Wolves and the Ecology of Fear: Can Predation Risk Structure
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Predators As Agents of Selection and Diversification
diversity Review Predators as Agents of Selection and Diversification Jerald B. Johnson * and Mark C. Belk Evolutionary Ecology Laboratories, Department of Biology, Brigham Young University, Provo, UT 84602, USA; [email protected] * Correspondence: [email protected]; Tel.: +1-801-422-4502 Received: 6 October 2020; Accepted: 29 October 2020; Published: 31 October 2020 Abstract: Predation is ubiquitous in nature and can be an important component of both ecological and evolutionary interactions. One of the most striking features of predators is how often they cause evolutionary diversification in natural systems. Here, we review several ways that this can occur, exploring empirical evidence and suggesting promising areas for future work. We also introduce several papers recently accepted in Diversity that demonstrate just how important and varied predation can be as an agent of natural selection. We conclude that there is still much to be done in this field, especially in areas where multiple predator species prey upon common prey, in certain taxonomic groups where we still know very little, and in an overall effort to actually quantify mortality rates and the strength of natural selection in the wild. Keywords: adaptation; mortality rates; natural selection; predation; prey 1. Introduction In the history of life, a key evolutionary innovation was the ability of some organisms to acquire energy and nutrients by killing and consuming other organisms [1–3]. This phenomenon of predation has evolved independently, multiple times across all known major lineages of life, both extinct and extant [1,2,4]. Quite simply, predators are ubiquitous agents of natural selection. Not surprisingly, prey species have evolved a variety of traits to avoid predation, including traits to avoid detection [4–6], to escape from predators [4,7], to withstand harm from attack [4], to deter predators [4,8], and to confuse or deceive predators [4,8]. -
Effects of Human Disturbance on Terrestrial Apex Predators
diversity Review Effects of Human Disturbance on Terrestrial Apex Predators Andrés Ordiz 1,2,* , Malin Aronsson 1,3, Jens Persson 1 , Ole-Gunnar Støen 4, Jon E. Swenson 2 and Jonas Kindberg 4,5 1 Grimsö Wildlife Research Station, Department of Ecology, Swedish University of Agricultural Sciences, SE-730 91 Riddarhyttan, Sweden; [email protected] (M.A.); [email protected] (J.P.) 2 Faculty of Environmental Sciences and Natural Resource Management, Norwegian University of Life Sciences, Postbox 5003, NO-1432 Ås, Norway; [email protected] 3 Department of Zoology, Stockholm University, SE-10691 Stockholm, Sweden 4 Norwegian Institute for Nature Research, NO-7485 Trondheim, Norway; [email protected] (O.-G.S.); [email protected] (J.K.) 5 Department of Wildlife, Fish, and Environmental Studies, Swedish University of Agricultural Sciences, SE-901 83 Umeå, Sweden * Correspondence: [email protected] Abstract: The effects of human disturbance spread over virtually all ecosystems and ecological communities on Earth. In this review, we focus on the effects of human disturbance on terrestrial apex predators. We summarize their ecological role in nature and how they respond to different sources of human disturbance. Apex predators control their prey and smaller predators numerically and via behavioral changes to avoid predation risk, which in turn can affect lower trophic levels. Crucially, reducing population numbers and triggering behavioral responses are also the effects that human disturbance causes to apex predators, which may in turn influence their ecological role. Some populations continue to be at the brink of extinction, but others are partially recovering former ranges, via natural recolonization and through reintroductions. -
Debris the Science and Changing Perceptions of Dead Trees by Alexander Evans and Robert Perschel
