Bibliografie tematiche / Native plants

Letteratura scientifica selezionata sul tema "Native plants"

Autore: Grafiati
Pubblicato: 4 giugno 2021
Ultima modifica: 21 febbraio 2023

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Articoli di riviste sul tema "Native plants"

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Meyer, Mary H., e Helen C. Harrison. "Using Native Plants". HortScience 32, n. 3 (giugno 1997): 493A—493. http://dx.doi.org/10.21273/hortsci.32.3.493a.

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Using Native Plants is a 120-min videotape that was developed as a result of a Cooperative Extension Partnership Programming Grant between the Univ. of Minnesota, Minnesota Extension Service and the Cooperative Extension–Univ. of Wisconsin-Extension. The content covers woodland wildflowers, prairie establishment and maintenance, landscaping lakeshores, and using native plants in traditional gardens settings.Video segments include: Eloise Butler Wildflower garden, Minneapolis, Minn.; Curtis Prairie, Madison, Wis.; Big Sandy Lake, Minn.; and the Minnesota Landscape Arboretum, Chanhassen. Developed originally as advanced Master Gardener training, the program was a national satellite broadcast on 29 Feb. 1996. It was viewed by at least nine states and more than 500 participants. Video production costs, including a 20-page participant's handout with extensive references and plant lists, were just under $13,000. A cost analysis, evaluation, sample of the participant's packet, pictures from the videotape and an order form will be presented. Copies of the tape and print packet may be obtained for $50 from Minnesota Extension Service, 1.800.876.8636, or Univ. of Wisconsin-Extension, at 1.608.262.3346.
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Pearse, Ian S., e Andrew L. Hipp. "Native plant diversity increases herbivory to non-natives". Proceedings of the Royal Society B: Biological Sciences 281, n. 1794 (7 novembre 2014): 20141841. http://dx.doi.org/10.1098/rspb.2014.1841.

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There is often an inverse relationship between the diversity of a plant community and the invasibility of that community by non-native plants. Native herbivores that colonize novel plants may contribute to diversity–invasibility relationships by limiting the relative success of non-native plants. