Thematische Bibliographien / Restoration ecology

Inhaltsverzeichnis

  1. Zeitschriftenartikel
  2. Dissertationen
  3. Bücher
  4. Buchteile
  5. Konferenzberichte
  6. Berichte der Organisationen

Auswahl der wissenschaftlichen Literatur zum Thema „Restoration ecology“

Autor: Grafiati
Veröffentlicht am 4. Juni 2021
Zuletzt aktualisiert am 30. Juli 2024

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Zeitschriftenartikel zum Thema "Restoration ecology"

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Clewell, Andre F. „Ecology, Restoration Ecology, and Ecological Restoration“. Restoration Ecology 1, Nr. 3 (07.04.2006): 141. http://dx.doi.org/10.1111/j.1526-100x.1993.tb00020.x.

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Baker, A. J. M., W. R. Jordan, M. E. Gilpin und J. D. Aber. „Restoration Ecology.“ Journal of Ecology 79, Nr. 2 (Juni 1991): 562. http://dx.doi.org/10.2307/2260739.

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Alcoze, T. A. „Restoration Ecology“. Science 287, Nr. 5461 (24.03.2000): 2159b—2159. http://dx.doi.org/10.1126/science.287.5461.2159b.

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Reid, J. Leighton. „Restoration Ecology's Silver Jubilee: big time questions for restoration ecology“. Restoration Ecology 26, Nr. 6 (24.09.2018): 1029–31. http://dx.doi.org/10.1111/rec.12883.

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Jordan, William R. „Restoration Ecology Symposium“. Ecological Restoration 3, Nr. 1 (1985): 12–13. http://dx.doi.org/10.3368/er.3.1.12.

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Lithgow, D., M. L. Martínez, J. B. Gallego-Fernández, P. A. Hesp, P. Flores, S. Gachuz, N. Rodríguez-Revelo, O. Jiménez-Orocio, G. Mendoza-González und L. L. Álvarez-Molina. „Linking restoration ecology with coastal dune restoration“. Geomorphology 199 (Oktober 2013): 214–24. http://dx.doi.org/10.1016/j.geomorph.2013.05.007.

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Siqueira, Marcos Vinicius Bohrer Monteiro, Patricia Sanae Sujii, Miklos Bajay, Carolina Grando, Kaiser Schwarcz, Camila Macrini und Maria Imaculada Zucchi. „How can molecular ecology contribute to forest restoration?“ Journal of Biotechnology and Biodiversity 4, Nr. 4 (01.11.2013): 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 quest for more efficient forest restorations from the point of view of biodiversity as well as the ecological ynamics as a whole. It is believed that in the coming years we will observe integrated strategies in molecular ecology with specific methodologies for restoration in tropical forests.
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Liu, Chang, Jingyi Ouyang, Jinshan Yan und Lina Tang. „Landsenses Ecology: A New Idea for Watershed Ecology Restoration“. International Journal of Environmental Research and Public Health 20, Nr. 4 (17.02.2023): 3610. http://dx.doi.org/10.3390/ijerph20043610.

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Watershed ecology restoration is the key to solving the ecological and environmental problems of watersheds and achieving sustainable development. As one direction of the frontiers of ecology, landsenses ecology is supported by science and technology and cares for humans. It has a great significance for enhancing the human habitat and achieving sustainable development. Combining landsenses ecology and the technical process of watershed ecology restoration allows the integration of people’s visions into the system of strategies and applied technologies for watershed ecology restoration while ensuring the restoration of the ecological functions of watersheds. It is a complement to the traditional ecosystem restoration model. This study establishes the connection between landsenses ecology and watershed ecology restoration in terms of goals, models and focus of attention. It aims to construct an indicator system of restoration with the application of landsenses ecology, form a complete process of ecological restoration with the integration of landsenses ecology and apply it to the ecological restoration of watershed elements with relatively intensive human activity such as urban green areas, buildings and wetlands (rivers and lakes). Rather than just always emphasizing natural ecology, landsenses ecology treats human beings as part of nature. It tries to establish a more comprehensive, humanized ideal restoration model by taking “human perceptions” into consideration. Through a restoration process based on long-term and continuous coordination, feedback and improvement, it can improve the ecological benefits of the watershed and improve residents’ well-being, so as to ultimately realize the establishment of a “community of life between man and nature”.
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Anderson, P., K. M. Urbanska und K. Grodzinska. „Restoration Ecology in Europe.“ Journal of Applied Ecology 33, Nr. 1 (Februar 1996): 184. http://dx.doi.org/10.2307/2405036.

