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Journal articles on the topic 'Biodiversity restoration'

Author: Grafiati

Published: 2 June 2025

Last updated: 31 July 2025

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1

Santa-Regina. "RESTORATION OF BIODIVERSITY AND ECOSYSTEM." American Journal of Engineering and Applied Sciences 6, no. 1 (2013): 69–86. http://dx.doi.org/10.3844/ajeassp.2013.69.86.

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2

Handel, Steven N., George R. Robinson, and Andrew J. Beattie. "Biodiversity Resources for Restoration Ecology." Restoration Ecology 2, no. 4 (1994): 230–41. http://dx.doi.org/10.1111/j.1526-100x.1994.tb00055.x.

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3

Edwards, David P., and Gianluca R. Cerullo. "Biodiversity is central for restoration." Current Biology 34, no. 9 (2024): R371—R379. http://dx.doi.org/10.1016/j.cub.2024.02.032.

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Toma, Tiago S. P., Hernani F. M. Oliveira, Gerhard E. Overbeck, et al. "Aim for heterogeneous biodiversity restoration." Science 383, no. 6681 (2024): 376. http://dx.doi.org/10.1126/science.adn3767.

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5

Aerts, Raf, and Olivier Honnay. "Forest restoration, biodiversity and ecosystem functioning." BMC Ecology 11, no. 1 (2011): 29. http://dx.doi.org/10.1186/1472-6785-11-29.

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6

Jacob, Céline, Anaïs Buffard, Sylvain Pioch, and Sébastien Thorin. "Marine ecosystem restoration and biodiversity offset." Ecological Engineering 120 (September 2018): 585–94. http://dx.doi.org/10.1016/j.ecoleng.2017.09.007.

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7

Bullock, James M., Richard F. Pywell, Mike J. W. Burke, and Kevin J. Walker. "Restoration of biodiversity enhances agricultural production." Ecology Letters 4, no. 3 (2001): 185–89. http://dx.doi.org/10.1046/j.1461-0248.2001.00215.x.

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8

Eka Mahadewi, Ni Made. "Sustainable Restoration of Degraded Wetlands Focusing on Biodiversity and Hydrological Balance." FMDB Transactions on Sustainable Environmental Sciences 1, no. 3 (2024): 117–25. https://doi.org/10.69888/ftsess.2024.000298.

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The threat of wetland degradation to human activities because of biodiversity loss, disturbances in hydrological cycles, and loss of ecosystem services, including climate change, urbanization, and anthropogenic activities, calls for a more sustainable strategy for restoring degraded wetlands. This paper addresses the biodiversity and hydrological balance in such wetlands for their restoration. This study employs an ecological and hydrological methodology and an integrated socio-economic approach to develop the framework. Techniques include native vegetation restoration, invasive species manage

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9

Guiden, Peter W., Nicholas A. Barber, Ryan Blackburn, et al. "Effects of management outweigh effects of plant diversity on restored animal communities in tallgrass prairies." Proceedings of the National Academy of Sciences 118, no. 5 (2021): e2015421118. http://dx.doi.org/10.1073/pnas.2015421118.

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A primary goal of ecological restoration is to increase biodiversity in degraded ecosystems. However, the success of restoration ecology is often assessed by measuring the response of a single functional group or trophic level to restoration, without considering how restoration affects multitrophic interactions that shape biodiversity. An ecosystem-wide approach to restoration is therefore necessary to understand whether animal responses to restoration, such as changes in biodiversity, are facilitated by changes in plant communities (plant-driven effects) or disturbance and succession resultin

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Qin, Ziliu, Qiutong Chen, Xiang Ji, Shuang Ming, and Qin Du. "Biodiversity protection and ecological restoration of Guilin Karst quarry." E3S Web of Conferences 194 (2020): 04025. http://dx.doi.org/10.1051/e3sconf/202019404025.

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The abandoned quarry as a witness left by industrial history has greatly damaged the mining area and the surrounding ecological environment, causing severe disturbances on the surface, soil erosion and biodiversity decline. Therefore, the ecological restoration of abandoned quarries has become an important focus of ecological restoration. This article summarizes the current situation and distribution characteristics of Guilin karst quarry, and analyses the current problems of ecological restoration in karst quarry. Accordingly, it is proposed that the ecological restoration of the Guilin Karst

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11

Drury, Crawford, and Diego Lirman. "Making biodiversity work for coral reef restoration." Biodiversity 18, no. 1 (2017): 23–25. http://dx.doi.org/10.1080/14888386.2017.1318094.