An Appreciation of Debris The Science and Changing Perceptions of Dead Trees By Alexander Evans and Robert Perschel oarse woody debris. To most people, two Coarse woody debris (CWD) is wood in the forest that’s no of the three words in that phrase have longer part of a living tree. Rather than being dead, this wood negative connotations. Debris is the worst is an important source of life in the forest. Foresters who value offender, suggesting random junk strewn it for its ecological functions have been searching for new terms about. When the debris is coarse, it’s even for CWD, and you’ll hear it referred to as biomass, dead wood, worse – it’s unrefined, it’s big. coarse woody material, and even retained organic matter. VIRGINIA BARLOW 44 Northern Woodlands / Winter 2008 Harry Dwyer, a forester in Fayette, Maine, likens the lan- as a seed bed for trees and plants, a mulch layer, and a slow- guage predicament to that of another formerly maligned mate- release fertilizer. Decomposing fungi depend on dead wood for rial: garden waste. He said, “You could look at a pile of rotting nutrients and moisture, and in turn many trees rely on mutu- vegetables as garbage, or you could note its value and call it alistic relationships with mycorrhizal fungi. Nitrogen fixation compost.” Digging into a rotten log in his woodlot, Dwyer in CWM by microbes (both anaerobic and microaerophyllic displays some of the dark, wet material in his hand. “It doesn’t bacteria) provides this important element in both terrestrial matter what you call this – coarse woody debris, coarse woody and aquatic ecosystems. -
AN ABSTRACT of the THESIS of Douglas William Havlina for The
AN ABSTRACT OF THE THESIS OF Douglas William Havlina for the degree of Master of Science in Rangeland Resources presented on January 27, 1995 Title: Fire Effects on Vegetation Diversity, Structure, and Successional Dynamics in Shrub-Steppe and Mixed Conifer Environments of the Hells Canyon, Idaho. Abstract approved: The effects of fire severity on post-fire succession and shrub demography were quantified in shrub-steppe grasslands and subalpine forests in the Hells Canyon of the Payette National Forest, Idaho. Following the 1988 Eagle Bar Fire, species frequency, community diversity, fire adaptations, and stand ages were quantified at 12 plots in burned and unburned forests. Pre-fire composition was dominated by Pseudotsuga menziesii, Pinus contorta, Abies grandis, and Abies lasiocarpa in the overstory. Pre- fire basal area ranged from 41 to 80 m 2 ha-1 . Pre-fire stand ages ranged from 71 years in Abies lasiocarpa forests to > 200 years in Pseudotsuga menziesii stands. Fire scenarios which were sampled consisted of: (1) complete stand-replacement fires; (2) partial stand- replacement fires; and (3) unburned forests (control). Partial stand-replacement forests were characterized by significantly higher mean species diversity and richness (H'=3.16, S=36) than complete stand-replacement (H'=2.78, S=27) or unburned forests (H=2.26, S=15). Vegetation preferentially established in burned areas along a gradient of fire severity according to adapted fire guilds. Single-storied forests dominated by Pinus contorta and Abies lasiocarpa typified stand-replacement fire scenarios, with mean ages ranging from 99 to 159 years corresponding to fire return intervals common in this type. -
Influence of Coarse Woody Debris on Seedlings and Saplings in A
INFLUENCE OF COARSE WOODY DEBRIS ON SEEDLINGS AND SAPLINGS IN A PINUS PALUSTRIS WOODLAND by ALEXANDRA LOGAN JUSTIN L. HART, COMMITTEE CHAIR MATTHEW C. LAFEVOR ARVIND A.R. BHUTA A THESIS Submitted in partial fulfillment of the requirements for the degree of Master of Science in the Department of Geography in the Graduate School of The University of Alabama TUSCALOOSA, ALABAMA 2020 Copyright Alexandra Logan 2020 ALL RIGHTS RESERVED 2 ABSTRACT Coarse woody debris (CWD) has beneficial effects on plant growth and establishment. Longleaf pine (Pinus palustris Mill.) stands support relatively low amounts of CWD — 2 to 30 m3 ha-1. In April 2011, an EF3 tornado passed through the Oakmulgee Ranger District of the Talladega National Forest in the Fall Line Hills of Alabama. This disturbance resulted in the large addition of CWD to a longleaf pine woodland, and a rare opportunity to analyze how CWD can influence a managed, pine woodland. The goal of this study was to examine the effect of CWD on woody plant richness, density, and growth rate (quantified by height) in a longleaf pine woodland that experienced a catastrophic wind disturbance. A total of three 1 m2 quadrats were established against either side of a piece of CWD (> 3 m in length and ≥ 10 cm in diameter). Another quadrat was established at least 3 m away from the focal CWD piece. For each plot, the presence and height of every woody plant (< 5 cm dbh) were recorded. Sapling density, oak and hickory density, and organic matter were all found to be significantly higher in quadrats adjacent to CWD than away (all p < 0.05). -
