses were rare or absent. The net rate of energy gain by foraging sea otters, body length and condition, and prey biomass density, all increased after the decline and varied inversely with sea otter population density beyond the area of decline. Sea otters within the area of decline showed no increases in health anomalies, disease, contaminant exposure, or abnormal gene transcription patterns as compared to animals outside the area of decline. These collective findings are inconsistent with nutritional limitation, disease, or environmental contaminants, and consistent with predation (or possibly some other density‐independent factor) as the reason for the sea otter population decline. Our approach and analyses provide a broad conceptual template for thinking about and assessing the causes of wildlife population declines.


Fig. 1. Erosion of long-lived coralline algal reefs across the Aleutian archipelago. (A) Over centuries to millennia, C. nereostratum formed massive reefs that structurally underpinned Aleutian kelp forests. (B) However, these reefs are now eroding because of overgrazing by sea urchins. (C) Area (in square centimeters) of each colony that was grazed to a depth below its regenerative layer (gray bar) versus the area that persisted as living tissue (blue bar). (D) Maximum depth (in millimeters) of individual sea urchin bites on each colony. (E) Depth (in centimeters) of grazing "excavation pits" on the reef. Bars in (C) to (E) are global means ± SE from each island in 2014 (n = 10 surveys/site; n = 2 sites/island or group; n = 8 sites total). (F) Spatial coverage of the coralline algal framework (median and quartiles; whiskers indicate 95% confidence intervals) when assessed at n = 6 islands (n = 20 quadrats/site; n = 4 to 6 sites/island) in 2014 (dark gray bars), 2015 (white bars), and 2017 (light gray bars).
Fig. 3. Effects of seawater temperature and PCO 2 on algal integrity and bioerosion rate. (A) Skeletal density (in milligrams of CaCO 3 per cubic centimeter) of C. nereostratum when cultured for 4 months under various temperatures and PCO 2 levels, including pairs that represent preindustrial (P), modern (M), and predicted near-future (F) conditions specific to the Aleutian Islands (n = 3/treatment). (B) Rate at which large S. polyacanthus consumed C. nereostratum (in milligrams of CaCO 3 per day per square centimeter of alga) during a 20-day grazing assay plotted as a function of the treatments that both experienced for 3 months before and during the assay (n = 9 to 13/treatment). Bars in (A) and (B) are means ± SE.
Keystone predators govern the pathway and pace of climate impacts in a subarctic marine ecosystem

September 2020

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1,242 Reads

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52 Citations

Science

Predator loss and climate change are hallmarks of the Anthropocene yet their interactive effects are largely unknown. Here, we show that massive calcareous reefs, built slowly by the alga Clathromorphum nereostratum over centuries to millennia, are now declining because of the emerging interplay between these two processes. Such reefs, the structural base of Aleutian kelp forests, are rapidly eroding because of overgrazing by herbivores. Historical reconstructions and experiments reveal that overgrazing was initiated by the loss of sea otters, Enhydra lutris (which gave rise to herbivores capable of causing bioerosion), and then accelerated with ocean warming and acidification (which increased per capita lethal grazing by 34 to 60% compared with preindustrial times). Thus, keystone predators can mediate the ways in which climate effects emerge in nature and the pace with which they alter ecosystems.




Citations (78)


... On the other hand, defaunation is a humaninduced process that reduces the abundance and cause extinction of animal species. This threat is linked to hunting, natural resource exploitation, and climate change (Dirzo et al. 2014, Darimont et al. 2023, Pires & Galetti 2023. Mammals are among the most affected groups, with approximately 24% of global species facing some form of exploitation. ...

Reference:

SURVEY OF NON-FLYING MAMMALS IN A SEMI-DECIDUOUS SEASONAL FOREST FRAGMENT AT SÃO FRANCISCO FOREST STATE PARK
Humanity’s diverse predatory niche and its ecological consequences

Communications Biology

... Somewhat unexpectedly, these legacies are often underestimated and understudied by ecologists (Estes & Vermeij, 2022;Lunt & Spooner, 2005). A global review of studies reporting the effects of forest grazing, for example, found that past land use was not considered in roughly a third of them (Öllerer et al., 2019). ...

History's legacy: Why future progress in ecology demands a view of the past

... Some of the reported receptors have previously been identified as lost in early vertebrate lineages, such as SSTR4 in ray-finned fish [35], or in the ancestors of mammals and birds, like QRFPR [36]. Additionally, certain receptors, such as NPFFR2 [37], QRFPR [5], SSTR4 [35] and Npy6r [38], have been reported as lost in other mammals. ...