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12

Zedler, Joy B. "European Wet Grasslands: Biodiversity, Management, and Restoration." Restoration Ecology 7, no. 4 (1999): 411–12. http://dx.doi.org/10.1046/j.1526-100x.1999.72037.x.

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13

Oleskog, Gunilla. "Wetland Restoration benefits both climate and biodiversity." Project Repository Journal 21, no. 1 (2024): 66–69. http://dx.doi.org/10.54050/prj2122380.

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Wetland Restoration benefits both climate and biodiversity In GRIP on LIFE IP, public authorities in Sweden work together with forest owners’ associations, non-governmental organisations and researchers to improve environmental consideration of waters and wetlands in the forest landscape while continuing active forest management. Our goal is to improve the environment and conditions for animals and plants living in the forest’s watercourses and wetlands.

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14

Klaphake, Axel. "The Assessment and Restoration of Biodiversity Damages." Journal for European Environmental & Planning Law 2, no. 4 (2005): 268–76. http://dx.doi.org/10.1163/187601005x00048.

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15

Brudvig, Lars A. "Toward prediction in the restoration of biodiversity." Journal of Applied Ecology 54, no. 4 (2017): 1013–17. http://dx.doi.org/10.1111/1365-2664.12940.

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16

WEBER, MARIAN, GRANT HAUER, and DAN FARR. "Economic-ecological evaluation of temporary biodiversity offsets in Alberta's boreal forest." Environmental Conservation 42, no. 4 (2015): 315–24. http://dx.doi.org/10.1017/s0376892915000181.

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SUMMARYTo conserve biodiversity on forest landscapes, it is necessary to understand how incentives in an offset market affect the dynamics of habitat loss and restoration. In this study, a model of firm behaviour in a temporary biodiversity offset market is developed to understand the impact of offset rules on the dynamics of land use and offset policy costs and benefits for Alberta's boreal forest. Policy treatments include eligibility rules for restoration versus avoided loss; time lags for crediting restoration benefits; and geographic trading restrictions. The analysis highlights the assum

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17

Chen, Jingru, Binsheng Wu, Kunli Dai, and Jiao Yu. "Linking Perceived Biodiversity and Restorative Benefits in Urban Parks through Place Attachment—A Case Study in Fuzhou, China." Diversity 16, no. 7 (2024): 416. http://dx.doi.org/10.3390/d16070416.

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Enhanced understanding of environmental restoration can be achieved by examining how urban park visitors’ perceptions of biodiversity contribute to their sense of environmental rejuvenation. In this study, a questionnaire survey was conducted among 554 visitors from five representative urban parks in Fuzhou, China, and a structural equation model was used to explore the interactions among perceived biodiversity, place attachment, and self-rated repair. The main findings were as follows: (1) Perceived biodiversity had significant positive and direct effects on place dependence and self-rated re

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18

Williams, Susan L., Rohani Ambo-Rappe, Christine Sur, Jessica M. Abbott, and Steven R. Limbong. "Species richness accelerates marine ecosystem restoration in the Coral Triangle." Proceedings of the National Academy of Sciences 114, no. 45 (2017): 11986–91. http://dx.doi.org/10.1073/pnas.1707962114.

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Ecosystem restoration aims to restore biodiversity and valuable functions that have been degraded or lost. The Coral Triangle is a hotspot for marine biodiversity held in its coral reefs, seagrass meadows, and mangrove forests, all of which are in global decline. These coastal ecosystems support valuable fisheries and endangered species, protect shorelines, and are significant carbon stores, functions that have been degraded by coastal development, destructive fishing practices, and climate change. Ecosystem restoration is required to mitigate these damages and losses, but its practice is in i

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19

Wang, James. "Ecological Restoration in New Zealand: Parks for Biodiversity." CITYGREEN 01, no. 03 (2011): 104. http://dx.doi.org/10.3850/s2382581211010489.

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20

Yan, Hui, and Guixiang Liu. "Fire’s Effects on Grassland Restoration and Biodiversity Conservation." Sustainability 13, no. 21 (2021): 12016. http://dx.doi.org/10.3390/su132112016.