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Young, T. P. „Introduction to Restoration Ecology“. Ecological Restoration 30, Nr. 3 (30.07.2012): 246. http://dx.doi.org/10.3368/er.30.3.246.

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Dissertationen zum Thema "Restoration ecology"

1

Miller, John Anthony. „Monitoring of Sphagnum at a Restoration Site and Possibilities for Restorative Activities“. University of Akron / OhioLINK, 2016. http://rave.ohiolink.edu/etdc/view?acc_num=akron1466790016.

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Lawrence, James Mark. „Restoration ecology of the Seychelles giant millipede“. Thesis, Stellenbosch : Stellenbosch University, 2013. http://hdl.handle.net/10019.1/85596.

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Thesis (PhD)--Stellenbosch University, 2013.
ENGLISH ABSTRACT: The loss and degradation of habitat is recognised as the greatest threat to invertebrate biodiversity. Restoration practices have the potential to reduce these impacts. The Seychelles giant millipede (SGM), Sechelleptus seychellarum, is a threatened and functionally important macro-detritivore endemic to the Seychelles granitic islands. The broad objective of this dissertation was to investigate selected aspects of the restoration ecology of the SGM, with the intention of making practical restoration recommendations that can be used to assist in the conservation of this species. This study was carried out on Cousine Island, Seychelles between 1998 and 2009, in the context of the large-scale plant community restoration that has taken place on the island. Large fluctuations in millipede population densities were found between 1998 and 2009. In 2002, 2003, 2005 and 2007 millipede densities were low, while densities were high in 1998 and 2009. Although the SGM is active all year round, its surface activity was positively correlated with rainfall, with density high during the high rainfall period (i.e. October – April) and low during the low rainfall period (i.e. May – September). Female:male:juvenile ratios were ~ 3:1:1. The implications are that translocations should preferably be done in years of high millipede densities and during the wet season. Alien coconut trees did not affect SGM density, but negatively affected its foraging behaviour, whereas bamboo stands negatively affected both its density and foraging behaviour. The SGM showed feeding preferences for Pisonia grandis and Ficus sp. leaf litter types. Alien bamboo and coconut pose a varied threat to the SGM, and their removal and replacement by indigenous forest species (e.g. P. grandis and Ficus sp.) should form part of an island’s restoration programme. SGM density was an order of magnitude lower in the restored area compared to the natural forest. In contrast, SGM physical condition improved significantly in the restored area, as vegetation structure increased. Furthermore, SGM behaviour in the restored area switched from a predominantly walking to a predominantly feeding behaviour over the study period, resulting in the forest restoration programme on Cousine increasing the foraging area of the SGM by 43%. SGM spatial density did not significantly correlate with edaphic and litter properties, but did positively correlate with the toposcape (i.e. elevation and granitic rock cover). Granite rock crevices in forest covered areas were important diurnal refuges for the SGM, as microclimate conditions in non-forest covered rock refuges were unsuitable. SGM physical condition was significantly lower in non-shaded crevices compared to those shaded by forest. Low granite rock cover in the restored forest limited the SGM colonisation of this area in large numbers, despite canopy cover in the restored forest being comparable with that in the reference natural forest. As most restoration practices are primarily vegetation-based, this study demonstrates that such an approach can be inadequate for restoring habitat for target invertebrates, as many species’ habitat requirements extend beyond that of vegetation. For the SGM, selecting restoration sites that already have abundant rock cover would be the most practical way to increase SGM habitat through forest restoration practices. Taking into consideration the habitat requirements of target invertebrates can help in setting or redirecting restoration goals and thus enhance the conservation value of such practices.
