Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
Review
. 2025 Aug;39(4):e70018.
doi: 10.1111/cobi.70018. Epub 2025 Apr 7.

Opportunities, research gaps, and risks in allogenic ecosystem engineer mimicry

Affiliations
Review

Opportunities, research gaps, and risks in allogenic ecosystem engineer mimicry

Brandi Goss et al. Conserv Biol. 2025 Aug.

Abstract

In an age of anthropogenically driven species loss and increasingly novel ecosystems, ecosystem engineer restoration is a process-based approach to supporting ecosystem function. Many ecosystem engineers have low or declining population sizes. When feasibility and costs impede reintroduction of ecosystem engineers, an alternative may be artificial mimicry of ecosystem engineer structures. Research on mimicry of autogenetic ecosystem engineers, whose physical structure shapes habitat availability and complexity (e.g., tropical corals whose hard skeletons create complex reefs that provide habitat), spans many process scales. However, mimicry of allogenic ecosystem engineers, which shape habitat availability through their behavior (e.g., beavers building dams that influence hydrology), is less well explored. We reviewed the literature to examine the efficacy of artificial mimicry of allogenic ecosystem engineers and gaps in the research. Emerging findings suggest that artificial mimicry could restore physical processes, support focal species, alter biological communities, deliver benefits to landowners and ecosystems, and promote population recovery. However, some studies document the potential for unintended negative consequences for ecosystem engineers or species that use engineered structures or respond to environmental cues produced by engineered structures. Topics requiring additional research include assessing the efficacy of artificial structures as compared with natural structures, evaluating the scalability and cost-effectiveness of mimicry projects, and investigating the potential for unintended consequences with mimicked structures.

Oportunidades, brechas en la investigación y riesgos en el mimetismo de la ingeniería de ecosistemas alógenos Resumen Con la actual pérdida de especies por causas antropogénicas y ecosistemas cada vez más novedosos, la restauración por ingenieros de ecosistemas es un enfoque basado en procesos para apoyar la función de los ecosistemas. Muchos ingenieros de ecosistemas tienen poblaciones reducidas o en declive. Cuando la viabilidad y el costo impiden la reintroducción de ingenieros de ecosistemas, una alternativa puede ser la imitación artificial de estructuras de ingenieros de ecosistemas. La investigación sobre el mimetismo de los ingenieros de ecosistemas autogénicos, cuya estructura física determina la disponibilidad y complejidad del hábitat (por ejemplo, los corales tropicales cuyos esqueletos duros crean arrecifes complejos que proporcionan hábitat), abarca muchas escalas de procesos. Sin embargo, el mimetismo de los ingenieros alógenos de los ecosistemas, que modifican la disponibilidad de hábitats a través de su comportamiento (por ejemplo, los castores que construyen presas que influyen en la hidrología), está menos explorado. Revisamos la bibliografía para examinar la eficacia del mimetismo artificial de los ingenieros de ecosistemas alógenos y los vacíos en la investigación. Los hallazgos emergentes sugieren que el mimetismo artificial podría restaurar los procesos físicos, apoyar a las especies focales, alterar las comunidades biológicas, aportar beneficios a los propietarios de tierras y a los ecosistemas, y promover la recuperación de las poblaciones. Sin embargo, algunos estudios documentan la posibilidad de que se produzcan consecuencias negativas no deseadas para los ingenieros de ecosistemas o las especies que utilizan estructuras artificiales o responden a señales ambientales producidas por estructuras artificiales. Entre los temas que requieren más investigación figuran la evaluación de la eficacia de las estructuras artificiales en comparación con las estructuras naturales, la evaluación de la escalabilidad y rentabilidad de los proyectos de imitación y la investigación de las posibles consecuencias no deseadas de las estructuras imitadas.