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Ecosystem succession and biodiversity change associated with grassland fires are crucial for the patterns and dynamics of ecosystem functioning and services. The reactions to fire by different grassland types vary diversely, and are determined by certain species assemblages and environments. However, there are still uncertainties concerning the role of fire in affecting grassland ecosystems and how the effects are sustained. By conducting a bibliometric analysis of related articles indexed in the Web of Science between 1984 and 2020, we firstly described the general trend of these articles ove

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21

Ramchunder, Sorain J., Lee E. Brown, and Joseph Holden. "Catchment-scale peatland restoration benefits stream ecosystem biodiversity." Journal of Applied Ecology 49, no. 1 (2011): 182–91. http://dx.doi.org/10.1111/j.1365-2664.2011.02075.x.

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22

Sayer, Jeffrey, Unna Chokkalingam, and John Poulsen. "The restoration of forest biodiversity and ecological values." Forest Ecology and Management 201, no. 1 (2004): 3–11. http://dx.doi.org/10.1016/j.foreco.2004.06.008.

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23

Brans, Edward. "Climate Change Liability, Negative Emissions and Biodiversity Restoration." Journal for European Environmental & Planning Law 19, no. 4 (2022): 311–36. http://dx.doi.org/10.1163/18760104-19040003.

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Abstract This article is about climate liability and the stimulation of negative emissions through nature restoration. Such a measure can contribute to the reduction of greenhouse gas emissions, but can also lead to a restoration of biodiversity and of ecosystem services. In order to finance measures aimed at achieving natural negative emissions, the European Commission is considering introducing a system of carbon credits as part of the ‘Fit for 55’ program. This contribution investigates the advantages and disadvantages thereof and wonders about the nature and extent of the liability risks i

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24

Urbanska, Krystyna M. "Biodiversity assessment in ecological restoration above the timberline." Biodiversity and Conservation 4, no. 7 (1995): 679–95. http://dx.doi.org/10.1007/bf00158862.

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25

Wambugu, Peterson W., Desterio O. Nyamongo, and Everlyne C. Kirwa. "Role of Seed Banks in Supporting Ecosystem and Biodiversity Conservation and Restoration." Diversity 15, no. 8 (2023): 896. http://dx.doi.org/10.3390/d15080896.

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The world is witnessing massive land degradation caused by climate change and various anthropogenic activities. There has been a significant increase in habitat restoration efforts, with demand for seeds to restore these degraded ecosystems in some cases outstripping supply. Traditionally, seeds for restoration activities have mainly been sourced through collections from the wild, but with the growing seed demand, this is increasingly becoming unsustainable. In order to ensure responsible restoration practice, restoration practitioners need to explore other options of economical, ethical and s

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26

Hoek, Niels. "A Critical Analysis of the Proposed EU Regulation on Nature Restoration: Have the Problems Been Resolved?" European Energy and Environmental Law Review 31, Issue 5 (2022): 320–33. http://dx.doi.org/10.54648/eelr2022021.

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European biodiversity is on a steep decline, in part due to climate change, pollution, overexploitation and changes in land use. In light of this decline, the Habitats Directive, the cornerstone of EU nature conservation law, has been the subject of critique. It can be observed that the Directive suffers from lacklustre (binding) norms on nature restoration – from connectivity restoration to climate change adaptation. However, in June of 2022, the European Commission published a proposal for a Regulation on Nature Restoration, which supplements the existing regimes withinEUnature conservation

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27

Nuévalos-Tello, Carlos, Daniel Hernández-Torres, Santiago Sardinero-Roscales, Miriam Pajares-Guerra, Anna Chilton, and Raimundo Jiménez-Ballesta. "Ecological Restoration Process of El Hito Saline Lagoon: Potential Biodiversity Gain in an Agro-Natural Environment." Land 13, no. 12 (2024): 1992. http://dx.doi.org/10.3390/land13121992.

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In the global context of biodiversity and ecosystem services loss, the integration of agriculture with ecological restoration is crucial.. This study presents the biodiversity value (Bv) index for the first time as a tool for decision-making and securing funding for future restoration projects. The Bv index was used to assess biodiversity values in both restored natural habitats and agricultural areas in the saline lagoon of El Hito, a natural reserve located within an agricultural landscape in central Spain. Additionally, we estimated biodiversity gains from habitat transitions and explored t

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28

Siqueira, Marcos Vinicius Bohrer Monteiro, Patricia Sanae Sujii, Miklos Bajay, et al. "How can molecular ecology contribute to forest restoration?" Journal of Biotechnology and Biodiversity 4, no. 4 (2013): 316–21. http://dx.doi.org/10.20873/jbb.uft.cemaf.v4n4.siqueira.