AFRIKAANSE OPSOMMING: Die verlies en agteruitgang van habitat word alom beskou as die grootste bedreiging var die biodiversiteit van ongewerweldes. Herstellingspraktyke kan hierdie agteruitgang verminder of stop. Die Seychelle Reuse Duisendpoot (SGM), Sechelleptus seychellarum, is 'n bedreigde en funksioneel belangrike makro-detritusvoeder wat endemies is aan die Seychelle graniet-eilande. Die breë doelstelling van hierdie verhandeling is die doen van navorsing om praktiese aanbevelings te kan maak om die habitat van die SGM tot so ‘n mate te herstel dat die spesie kan bly voortbestaan. Hierdie studie is tussen 1998 en 2009 uitgevoer op Cousine Island, Seychelles, nadat ‘n grootskaalse herstellingsfase van die plantgemeenskap plaasgevind het. Groot skommelings in duisendpootgetalle is waargeneem tussen 1998 en 2009, viz. duisendpootgetalle was laag in 2002, 2003, 2005 en 2007, terwyl dit hoog was in 1998 en 2009. Alhoewel die SGM gedurende die hele jaar aktief is, is hulle tog in groter getalle aanwesig in die tydperke met hoë reënval (Oktober-April) en laag in die droë tydperk (Mei-September). Die verhouding van wyfies, mannetjies en onvolwassenes was deurgaans ~ 3:1:1. Dit bring mee dat hervestiging van SGM verkieslik gedoen moet word wanneer hul populasies hoog is en dan ook in die nat seisoen. Uitheemse klapperbome het geen invloed op SGM getalle gehad nie, alhoewel hul voedingsgedrag negatief beïnvloed is deur dié bome. Bamboesbosse darenteen, beïnvloed beide populasiedigtheid en voedingsgedrag van SGM negatief. Verder is daar gevind dat Pisonia grandis en Ficus sp. blaardetritus voorkeurvoedsel vir SGM is. Die verwydering van die uitheemse bamboes en klapperbome en vervanging daarvan met inheemse woudspesies (P. grandis en Ficus sp.) moet dus deel vorm van die eiland se herstelprogram om sodoende die SGM te bevoordeel. Die SGM-bevolkingsdigtheid was 'n grootte-orde laer in die herstelde gebied in vergelyking met die natuurlike bos, maar hul fisiese toestand het aansienlik verbeter in die herstelde gebied, waarskynlik omdat die plantegroei as geheel verbeter het. Verder het die SGM se gedrag gedurende die studietydperk in die herstelde area oorgegaan vanaf ‘n oorwegend loopgedrag om na kos te soek, na ‘n oorwegend voedende gedrag. Die vervanging van uitheemse- met inheemse boomspesies op Cousine Island het dus die voedingsarea van SGM met tot 43% verhoog. Die ruimtelike SGM populasiedigtheid is nie beduidend beïnvloed deur blaardetritus nie, maar is wel positief beïnvloed deur die topografie (hoogte en granietbedekking). Bebosde graniet rotsskeure bied belangrike toevlugsoorde vir SGM gedurende die dag, terwyl die mikroklimaat wat deur onbebosde rotsskeure veroorsaak word, totaal ongeskik is vir SGM. Die fisiese toestand van SGM was ook aansienlik swakker in die nie bebosde rotsskeure teenoor dié van die bebosde areas. In herstelde bos met min granietskuiling was die herkolonisering van SGM ook getalsgewys laer alhoewel die bosbedekking vergelykbaar was met dié van die inheemse bos. Dit bewys dus dat herstellingspraktyke wat hoofsaaklik plantegroei teiken, nie altyd die teikenspesie bevoordeel nie, maar dat ‘n meer holistiese benadering wat alle habitatvoorkeure in ag neem, toegepas moet word. Om SGM te bevoordeel moet herstel areas vir herbebossing dus gekies word waar daar reeds genoegsame granietskuiling is. Deur die habitatvereistes van ongewerwelde teikenspesies in ag te neem kan die herstellingspraktyke meer oordeelkundig ingestel word en sodoende kan die bewaringswaarde van sulke praktyke verbeter word.
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Zaloumis, Nicholas Paul. „South African grassland ecology and its restoration“. Master's thesis, University of Cape Town, 2013. http://hdl.handle.net/11427/6629.

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The aim of this study is to investigate how human related disturbances affect mesic grasslands. I identified what was lost from the system after a disturbance and what biological constraints ecologists and managers will face when approaching their restoration. I then investigated biological limitations to grassland restoration by attempting species reintroduction into secondary grasslands and exploring the interaction between grasses and forbs.
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Spencer, Jessica. „An Internship in Restoration Ecology at The Wilds“. Miami University / OhioLINK, 2012. http://rave.ohiolink.edu/etdc/view?acc_num=miami1354757034.