【摘要】 在人类活动导致物种丧失、新型生态系统出现的时代, 恢复生态系统工程师是一种基于过程的支持生态系统功能的方法。许多生态系统工程师的种群数量较少或正在下降。当重新引入生态系统工程师面临可行性或成本的阻碍时, 人工模拟生态系统工程师的结构或能作为一种替代方法。自生生态系统工程师的物理结构决定了栖息地可用性和复杂性(如热带珊瑚坚硬的骨骼形成了复杂的珊瑚礁并提供栖息地), 对其进行模拟的研究跨越了许多过程尺度。然而, 模拟通过行为改变栖息地可用性的外源生态系统工程师(如海狸筑坝影响水文)的研究仍较少。我们通过查阅相关文献, 分析了人工模拟外源生态系统工程师的效果, 以及研究中存在的不足。新兴研究表明, 人工模拟可以恢复物理过程、支持目标物种、改变生物群落、为土地所有者和生态系统带来收益, 并促进种群恢复。然而, 一些研究指出, 这些人工模拟对于使用工程结构或对工程结构产生的环境线索做出反应的生态系统工程师或物种来说, 可能会产生意想不到的负面影响。仍需深入研究的话题包括评估人工结构与自然结构相比的效果、评估模拟项目的可扩展性和成本效益, 以及调查模拟结构可能产生的意外后果等。【翻译:胡怡思;审校:聂永刚】.

Keywords: allogenic ecosystem engineers; artificial mimicry; ecosistemas alógenos; ecosistemas novedosos; evolutionary traps; ingeniería de ecosistemas; mimetismo artificial; novel ecosystems; restauración; restoration; trampas evolutivas; 人工模拟; 外源生态系统工程师; 恢复; 新型生态系统; 演化陷阱.