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The advance of scientific knowledge in various areas of molecular ecology has allowed the adoption of new strategies, particularly in forest restoration. The fusion of multidisciplinary areas and the implementation of management methodologies in order to get better results in forest restoration are current realities. In order to review the main ideas about the role of molecular techniques in the service of ecology restoration, this paper outlines how forest recovery can benefit from genetic and genomic plant population studies. The next challenges in conservation genetics can be brought by the

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29

Mendiondo, EM. "Challenging issues of urban biodiversity related to ecohydrology." Brazilian Journal of Biology 68, no. 4 suppl (2008): 983–1002. http://dx.doi.org/10.1590/s1519-69842008000500007.

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This paper aims to outline challenging issues of urban biodiversity in order to address yardsticks related to ecohydrology, and with a complementary approach to eutrophication impacts. The vision of environmental services, urbanization's consequences and management aspects of water governance are also depicted. Factors of river restoration, environmental tradeoffs and socio-cultural constrains are envisaged through concept questions towards emerging aspects that figure out methodological guides, strategic challenges for stakeholders and inter-disciplinary opportunities. Examples from case stud

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30

Wilkes, Martin A., Morwenna Mckenzie, Marc Naura, et al. "Defining Recovery Potential in River Restoration: A Biological Data-Driven Approach." Water 13, no. 23 (2021): 3339. http://dx.doi.org/10.3390/w13233339.

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Scientists and practitioners working on river restoration have made progress on understanding the recovery potential of rivers from geomorphological and engineering perspectives. We now need to build on this work to gain a better understanding of the biological processes involved in river restoration. Environmental policy agendas are focusing on nature recovery, reigniting debates about the use of “natural” reference conditions as benchmarks for ecosystem restoration. We argue that the search for natural or semi-natural analogues to guide restoration planning is inappropriate due to the absenc

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31

Keith, Kayla M., Matthew K. Potvin, Summer R. Saad, and Thilina D. Surasinghe. "Temporal Shifts in Biological Community Structure in Response to Wetland Restoration: Implications for Wetland Biodiversity Conservation and Management." Diversity 17, no. 3 (2025): 198. https://doi.org/10.3390/d17030198.

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Wetlands are vital ecosystems that provide diverse ecosystem services. However, their degradation poses an environmental threat globally, impacting human society. Recognizing their economic importance amidst escalating degradation emphasizes the urgent need for wetland conservation. Wetland restoration emerges as a crucial strategy to recover lost acreage and ecosystem functions. Despite substantial investments in restoration, the success of these efforts remains uncertain. We addressed this gap by investigating temporal changes in biological communities in restored wetlands to assess restorat

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32

Long, Fayu, Guanghui Zhou, Lei Zu, et al. "Multi-Trophic Species Diversity Contributes to the Restoration of Soil Multifunctionality in Degraded Karst Forests through Cascading Effects." Forests 15, no. 3 (2024): 559. http://dx.doi.org/10.3390/f15030559.

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The biodiversity–ecosystem function (BEF) relationship is the basis for studying the restoration of degraded ecosystems, and the simultaneous assessment of multi-trophic-level biodiversity and ecosystem multifunctionality relationship is more conducive to unravelling the restoration mechanism of degraded ecosystems, especially for degraded forest ecosystems with harsh habitats and infertile soils such as karst. In this study, we evaluated the biodiversity and soil multifunctionality (SMF) of degraded karst forests (scrub, SB; secondary growth forests, SG; old-growth forests, OG) in the Maolan

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33

Richards, Daniel, Thomas R. Etherington, Alexander Herzig, and Sandra Lavorel. "The Importance of Spatial Configuration When Restoring Intensive Production Landscapes for Biodiversity and Ecosystem Service Multifunctionality." Land 13, no. 4 (2024): 460. http://dx.doi.org/10.3390/land13040460.