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Forup, Mikael Lytzau. „The restoration of plant pollinator interactions“. Thesis, University of Bristol, 2003. http://hdl.handle.net/1983/f77be7e4-2baa-4d8e-8ffb-e261541923c5.

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Magnusson, Gisele Marie. „Economic-ecological relationships in coastal wetland restoration /“. View online ; access limited to URI, 2006. http://0-wwwlib.umi.com.helin.uri.edu/dissertations/dlnow/3225321.

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Vranizan, Gregory Matthew. „Rhetoric and the restoration landscape forest restoration in environmental debate /“. CONNECT TO THIS TITLE ONLINE, 2006. http://etd.lib.umt.edu/theses/available/etd-03022007-101332/.

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Briggs, Mark Kendig. „An evaluation of riparian revegetation efforts in Arizona“. Ann Arbor, Mich. : UMI, 1992.

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Rowland, Jennifer M. „Restoration ecology of Cirsium pitcheri along Lake Huron sand dunes“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1999. http://www.collectionscanada.ca/obj/s4/f2/dsk2/ftp01/MQ42096.pdf.

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Watrous, Kristal M. „Reproductive Ecology of Astragalus filipes, a Great Basin Restoration Legume“. DigitalCommons@USU, 2010. https://digitalcommons.usu.edu/etd/617.

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Astragalus filipes Torrey ex. A. Gray (Fabaceae) is being studied and propagated for use in rangeland restoration projects throughout the Great Basin. Restoration forbs often require sufficient pollination services for seed production and persistence in restoration sites. Knowledge of a plant's breeding biology is important in providing pollination for maximal seed set. Reproductive output from four manual pollination treatments (autogamy, geitonogamy, xenogamy, and distant xenogamy) was examined in a common garden. Pod set, seed set, and seed germination were quantified for each of the treatments. Seed set from four wild populations was compared to that of an openly visited common garden array. A. filipes was found to be self-compatible, but to benefit greatly from outcrossing. Less seed germinated from distantly outcrossed treatments than for any other treatment, indicating possible outbreeding depression. Common garden plants set less seed per pod than any wild population, possibly due to a depauperate pollinator guild in the common garden. Bees were surveyed at wild A. filipes populations to identify common pollinators. Solitary and social bee species were observed visiting A. filipes to estimate aspects of their pollination efficacies, particularly foraging tempo and frequency of stigmatic contact. The nesting biologies of bees that visit A. filipes were considered as a component of bee manageability. Bees in the genus Osmia (Megachilidae) dominated this pollinator guild. Bombus nevadensis queens were the fastest foragers; honey bees and native solitary bees did not differ in foraging tempo. Megachilid bees consistently contacted the stigma during foraging, but honey bees exhibited sideworking behavior, contacting stigmas far less frequently than any other bee species observed. Two solitary bee species (Osmia bruneri and Hoplitis hypocrita) are recommended as prospective pollinators for management in association with Great Basin rehabilitation efforts.
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Bücher zum Thema "Restoration ecology"

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van Andel, Jelte, und James Aronson, Hrsg. Restoration Ecology. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.

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Schröder, Hans G. Grasslands: Ecology, management & restoration. New York: Nova Science Publishers, 2008.

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Palmer, Margaret A., Joy B. Zedler und Donald A. Falk, Hrsg. Foundations of Restoration Ecology. Washington, DC: Island Press/Center for Resource Economics, 2016. http://dx.doi.org/10.5822/978-1-61091-698-1.

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A, Falk Donald, Palmer Margaret A und Zedler Joy B, Hrsg. Foundations of restoration ecology. Washington, DC: Island Press, 2006.

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A, Harrington John, und Glass Stephen B. 1946-, Hrsg. Introduction to restoration ecology. Island Press: Washington, DC, 2011.

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K, Olvera Thomas, Hrsg. Ecological restoration. Hauppauge, NY: Nova Science Publishers, 2009.

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Andel, J. van. Restoration ecology: The new frontier. 2. Aufl. Hoboken, NJ: Wiley, 2012.