A Review of Planktivorous Fishes: Their Evolution, Feeding Behaviours, Selectivities, and Impacts
Hydrobiologia 146: 97-167 (1987) 97 0 Dr W. Junk Publishers, Dordrecht - Printed in the Netherlands A review of planktivorous fishes: Their evolution, feeding behaviours, selectivities, and impacts I Xavier Lazzaro ORSTOM (Institut Français de Recherche Scientifique pour le Développement eri Coopération), 213, rue Lu Fayette, 75480 Paris Cedex IO, France Present address: Laboratorio de Limrzologia, Centro de Recursos Hidricob e Ecologia Aplicada, Departamento de Hidraulica e Sarzeamento, Universidade de São Paulo, AV,DI: Carlos Botelho, 1465, São Carlos, Sï? 13560, Brazil t’ Mail address: CI? 337, São Carlos, SI? 13560, Brazil Keywords: planktivorous fish, feeding behaviours, feeding selectivities, electivity indices, fish-plankton interactions, predator-prey models Mots clés: poissons planctophages, comportements alimentaires, sélectivités alimentaires, indices d’électivité, interactions poissons-pltpcton, modèles prédateurs-proies I Résumé La vision classique des limnologistes fut de considérer les interactions cntre les composants des écosystè- mes lacustres comme un flux d’influence unidirectionnel des sels nutritifs vers le phytoplancton, le zoo- plancton, et finalement les poissons, par l’intermédiaire de processus de contrôle successivement physiqucs, chimiques, puis biologiques (StraSkraba, 1967). L‘effet exercé par les poissons plaiictophages sur les commu- nautés zoo- et phytoplanctoniques ne fut reconnu qu’à partir des travaux de HrbáEek et al. (1961), HrbAEek (1962), Brooks & Dodson (1965), et StraSkraba (1965). Ces auteurs montrèrent (1) que dans les étangs et lacs en présence de poissons planctophages prédateurs visuels. les conimuiiautés‘zooplanctoniques étaient com- posées d’espèces de plus petites tailles que celles présentes dans les milieux dépourvus de planctophages et, (2) que les communautés zooplanctoniques résultantes, composées d’espèces de petites tailles, influençaient les communautés phytoplanctoniques. -
Environmental Limits Page 1
POST Report 370 January 2011 Living with Environmental Limits Page 1 Summary Human well-being is dependent upon assessment approaches. However, where renewable natural resources. Agricultural there is a risk of thresholds being systems, for example, depend upon plant breached and potentially irreversible productivity, soil, the water cycle, the impacts occurring, additional policy nitrogen, sulphur and phosphorus nutrient safeguards to maintain natural resource cycles and a stable climate. Renewable systems within environmental limits are natural resources can be subject to required. biological and physical thresholds beyond which irreversible changes in benefit Managing ecosystems to maximise one provision may occur. These are difficult to particular benefit, such as food provision, define and many are likely to be identified can result in declines in other benefits. only once crossed. An environmental limit The evidence base is not yet sufficient to is usually interpreted as the point or range determine the most effective ways to of conditions beyond which there is a maintain benefit provision within significant risk of thresholds being environmental limits, but a range of policy exceeded and unacceptable changes responses are seeking to optimise multiple occurring.1 benefit provision, including: Biodiversity loss, climate change and a agri-environment schemes range of other pressures are affecting generic measures to enhance renewable natural resources. If biodiversity, which may increase governments do not effectively monitor the the capacity of natural resource use and degradation of natural resource systems to adapt to environmental systems in national account frameworks, change the probability of costs arising from the use of ecological processes to exploiting natural resources beyond increase overall natural system environmental limits is not taken into resilience to address problems account. -
Human Involvement in Food Webs*