PubMed Disclaimer

Figures

FIGURE 1
FIGURE 1
Comparison of existing research on natural and mimicked allogenic and autogenic engineer structures in a variety of research areas (spatial structure or design, research on effects of the physical shape, distribution, or construction materials of the natural or artificial structure; physical process, research on the effect of structures on physical processes; population effects, research on density of organisms, habitat or refuge creation for organisms, or primary production; community effects, research on community metrics, such as diversity, community composition, and colonization rates; ecosystem services, research on ecosystem processes, e.g., nutrient cycling and litter decomposition, and services, e.g., groundwater recharge, shoreline protection, ecotourism; EU, experimental use of an artificial structure rather than studies on artificial structures used in a restoration capacity; dark green shading indicates a research area with at least 3 studies on 3 different topics under that research area, light green shading indicates that one of these criteria were not met, yellow shading indicates that both of these criteria were not met). To illustrate the extent of research for each of allogenic and autogenic engineers, for each engineer type we choose three examples that differ in their habitat types (e.g., in terms of terrestrial vs. aquatic from freshwater to estuarine to marine, or tropical to temperate) and types of engineering functions. References: 1(Übernickel et al. 2021); 2(Yoshihara et al. 2010); 3(Machicote et al. 2004); 4(Platt et al. 2016); 5(Bowker et al. 2013); 6(Beca et al. 2022); 7(Fleming et al. 2014); 8(Linley et al. 2024); 9(Pike and Mitchell 2013); 10(Galvez Bravo et al. 2009); 11(Mallen‐Cooper et al. 2019); 12(Davidson and Lightfoot 2008); 13(Riding and Belthoff 2015); 14(Keppers et al. 2008); 15(Ebrahimi et al. 2012); 16(Nadeau et al. 2015); 17(Fromant and Bost 2020); 18(Wilson 1986); 19(Bourgeois et al. 2015); 20(Smith et al. 2005); 21(Grillet et al. 2010); 22(Souter et al. 2004); 23(Mosepele et al. 2009); 24(Kerley and Landman 2006); 25(Valeix et al. 2011); 26(Pringle 2008); 27(Coverdale et al. 2016); 28(Poulsen et al. 2017); 29(Stommel et al. 2016); 30(McComb et al. 1990); 31(Swinnen et al. 2019); 32(Ronnquist 2021); 33(Brazier et al. 2021); 34(Larsen et al. 2021); 35(Romansic et al. 2021); 36(Fairfax and Whittle 2020); 37(Wade et al. 2020); 38(Munir and Westbrook 2021); 39(Corline et al. 2023); 40(Weber et al. 2017); 41(Bouwes et al. 2018); 42(Orr et al. 2020); 43(Pollock et al. 2014); 44(Graham and Nash 2013); 45(Komyakova et al. 2013); 46(Escudero et al. 2021); 47(Oberdorfer and Buddemeier 1986); 48(Storlazzi et al. 2004); 49(Storlazzi et al. 2009); 50(Davis et al. 2011); 51(Wild et al. 2004); 52(Brooks et al. 2007); 53(Coker et al. 2014); 54(Rädecker et al. 2015); 55(Komyakova et al. 2019); 56(Perkol‐Finkel et al. 2006); 57(Walsh 1985); 58(Ambrose 1994); 59(Sherman et al. 2002); 60(Charbonnel et al. 2002); 61(Dewsbury and Fourqurean 2010); 62(Ambrose and Anderson 1990); 63(Falcão et al. 2009); 64(Andskog et al. 2023); 65(Ng et al. 2017); 66(Fabi et al. 2002); 67(Baynes and M. Szmant 1989); 68(Kim et al. 2020); 69(Belhassen et al. 2017); 70(Tynyakov et al. 2017); 71(Peterson et al. 2004); 72(Chen et al. 2007); 73(Christianen et al. 2013); 74(Hovel et al. 2002); 75(Bowden et al. 2001); 76(Bell et al. 1988); 77(Bos et al. 2007); 78(van Katwijk et al. 2010); 79(Prasad et al. 2019); 80(Healey and Hovel 2004); 81(Bologna and Heck 2000); 82(Upston and Booth 2003); 83(Ambo‐Rappe and Rani 2018); 84(Villanueva et al. 2023); 85(Carus et al. 2022); 86(Layman et al. 2016); 87(Virnstein and Curran 1986); 88(Nakamura et al. 2007); 89(Bartholomew 2002); 90(Shahbudin et al. 2011); 91Marin‐Diaz et al. (2021); 92(John et al. 2016); 93(Griffitt et al. 1999); 94(Roncolato et al. 2024); 95(Grabowski and Peterson 2007); 96(Reidenbach et al. 2013); 97(Pfirrmann and Seitz 2019); 98(Posey et al. 1999); 99(Lenihan 1999); 100(Walles et al. 2016); 101(Goelz et al. 2020); 102(Hogan and Reidenbach 2022); 103(Soniat et al. 2004); 104(Furlong 2012); 105(Cannon et al. 2022); 106(Smith et al. 2023); 107(Brown et al. 2014); 108(Hammond et al. 2020); 109(Pierson and Eggleston 2014); 110(Wellman et al. 2022).
FIGURE 2
FIGURE 2
Examples of artificial allogenic ecosystem engineer structures: (a) beaver dam analogs on Sugar Creek, Scott Valley, California (photo by an author), (b) nesting box on the Putah Creek nest box highway (photo from UC Davis Museum of Wildlife and Fish Biology Putah Creek Nest Box Highway Program), and (c) burrowing owl emerging from an artificial burrow (photo from Adobe stock). These structures can range in the naturalness of the construction materials, with the examples shown ranging from the most natural to the least natural from left to right.

References

    1. Aitken, K. E. H. , & Martin, K. (2007). The importance of excavators in hole‐nesting communities: Availability and use of natural tree holes in old mixed forests of western Canada. Journal of Ornithology, 148, S425–S434.
    1. Ambo‐Rappe, R. , & Rani, C. (2018). Physical structure of artificial seagrass affects macrozoobenthic community recruitment. Journal of Physics: Conference Series, 979, Article 012006. 10.1088/1742-6596/979/1/012006 - DOI
    1. Ambrose, R. F. (1994). Mitigating the effects of a coastal power plant on a kelp forest community: Rationale and requirements for an artificial reef. Bulletin of Marine Science, 55, 694–708.
    1. Ambrose, R. F. , & Anderson, T. W. (1990). Influence of an artificial reef on the surrounding infaunal community. Marine Biology, 107, 41–52.
    1. Andskog, M. A. , Layman, C. , & Allgeier, J. E. (2023). Seagrass production around artificial reefs is resistant to human stressors. Proceedings of the Royal Society B: Biological Sciences, 290, Article 20230803. - PMC - PubMed