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E, Russo Raymundo, Hrsg. Wetlands: Ecology, conservation, and restoration. New York: Nova Science Publishers, 2008.

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R, Herrera Jose, Hrsg. International wetlands: Ecology, conservation, and restoration. New York: Nova Science Publishers, 2008.

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Mulder, Christa P. H. Seabird islands: Ecology, invasion, and restoration. Oxford: Oxford University Press, 2011.

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Buchteile zum Thema "Restoration ecology"

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Weber, Louise M. „Restoration ecology“. In Understanding Nature, 301–7. Boca Raton: CRC Press, 2023. http://dx.doi.org/10.1201/9781003271833-29.

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van Diggelen, Rudy, Richard J. Hobbs und Ladislav Miko. „Landscape Ecology“. In Restoration Ecology, 45–58. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch5.

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Sabogal, Ana. „Ecological Restoration“. In Urban Ecology, 143–58. Cham: Springer International Publishing, 2021. http://dx.doi.org/10.1007/978-3-030-69905-5_8.

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van Andel, Jelte, und James Aronson. „Getting Started“. In Restoration Ecology, 3–8. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch1.

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Bainbridge, David A. „Restoration of Arid and Semi-Arid Lands“. In Restoration Ecology, 115–29. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch10.

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Vallejo, V. Ramón, Edith B. Allen, James Aronson, Juli G. Pausas, Jordi Cortina und Julio R. Gutierrez. „Restoration of Mediterranean-Type Woodlands and Shrublands“. In Restoration Ecology, 130–44. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch11.

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Fischer, Anton, und Holger Fischer. „Restoration of Temperate Forests: An European Approach“. In Restoration Ecology, 145–60. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch12.

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Apostol, Dean, und Ayn Shlisky. „Restoring Temperate Forests: A North American Perspective“. In Restoration Ecology, 161–72. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch13.

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Bakker, Jan P., Rudy Van Diggelen, Renée M. Bekker und Rob H. Marrs. „Restoration of Dry Grasslands and Heathlands“. In Restoration Ecology, 173–88. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch14.

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Krautzer, Bernhard, Christian Uhlig und Helmut Wittmann. „Restoration of Arctic-Alpine Ecosystems“. In Restoration Ecology, 189–202. Chichester, UK: John Wiley & Sons, Ltd, 2012. http://dx.doi.org/10.1002/9781118223130.ch15.

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Konferenzberichte zum Thema "Restoration ecology"

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„River management, ecology, and restoration“. In The International Conference On Fluvial Hydraulics (River Flow 2016). Taylor & Francis Group, 6000 Broken Sound Parkway NW, Suite 300, Boca Raton, FL 33487-2742: CRC Press, 2016. http://dx.doi.org/10.1201/9781315644479-311.

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Meier, Claudio I. „The Ecological Basis of River Restoration: 1. River Ecology for Hydraulic Engineers“. In Wetlands Engineering and River Restoration Conference 1998. Reston, VA: American Society of Civil Engineers, 1998. http://dx.doi.org/10.1061/40382(1998)69.

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An, Na, Wei Zeng und Binman Yang. „Research on geo-ecological restoration of mountain towns upon the influence of earthquake disaster. A case study of 4.20 Lushan Earthquake“. In Post-Oil City Planning for Urban Green Deals Virtual Congress. ISOCARP, 2020. http://dx.doi.org/10.47472/lzak8080.

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Earthquakes have a great destructive effect on the geo-ecological environment of mountain towns, and the restoration of the geo-ecological environment after the disaster is of great significance to the sustainable development of mountain towns. This paper applies the improved ecological footprint method to build a geo-ecological restoration footprint evaluation model from the aspects of factors affecting the geological ecology. Moreover, Comprehensive evaluation of geo-ecology were selected to analyse the dynamic change process of geological ecology before and after the Lushan earthquake in 2010-2017. The results show that earthquake disasters have a long-term and dual impact on the geo-ecological environment of mountainous towns. Earthquake disasters can change the geo-ecological footprint by reducing the output of ecological products, changing the population composition, diet structure and even the fuel ratio, thereby affecting the geo-ecological restoration process for a long time. On the one hand, the effect of sustainable restoration of the ecology after the disaster in Lushan County has achieved initial results, the geo-ecological deficit has been reduced by more than 43%. But on the other hand, the comprehensive evaluation of ecological restoration in Lushan County is in an unsustainable state and the geo-ecological environment is facing tremendous pressure. Based on this, this article considers the degree of geoecological restoration in Lushan County, and proposes a countermeasure for future geological and ecological restoration in Lushan County.
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Bergmann, J. „Using Functional Ecology to Predict Restoration Successin Managed Grasslands“. In XXV International Grassland Congress. Berea, KY 40403: International Grassland Congress 2023, 2023. http://dx.doi.org/10.52202/071171-0012.