Genomic basis for skin phenotype and cold adaptation in the extinct Steller’s sea cow

Science Advances

... Interestingly, ecological interactions between sea otters and modern kelp forests represent one of the best examples to demonstrate how ecosystems can evolve or be affected. [38][39][40] However, the recent origin, relative to Eocene/Oligocene mysticetes, of sea otters 41-43 clearly suggests a significant time gaplikely more than 20 Ma without the existence of sea otters or a mammalian analog (e.g. Kolponomos 44 ) in the kelp ecosystem. ...

Southeast Alaskan kelp forests: inferences of process from large-scale patterns of variation in space and time

... In the case that adult shoots are removed in a large disturbance event, the seed bank exists as a backup that can still allow recovery. And in fact, an intermediate level of disturbance can cause increased genetic diversity, further contributing to the resilience of that eelgrass population (Hughes and Stachowicz 2011;Foster et al. 2021). It is well established that prescribed disturbance can be used in terrestrial grassland management to promote biodiversity (Edwards et al. 2007;Valko et al. 2014). ...

Physical disturbance by recovering sea otter populations increases eelgrass genetic diversity

Science

... We dedicate this article to the memory of our esteemed colleague Michael Soulé (1936Soulé ( -2020, a pioneer in conservation biology. Analysis of the experiences and values that animated his life, as well as his contributions to science have been published in the journal, and by the society, that he co-founded and deeply influenced (Crooks et al., 2020;Taylor, 2020). ...

Reflections on Michael Soule, a visionary for conservation biology

Conservation Biology

... Declines of preferred prey resources in turn drive changes in sea otter foraging processes such that sea otters in long-occupied areas generally allocate more time to foraging (Bodkin et al., 2007;Esslinger et al., 2014) and consume a more diverse diet of smaller, lower quality prey (Hale et al., 2019;Laidre & Jameson, 2006;Ostfeld, 1982;Tinker et al., 2008). Shifting to smaller, lower quality, or less available prey may result in reduced energy intake, with consequences for sea otter demographic rates and population growth (Coletti et al., 2016;Hale et al., 2019;Tinker et al., 2008Tinker et al., , 2021Weitzman, 2013). As such, sea otter foraging ecology, prey availability, and otter population dynamics are tightly coupled processes (Estes, 1990;Laidre & Jameson, 2006;Monson et al., 2000). ...

Sea otter population collapse in southwest Alaska: assessing ecological covariates, consequences, and causal factors

... Consequently, while maintaining balanced sea urchin populations at intermediate abundances is key for habitat stability (Bronstein & Loya, 2014), the future of habitats following major trophic cascades alternations is largely dependent on the intensity and duration of disturbance. Just as sea otters exert top-down trophic control over S. polyacanthus populations in the Aleutian kelp forests (Rasher et al., 2020), so does DaSc-associated Philaster exert bottom-up control on diadematoid sea urchins in coral reefs. As current data show that the intensities of recent diadematoid mortalities in the Red Sea and WOI are severe, often reaching 100% and surpassing the intensity of mortalities reported from the Caribbean , it remains to be seen whether these mortalities are transitional or mark the onset of a new era of coral-algal competition in affected regions. ...

Keystone predators govern the pathway and pace of climate impacts in a subarctic marine ecosystem

Science

... Sea otters (Enhydra lutris ssp.) are a particularly salient example of this potential competition, in that they are a keystone species (Paine 1969) whose presence or absence can dramatically influence marine community structure (e.g., . Sea otter recovery may introduce significant new conservation challenges for Federal, State, and Tribal resource managers in areas where sea otters overlap with fisheries or other protected species (e.g., , Raimondi et al. 2015, Estes and Carswell 2020, although sea otter recovery can also result in multiple social, economic, and ecological benefits , Estes et al. 2004, Reisewitz et al. 2006, Wilmers and Estes 2012, Hughes et al. 2013, Markel and Shurin 2015, Gregr et al. 2020). ...

Costs and benefits of living with predators
  • Citing Article
  • June 2020

Science

... The removal of domestic cattle from south Swedish forests during the last 100 years was a signi®cant event in long-term grazing±vegetation interactions and has had a major in¯uence on forest composition and structure (Andersson et al., 1993). Models such as these place present-day conditions in a valuable temporal perspective, and reveal the constantly shifting nature of`base-line' conditions (Davis, 1989). ...

Long-term studies