EG35CH01-Strong ARI 13 September 2010 10:20 Human Involvement in Food Webs∗ Donald R. Strong1 and Kenneth T. Frank2 1Department of Evolution and Ecology, University of California, Davis, California 95616; email: [email protected] 2Bedford Institute of Oceanography, Ocean Sciences Division, Dartmouth, Nova Scotia B2Y 4A2, Canada; email: [email protected] Annu. Rev. Environ. Resour. 2010. 35:1–23 Key Words First published online as a Review in Advance on bottom-up, fisheries, intraguild predation, mesopredator, top-down, July 1, 2010 trophic cascade The Annual Review of Environment and Resources is online at environ.annualreviews.org Abstract This article’s doi: Human involvement in food webs has been profound, bringing about 10.1146/annurev-environ-031809-133103 enormous and disproportionate losses of large apex predators on land Copyright c 2010 by Annual Reviews. and in water. The losses have modified or even eliminated concatena- All rights reserved tions of indirect interactions propagating from predators to herbivores 1543-5938/10/1121-0001$20.00 to plants, inter alia. Food webs are a synthesis of bottom-up energy and ∗This article was co-authored by an employee of nutrient flow from plant producers to consumers and top-down regula- a British Commonwealth government as part of tion of producers by consumers. The trophic cascade is the simplest top- his official duties and is therefore subject to down interaction and accounts for a great deal of what is known about Crown Copyright. food webs. In three-link cascades, predators suppress herbivores, re- leasing plants. In longer cascades, predators can suppress smaller meso- by UNIVERSITY OF IDAHO LIBRARY on 03/21/11. -
Can More K-Selected Species Be Better Invaders?
Diversity and Distributions, (Diversity Distrib.) (2007) 13, 535–543 Blackwell Publishing Ltd BIODIVERSITY Can more K-selected species be better RESEARCH invaders? A case study of fruit flies in La Réunion Pierre-François Duyck1*, Patrice David2 and Serge Quilici1 1UMR 53 Ӷ Peuplements Végétaux et ABSTRACT Bio-agresseurs en Milieu Tropical ӷ CIRAD Invasive species are often said to be r-selected. However, invaders must sometimes Pôle de Protection des Plantes (3P), 7 chemin de l’IRAT, 97410 St Pierre, La Réunion, France, compete with related resident species. In this case invaders should present combina- 2UMR 5175, CNRS Centre d’Ecologie tions of life-history traits that give them higher competitive ability than residents, Fonctionnelle et Evolutive (CEFE), 1919 route de even at the expense of lower colonization ability. We test this prediction by compar- Mende, 34293 Montpellier Cedex, France ing life-history traits among four fruit fly species, one endemic and three successive invaders, in La Réunion Island. Recent invaders tend to produce fewer, but larger, juveniles, delay the onset but increase the duration of reproduction, survive longer, and senesce more slowly than earlier ones. These traits are associated with higher ranks in a competitive hierarchy established in a previous study. However, the endemic species, now nearly extinct in the island, is inferior to the other three with respect to both competition and colonization traits, violating the trade-off assumption. Our results overall suggest that the key traits for invasion in this system were those that *Correspondence: Pierre-François Duyck, favoured competition rather than colonization. CIRAD 3P, 7, chemin de l’IRAT, 97410, Keywords St Pierre, La Réunion Island, France. -
Bibliography
Bibliography Abella, S. R. 2010. Disturbance and plant succession in the Mojave and Sonoran Deserts of the American Southwest. International Journal of Environmental Research and Public Health 7:1248—1284. Abella, S. R., D. J. Craig, L. P. Chiquoine, K. A. Prengaman, S. M. Schmid, and T. M. Embrey. 2011. Relationships of native desert plants with red brome (Bromus rubens): Toward identifying invasion-reducing species. Invasive Plant Science and Management 4:115—124. Abella, S. R., N. A. Fisichelli, S. M. Schmid, T. M. Embrey, D. L. Hughson, and J. Cipra. 2015. Status and management of non-native plant invasion in three of the largest national parks in the United States. Nature Conservation 10:71—94. Available: https://doi.org/10.3897/natureconservation.10.4407 Abella, S. R., A. A. Suazo, C. M. Norman, and A. C. Newton. 2013. Treatment alternatives and timing affect seeds of African mustard (Brassica tournefortii), an invasive forb in American Southwest arid lands. Invasive Plant Science and Management 6:559—567. Available: https://doi.org/10.1614/IPSM-D-13-00022.1 Abrahamson, I. 2014. Arctostaphylos manzanita. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, Fire Effects Information System (Online). plants/shrub/arcman/all.html Ackerman, T. L. 1979. Germination and survival of perennial plant species in the Mojave Desert. The Southwestern Naturalist 24:399—408. Adams, A. W. 1975. A brief history of juniper and shrub populations in southern Oregon. Report No. 6. Oregon State Wildlife Commission, Corvallis, OR. Adams, L. 1962. Planting depths for seeds of three species of Ceanothus. -