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Harger, Bruce W. W. „Kelp Bed Restoration Techniques: Insights into Kelp Biology and Ecology“. In California and the World Ocean 2002. Reston, VA: American Society of Civil Engineers, 2005. http://dx.doi.org/10.1061/40761(175)102.

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Nucci, M. E., R. Angelini, A. Cirelli, G. Marcantonio und P. M. Pedroni. „Optimizing Effectiveness of Restoration Practices Using Principles of Applied Ecology“. In SPE International Conference on Health, Safety, and Environment. Society of Petroleum Engineers, 2014. http://dx.doi.org/10.2118/168367-ms.

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G.E., Slyusarev. „RESTORATION OF THE STURGEON POPULATION“. In II INTERNATIONAL SCIENTIFIC AND PRACTICAL CONFERENCE "DEVELOPMENT AND MODERN PROBLEMS OF AQUACULTURE" ("AQUACULTURE 2022" CONFERENCE). DSTU-Print, 2022. http://dx.doi.org/10.23947/aquaculture.2022.127-128.

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In the conditions of sanctions, the provision of fish farming products to the population is of great importance. Due to intensive hydraulic engineering, poaching and a decrease in the quality of the environment, the population has declined sharply. To date, the catches of sturgeon are not able to ensure the volume of natural reproduction of these valuable species. At the moment, the population of the sturgeon is replenished exclusively by artificial means. Consideration of ways to eliminate this problem is the most significant topic in the ecology of aquatic ecosystems.
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Roshchin, M. N. „Restoration of shrouds of turbine blades“. In INTERNATIONAL SCIENTIFIC AND PRACTICAL CONFERENCE “ENERGY, ECOLOGY AND TECHNOLOGY IN AGRICULTURE” (EEA2022). AIP Publishing, 2022. http://dx.doi.org/10.1063/5.0128394.

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Kosican, Miroslav. „METHODOLOGY MAINTENANCE AND RESTORATION OF HISTORIC STRUCTURES AND ELEMENTS“. In 14th SGEM GeoConference on ECOLOGY, ECONOMICS, EDUCATION AND LEGISLATION. Stef92 Technology, 2014. http://dx.doi.org/10.5593/sgem2014/b53/s23.109.

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Uzakov, Zafar, Xusniddin Karimov und Zair Uzakov. „Restoration of contaminated soils by agricultural crops“. In III INTERNATIONAL CONFERENCE “SUSTAINABLE DEVELOPMENT: AGRICULTURE, ENERGY AND ECOLOGY” (VMAEE-III 2024). AIP Publishing, 2024. http://dx.doi.org/10.1063/5.0211975.

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Berichte der Organisationen zum Thema "Restoration ecology"

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Shepperd, Wayne D., Paul C. Rogers, David Burton und Dale L. Bartos. Ecology, biodiversity, management, and restoration of aspen in the Sierra Nevada. Ft. Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, 2006. http://dx.doi.org/10.2737/rmrs-gtr-178.

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Burke, Marianne K., und Philip Sheridan. Atlantic white cedar: ecology, restoration, and management: Proceedings of the Arlington Echo symposium. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station, 2005. http://dx.doi.org/10.2737/srs-gtr-91.

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3

Burke, Marianne K., und Philip Sheridan. Atlantic white cedar: ecology, restoration, and management: Proceedings of the Arlington Echo symposium. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southern Research Station, 2005. http://dx.doi.org/10.2737/srs-gtr-91.

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Chambers, Jeanne C., und Jerry R. Miller. Geomorphology, hydrology, and ecology of Great Basin meadow complexes - implications for management and restoration. Ft. Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, 2011. http://dx.doi.org/10.2737/rmrs-gtr-258.

