مقاله انگلیسی رایگان در مورد خدمات اکوسیستم و تنوع زیستی – الزویر 2020

 

مشخصات مقاله
ترجمه عنوان مقاله حفظ خدمات اکوسیستم و تنوع زیستی: اندازه گیری جایگزین های مربوط به تقسیم بودجه های حفاظت
عنوان انگلیسی مقاله Conserving ecosystem services and biodiversity: Measuring the tradeoffs involved in splitting conservation budgets
انتشار مقاله سال 2020
تعداد صفحات مقاله انگلیسی 8 صفحه
هزینه دانلود مقاله انگلیسی رایگان میباشد.
پایگاه داده نشریه الزویر
نوع نگارش مقاله
مقاله پژوهشی (Research Article)
مقاله بیس این مقاله بیس نمیباشد
نمایه (index) Scopus – Master Journals List – JCR
نوع مقاله ISI
فرمت مقاله انگلیسی  PDF
ایمپکت فاکتور(IF)
6.401 در سال 2019
شاخص H_index 46 در سال 2020
شاخص SJR 2.151 در سال 2019
شناسه ISSN 2212-0416
شاخص Quartile (چارک) Q1 در سال 2019
مدل مفهومی ندارد
پرسشنامه ندارد
متغیر ندارد
رفرنس دارد
رشته های مرتبط مهندسی محیط زیست
گرایش های مرتبط زیستگاه ها و تنوع زیستی
نوع ارائه مقاله
ژورنال
مجله  خدمات اکوسیستم – Ecosystem Services
دانشگاه  Department of Earth and Environmental Systems, University of the South, Sewanee, TN, USA
کلمات کلیدی تنوع زیستی، خدمات اکوسیستم، برنامه ربزی حفاظت
کلمات کلیدی انگلیسی Biodiversity، Ecosystem services، Conservation planning
شناسه دیجیتال – doi
https://doi.org/10.1016/j.ecoser.2020.101063
کد محصول E14656
وضعیت ترجمه مقاله  ترجمه آماده این مقاله موجود نمیباشد. میتوانید از طریق دکمه پایین سفارش دهید.
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فهرست مطالب مقاله:
Abstract
1. Introduction
2. Methods
3. Results
4. Discussion and conclusions
Declaration of Competing Interest
Acknowledgements
Appendices
References

بخشی از متن مقاله:
Abstract

Conservation organizations increasingly target ecosystem services alongside biodiversity, yet it remains unclear whether ecosystem service goals reinforce or detract from those for biodiversity. We assess tradeoffs between biodiversity and ecosystem services and test the hypothesis that the severity of this tradeoff is a function the breadth of taxa and ecosystem services targeted. We identify optimal conserved lands networks for four taxa, four ecosystem services, and all possible combinations of each. We then assess the amount of biodiversity and ecosystem service contained within each network, its conservation cost, and its overlap with every other network. We find that overlap varies widely across individual ecosystem services and taxa, and that networks targeting multiple services contain more biodiversity than networks targeting a single service. Safeguarding a given amount of ecosystem service and biodiversity through joint optimization requires a 13% increase in conservation budgets relative to achieving targets for biodiversity alone, and results in a 22% budget savings relative to achieving targets for each though separate efforts. We conclude that including ecosystem services goals alongside those for biodiversity is likely have a net positive impact on biodiversity, especially when a broad suite of services are targeted.

Introduction

Supporting the wellbeing of a growing human population while avoiding biodiversity loss is a central challenge of sustainable development (ICSU, 2015; Millennium Ecosystem Assessment, 2005; Steffen et al., 2015). Ecosystem services (ES) are the benefits that people derive from nature (Daily, 1997; Millennium Ecosystem Assessment, 2005). Development-driven environmental degradation is rapidly eroding both biodiversity (Butchart et al., 2010; Ceballos et al., 2015; Newbold et al., 2015; Pimm et al., 2014) and those ecosystem services whose value is not captured in markets (Foley et al., 2005; Millennium Ecosystem Assessment, 2005; Sutton et al., 2016). By making explicit the link between the well-being of people and nature, ES have the potential to serve as common ground for human development and conservation (Millennium Ecosystem Assessment, 2005). As a result, conservation organizations and governments are increasingly prioritizing ecosystem services (Bateman et al., 2013; Donovan et al., 2015; Guerry et al., 2015; Ruckelshaus et al., 2013). How will an ES focus impact biodiversity? Considerable debate has arisen among the conservation community over whether an ES approach is undercutting or bolstering traditional biodiversity goals (McCauley, 2006; Reyers et al., 2012). On the one hand, the resources once allocated specifically to protecting nature for its own sake are now being used to protect the parts of nature that have the highest utility to people.

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