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Intensive production landscapes provide low levels of many ecosystem services and support limited biodiversity, so they require restoration to enhance their multifunctionality. International guidelines suggest that restoration should aim to establish natural woody vegetation cover across 30% of landscapes. Such restoration may be implemented in varied spatial configurations and complemented by additional land use changes from intensive to extensive semi-natural pastoral grasslands. To restore multifunctional landscapes, we need to understand the impacts of restoration spatial configuration and

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34

Carbutt, Clinton, and Kevin Kirkman. "Ecological Grassland Restoration—A South African Perspective." Land 11, no. 4 (2022): 575. http://dx.doi.org/10.3390/land11040575.

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The principal drivers of Grassland Biome conversion and degradation in South Africa include agricultural intensification, plantation forestry, urban expansion and mining, together with invasive non-native plants and insidious rural sprawl. This biome is poorly conserved and in dire need of restoration, an ecologically centred practice gaining increasing traction given its wide application to people and biodiversity in this emerging culture of renewal. The pioneering proponent of restoration in South Africa is the mining industry, primarily to restore surface stability using vegetation cover. W

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35

Rong, Zhenzhen. "Using Environmental Litigation to Advance Ecological Restoration under the Convention on Biological Diversity in China." Chinese Journal of Environmental Law 7, no. 1 (2023): 100–130. http://dx.doi.org/10.1163/24686042-12340099.

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Abstract In response to unprecedented global biodiversity loss, the obligation of restoration has been integrated into the Convention on Biological Diversity (CBD, or Convention). As a Party to the CBD, China has implemented restoration commitments through the ‘National Biodiversity Strategy and Action Plan (2011–2030)’. This article focuses on how such commitments have been translated into the Chinese legal framework and environmental litigation, and how environmental litigation can advance ecological restoration. There exist restoration obligations of governments and individuals. When they f

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36

Chou, Loke Ming. "Enhancing Marine Biodiversity in Singapore’s Urbanizing Coastal Environment." International Journal of Environmental Science and Development 11, no. 11 (2020): 519–23. http://dx.doi.org/10.18178/ijesd.2020.11.11.1301.

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Urbanization of coastal cities has resulted in extensive physical modification of the coast that is commonly accompanied by habitat destruction or degradation, marine biodiversity loss and ecosystem services decline. Conversion of the natural environment to a human-modified one is often permanent, and it is important that development considerations take into account biodiversity enhancement of the ‘new’ environment. Development of biological communities in the modified environment takes time and is unlikely to return to levels once supported by the original habitats, but efforts can be made to

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37

Dixon, Kingsley W. "Pollination and Restoration." Science 325, no. 5940 (2009): 571–73. http://dx.doi.org/10.1126/science.1176295.

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Pollination services underpin sustainability of restored ecosystems. Yet, outside of agri-environments, effective restoration of pollinator services in ecological restoration has received little attention. This deficiency in the knowledge needed to restore pollinator capability represents a major liability in restoration programs, particularly in regions where specialist invertebrate and vertebrate pollinators exist, such as global biodiversity hotspots. When compounded with the likely negative impacts of climate change on pollination services, the need to understand and manage pollinator serv

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38

Montgomery, Ian, Tancredi Caruso, and Neil Reid. "Hedgerows as Ecosystems: Service Delivery, Management, and Restoration." Annual Review of Ecology, Evolution, and Systematics 51, no. 1 (2020): 81–102. http://dx.doi.org/10.1146/annurev-ecolsys-012120-100346.

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Hedge density, structure, and function vary with primary production and slope gradient and are subject to other diverse factors. Hedgerows are emerging ecosystems with both above- and belowground components. Functions of hedges can be categorized as provisioning, regulating, cultural, and supporting ecosystem services; these functions include food production, noncrop food and wood production, firewood production, pollination, pest control, soil conservation and quality improvement, mitigation of water flux and availability, carbon sequestration, landscape connectivity and character maintenance

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39

Cariveau, Daniel P., Bethanne Bruninga-Socolar, and Gabriella L. Pardee. "A review of the challenges and opportunities for restoring animal-mediated pollination of native plants." Emerging Topics in Life Sciences 4, no. 1 (2020): 99–109. http://dx.doi.org/10.1042/etls20190073.