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5

Schad, Aaron, Daniel Allen, Lynde Dodd, Ricardo Luna, Jacob Kelly, Kristina Hellinghausen, Nathan Harms, Gary Dick und Yaretzy Charo. Aquatic ecosystem restoration in the Texas Western Gulf Coast Plain / Lower Rio Grande alluvial floodplain ecoregion : Resaca Boulevard Resaca Section 206—vegetation community adaptive management. Engineer Research and Development Center (U.S.), September 2023. http://dx.doi.org/10.21079/11681/47559.

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As part of the US Army Corps of Engineers (USACE) Continuing Authorities Program (CAP), Section 206 projects focus on restoring aquatic habitats for the benefit of fish and other wildlife. From 2017–2021, USACE Engineer Research and Development Center–Environmental Laboratory researchers in the Aquatic Ecology and Invasive Species Branch (ERDC-EL EEA) at the Lewisville Aquatic Ecosystem Research Facility (LAERF) collaborated with USACE Galveston District, The Nature Conservancy, US Fish and Wildlife Service, National Park Service, and local nonfederal sponsors—Brownsville (Texas) Public Utility Board and the City of Brownsville—to study restoration methods on former, naturally cut-off, channels of the Lower Rio Grande River. These aquatic ecosystems, locally termed “resacas,” are home to endemic plants and animals and are thus an important natural resource of national interest. This technical report documents the planning, design, construction, monitoring, and adaptive management activities throughout the Resaca Boulevard Resaca Section 206 Aquatic Ecosystem Restoration project. Methods and results for invasive species management—primarily Brazilian peppertree (Schinus terebinthfolia)—and aquatic and riparian vegetation establishment in endemic Texas ebony resaca forest, subtropical Texas palmetto woodland, and Texas ebony/snake-eyes shrubland habitats are discussed.
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Sunny, Yemuna. Redefining Sustainable Development: Co-Creation of Knowledge with the Bharia People. Indian Institute for Human Settlements, 2023. http://dx.doi.org/10.24943/tesf0706.2023.

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This study examines the lived experiences of the Bharia people of Patalkot with regard to ecology, society, and the modern school. The research methodology, attempting to keep the agency of the Bharia at the centre, has helped to evolve knowledge that is at once embedded and questioning. At the interface of the tribal and the non-tribal existences, like the market and the modern school, there are undercurrents of exploitation, alienation and a sense of being undervalued. The thriving forests of Patalkot enhance socio-cultural and ecological relationships of tribal society and help rethink development in terms of ecological restoration and egalitarian relationships, both of which are in decline in the contemporary phase of capital through liberalisation, globalisation and privatisation.
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Anderson, Donald M., Lorraine C. Backer, Keith Bouma-Gregson, Holly A. Bowers, V. Monica Bricelj, Lesley D’Anglada, Jonathan Deeds et al. Harmful Algal Research & Response: A National Environmental Science Strategy (HARRNESS), 2024-2034. Woods Hole Oceanographic Institution, Juli 2024. http://dx.doi.org/10.1575/1912/69773.

