Building a systemic environmental monitoring and indicators for sustainability: What has the ecological network approach to offer?

2012 ◽  
Vol 15 (1) ◽  
pp. 140-148 ◽  
Author(s):  
Antonio Bodini
2020 ◽  
Author(s):  
Jean Paul Metzger ◽  
Pedro Fidelman ◽  
Claudia Sattler ◽  
Barbara Schröter ◽  
Martine Maron ◽  
...  

2019 ◽  
Vol 54 ◽  
pp. 113-123 ◽  
Author(s):  
Matthew Hamilton ◽  
Alexandra Paige Fischer ◽  
Alan Ager

2021 ◽  
Vol 125 ◽  
pp. 107487
Author(s):  
Shuang Wang ◽  
Maoquan Wu ◽  
Mengmeng Hu ◽  
Chen Fan ◽  
Tao Wang ◽  
...  

2021 ◽  
Vol 12 (1) ◽  
Author(s):  
Aislyn A. Keyes ◽  
John P. McLaughlin ◽  
Allison K. Barner ◽  
Laura E. Dee

2014 ◽  
Vol 83 (6) ◽  
pp. 1409-1417 ◽  
Author(s):  
Amanda D. Rodewald ◽  
Rudolf P. Rohr ◽  
Miguel A. Fortuna ◽  
Jordi Bascompte

1995 ◽  
Vol 33 (1-3) ◽  
pp. 179-193 ◽  
Author(s):  
John Linehan ◽  
Meir Gross ◽  
John Finn

2019 ◽  
Vol 2 ◽  
Author(s):  
Gabor Pozsgai ◽  
Ibtissem Ben Fekih ◽  
Gabor Lovei

Whereas they are of high ecological, conservation, and agricultural importance, ground beetles (Coleoptera: Carabidae) are amongst the organisms declining rapidly as a result of human activities. Since they are part of a complex ecological network –in which other taxa’s survival may depend on them, or they may depend on other taxa –in the case of their, hypothetical, extinction these connections would be impaired. In order to gain insight how different taxa would be affected by the extinction of carabids, and thus, how ecosystem functions would be altered, we conceptualised a network between ground beetles and all other organisms they are directly connected with. We used published literature data in building our network, thus interaction occurrences are likely to be skewed by research interest. Based on a single database search, we found 238 carabid species interacting with 395 other species, including plants (72), fungi (53), animals (286), and 7 other Eucaryota. Of the 817 described interactions, in 235 cases, carabids were prey, mostly for birds and mammals. Hosting ectoparasites was the second most frequent relationship, with 144 connections. Most of these connections were to Laboulbeniales fungi. Further, detailed searches on carabid – fungus relationshipsyielded over 700 different interactions. Carabids were listed to consume 88 other taxa, including many plants; an additional 200 records refer to seed predation by ground beetles, mostly from the Zabrini and Harpalini tribes. The specificity of seed dispersal, and therefore assessing the extent plant species depend on carabids was not possiblefrom this database. Carabids also visit flowers and even pollinate them in 12 cases. Amara, Harpalus and Cicindela genera had the most records of interactions with other species. Although this list of interactions between Carabidae and other taxa is incomplete, it shows that many other organisms can depend on ground beetles, and some (mostly fungi) have specific relationship with them. The apparent information gaps on symbiotic and competitive interactions, and the geographical bias towards Europe and North America open doors for further research in these areas.


2021 ◽  
Vol 12 (1) ◽  
Author(s):  
Aislyn A. Keyes ◽  
John P. McLaughlin ◽  
Allison K. Barner ◽  
Laura E. Dee

AbstractHuman-driven threats are changing biodiversity, impacting ecosystem services. The loss of one species can trigger secondary extinctions of additional species, because species interact–yet the consequences of these secondary extinctions for services remain underexplored. Herein, we compare robustness of food webs and the ecosystem services (hereafter ‘services’) they provide; and investigate factors determining service responses to secondary extinctions. Simulating twelve extinction scenarios for estuarine food webs with seven services, we find that food web and service robustness are highly correlated, but that robustness varies across services depending on their trophic level and redundancy. Further, we find that species providing services do not play a critical role in stabilizing food webs – whereas species playing supporting roles in services through interactions are critical to the robustness of both food webs and services. Together, our results reveal indirect risks to services through secondary species losses and predictable differences in vulnerability across services.


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