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Ecological restoration is increasingly implemented to reverse habitat loss and concomitant declines in biological diversity. Typically, restoration success is evaluated by measuring the abundance and/or diversity of a single taxon. However, for a restoration to be successful and persistent, critical ecosystem functions such as animal-mediated pollination must be maintained. In this review, we focus on three aspects of pollination within ecological restorations. First, we address the need to measure pollination directly in restored habitats. Proxies such as pollinator abundance and richness do

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40

Brancalion, Pedro H. S., Felipe P. L. Melo, Marcelo Tabarelli, and Ricardo R. Rodrigues. "Restoration Reserves as Biodiversity Safeguards in Human-Modified Landscapes." Natureza & Conservação 11, no. 2 (2013): 186–90. http://dx.doi.org/10.4322/natcon.2013.029.

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41

Symstad, A. J. "Does Biodiversity-Ecosystem Function Science Apply to Prairie Restoration?" Ecological Restoration 26, no. 2 (2008): 100–102. http://dx.doi.org/10.3368/er.26.2.100.

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42

Romanelli, João Paulo, Paula Meli, João Paulo Bispo Santos, et al. "Biodiversity responses to restoration across the Brazilian Atlantic Forest." Science of The Total Environment 821 (May 2022): 153403. http://dx.doi.org/10.1016/j.scitotenv.2022.153403.

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43

Norton, David A., Jason Butt, and David O. Bergin. "Upscaling restoration of native biodiversity: A New Zealand perspective." Ecological Management & Restoration 19 (June 15, 2018): 26–35. http://dx.doi.org/10.1111/emr.12316.

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Lehosmaa, Kaisa, Jussi Jyväsjärvi, Risto Virtanen, et al. "Does habitat restoration enhance spring biodiversity and ecosystem functions?" Hydrobiologia 793, no. 1 (2016): 161–73. http://dx.doi.org/10.1007/s10750-016-2760-4.

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45

Bullock, James M., James Aronson, Adrian C. Newton, Richard F. Pywell, and Jose M. Rey-Benayas. "Restoration of ecosystem services and biodiversity: conflicts and opportunities." Trends in Ecology & Evolution 26, no. 10 (2011): 541–49. http://dx.doi.org/10.1016/j.tree.2011.06.011.

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46

Klaus, Valentin H. "Urban Grassland Restoration: A Neglected Opportunity for Biodiversity Conservation." Restoration Ecology 21, no. 6 (2013): 665–69. http://dx.doi.org/10.1111/rec.12051.

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47

Lesage, Josephine C., Elizabeth A. Howard, and Karen D. Holl. "Homogenizing biodiversity in restoration: the “perennialization” of California prairies." Restoration Ecology 26, no. 6 (2018): 1061–65. http://dx.doi.org/10.1111/rec.12887.

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48

Stier, Sam C., and Stephen F. Siebert. "The Kyoto Protocol: an Opportunity for Biodiversity Restoration Forestry." Conservation Biology 16, no. 3 (2002): 575–76. http://dx.doi.org/10.1046/j.1523-1739.2002.01626.x.

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49

Nerlekar, Ashish N., Lauren L. Sullivan, and Lars A. Brudvig. "Grassland restorations must better foster forbs to facilitate high biodiversity." Restoration Ecology, June 18, 2024. http://dx.doi.org/10.1111/rec.14214.

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Grassland restoration efforts typically aim to recover lost biodiversity, guided by biologically diverse old‐growth grasslands as a benchmark. In most old‐growth grasslands, forbs greatly outnumber grasses in terms of richness and therefore contribute most to diversity, but globally, restoration practitioners continue to disproportionately focus on increasing perennial grass cover. While such grass‐centric restoration approaches might be appropriate for meeting some restoration goals, an increasing number of studies reveal negative effects of perennial grass cover on forb and total plant diver

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Kigonya, Ritah, Patrick Byakagaba, Edward Ssenyonjo, and Charlotte Nakakaawa Jjunju. "“Biodiversity Offsetting” in Uganda’s Protected Areas: A Pathway to Restoration of Forest Biodiversity?" Environmental Management, May 10, 2024. http://dx.doi.org/10.1007/s00267-024-01982-6.

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AbstractWith limited national financing for conservation, there is an increasing interest in using biodiversity offset funds to strengthen protected area management. Offsetting measures can potentially be used in the restoration of degraded protected areas. However, there are concerns related to the uncertainty of restoration outcomes and time-lags before the expected benefits can be observed. Using a case of the Gangu Central Forest Reserve in central Uganda, we contribute empirical findings showing the potential and limitations of biodiversity offsetting by means of the restoration of a degr

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