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Harmful and toxic algal blooms (HABs) are a well-established and severe threat to human health, economies, and marine and freshwater ecosystems on all coasts of the United States and its inland waters. HABs can comprise microalgae, cyanobacteria, and macroalgae (seaweeds). Their impacts, intensity, and geographic range have increased over past decades due to both human-induced and natural changes. In this report, HABs refers to both marine algal and freshwater cyanobacterial events. This Harmful Algal Research and Response: A National Environmental Science Strategy (HARRNESS) 2024-2034 plan builds on major accomplishments from past efforts, provides a state of the science update since the previous decadal HARRNESS plan (2005-2015), identifies key information gaps, and presents forward-thinking solutions. Major achievements on many fronts since the last HARRNESS are detailed in this report. They include improved understanding of bloom dynamics of large-scale regional HABs such as those of Pseudo-nitzschia on the west coast, Alexandrium on the east coast, Karenia brevis on the west Florida shelf, and Microcystis in Lake Erie, and advances in HAB sensor technology, allowing deployment on fixed and mobile platforms for long-term, continuous, remote HAB cell and toxin observations. New HABs and impacts have emerged. Freshwater HABs now occur in many inland waterways and their public health impacts through drinking and recreational water contamination have been characterized and new monitoring efforts have been initiated. Freshwater HAB toxins are finding their way into marine environments and contaminating seafood with unknown consequences. Blooms of Dinophysis spp., which can cause diarrhetic shellfish poisoning, have appeared around the US coast, but the causes are not understood. Similarly, blooms of fish- and shellfish-killing HABs are occurring in many regions and are especially threatening to aquaculture. The science, management, and decision-making necessary to manage the threat of HABs continue to involve a multidisciplinary group of scientists, managers, and agencies at various levels. The initial HARRNESS framework and the resulting National HAB Committee (NHC) have proven effective means to coordinate the academic, management, and stakeholder communities interested in national HAB issues and provide these entities with a collective voice, in part through this updated HARRNESS report. Congress and the Executive Branch have supported most of the advances achieved under HARRNESS (2005-2015) and continue to make HABs a priority. Congress has reauthorized the Harmful Algal Bloom and Hypoxia Research and Control Act (HABHRCA) multiple times and continues to authorize the National Oceanic and Atmospheric Administration (NOAA) to fund and conduct HAB research and response, has given new roles to the US Environmental Protection Agency (EPA), and required an Interagency Working Group on HABHRCA (IWG HABHRCA). These efforts have been instrumental in coordinating HAB responses by federal and state agencies. Initial appropriations for NOAA HAB research and response decreased after 2005, but have increased substantially in the last few years, leading to many advances in HAB management in marine coastal and Great Lakes regions. With no specific funding for HABs, the US EPA has provided funding to states through existing laws, such as the Clean Water Act, Safe Drinking Water Act, and to members of the Great Lakes Interagency Task Force through the Great Lakes Restoration Initiative, to assist states and tribes in addressing issues related to HAB toxins and hypoxia. The US EPA has also worked towards fulfilling its mandate by providing tools and resources to states, territories, and local governments to help manage HABs and cyanotoxins, to effectively communicate the risks of cyanotoxins and to assist public water systems and water managers to manage HABs. These tools and resources include documents to assist with adopting recommended recreational criteria and/or swimming advisories, recommendations for public water systems to choose to apply health advisories for cyanotoxins, risk communication templates, videos and toolkits, monitoring guidance, and drinking water treatment optimization documents. Beginning in 2018, Congress has directed the U.S. Army Corps of Engineers (USACE) to develop a HAB research initiative to deliver scalable HAB prevention, detection, and management technologies intended to reduce the frequency and severity of HAB impacts to our Nation’s freshwater resources. Since the initial HARRNESS report, other federal agencies have become increasingly engaged in addressing HABs, a trend likely to continue given the evolution of regulations(e.g., US EPA drinking water health advisories and recreational water quality criteria for two cyanotoxins), and new understanding of risks associated with freshwater HABs. The NSF/NIEHS Oceans and Human Health Program has contributed substantially to our understanding of HABs. The US Geological Survey, Centers for Disease Control and Prevention, and the National Aeronautics Space Administration also contribute to HAB-related activities. In the preparation of this report, input was sought early on from a wide range of stakeholders, including participants from academia, industry, and government. The aim of this interdisciplinary effort is to provide summary information that will guide future research and management of HABs and inform policy development at the agency and congressional levels. As a result of this information gathering effort, four major HAB focus/programmatic areas were identified: 1) Observing systems, modeling, and forecasting; 2) Detection and ecological impacts, including genetics and bloom ecology; 3) HAB management including prevention, control, and mitigation, and 4) Human dimensions, including public health, socio-economics, outreach, and education. Focus groups were tasked with addressing a) our current understanding based on advances since HARRNESS 2005-2015, b) identification of critical information gaps and opportunities, and c) proposed recommendations for the future. The vision statement for HARRNESS 2024-2034 has been updated, as follows: “Over the next decade, in the context of global climate change projections, HARRNESS will define the magnitude, scope, and diversity of the HAB problem in US marine, brackish and freshwaters; strengthen coordination among agencies, stakeholders, and partners; advance the development of effective research and management solutions; and build resilience to address the broad range of US HAB problems impacting vulnerable communities and ecosystems.” This will guide federal, state, local and tribal agencies and nations, researchers, industry, and other organizations over the next decade to collectively work to address HAB problems in the United States.
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