Herbivore Physiological Response to Predation Risk and Implications for Ecosystem Nutrient Dynamics
Herbivore physiological response to predation risk and implications for ecosystem nutrient dynamics Dror Hawlena and Oswald J. Schmitz1 School of Forestry and Environmental Studies, Yale University, New Haven, CT 06511 Communicated by Thomas W. Schoener, University of California, Davis, CA, June 29, 2010 (received for review January 4, 2010) The process of nutrient transfer throughan ecosystem is an important lower the quantity of energy that can be allocated to production determinant of production, food-chain length, and species diversity. (20–23). Consequently, stress-induced constraints on herbivore The general view is that the rate and efficiency of nutrient transfer up production should lower the demand for N-rich proteins (24). the food chain is constrained by herbivore-specific capacity to secure Herbivores also have low capacity to store excess nutrients (24), N-rich compounds for survival and production. Using feeding trials and hence should seek plants with high digestible carbohydrate with artificial food, we show, however, that physiological stress- content to minimize the costs of ingesting and excreting excess N. response of grasshopper herbivores to spider predation risk alters the Such stress-induced shift in nutrient demand may be especially nature of the nutrient constraint. Grasshoppers facing predation risk important in terrestrial systems in which digestible carbohydrate had higher metabolic rates than control grasshoppers. Elevated represents a small fraction of total plant carbohydrate-C, and may metabolism accordingly increased requirements for dietary digestible be limiting even under risk-free conditions (25). Moreover, stress carbohydrate-C to fuel-heightened energy demands. Moreover, di- responses include break down of body proteins to produce glucose gestible carbohydrate-C comprises a small fraction of total plant (i.e., gluconeogenesis) (14), which requires excretion of N-rich tissue-C content, so nutrient transfer between plants and herbivores waste compounds (ammonia or primary amines) (26). -
The Ecological Role of Coarse Woody Debris an Overview of The
WORKING PAPER 30 The Ecological Role of Coarse Woody Debris An Overview of the Ecological Importance of CWD in BC Forests 1997 Ministry of Forests Research Program The Ecological Role of Coarse Woody Debris An Overview of the Ecological Importance of CWD in BC Forests Victoria Stevens Ministry of Forests Research Program The use of trade, firm, or corporation names in this publication is for the information and convenience of the reader. Such use does not constitute an official endorsement or approval by the Government of British Columbia of any product or service to the exlusion of any others that may also be suitable. Contents of this report are presented for discussion purposes only. Citation Stevens, Victoria. 1997. The ecological role of coarse woody debris: an overview of the ecological importance of CWD in B.C. forests. Res. Br., B.C. Min. For., Victoria, B.C. Work. Pap. 30/1997. Compiled by Victoria Stevens for B.C. Ministry of Forests Research Branch 31 Bastion Square Victoria, B.C. V8W 3E7 Copies of this report may be obtained, depending upon supply, from: B.C. Ministry of Forests Forestry Division Services Branch Production Resources 595 Pandora Avenue, 1st Floor Victoria, B.C. V8W 3E7 © 1997 Province of British Columbia The contents of this report may not be cited in whole or in part without the approval of the Director of Research, B.C. Ministry of Forests, Victoria, B.C. ACKNOWLEDGEMENTS Plunging into a subject as complex as ecological roles of coarse woody debris is not an activity lending itself to solitude. This paper has been at least partially digested by a large number of readers and greatly improved by the suggestions of many.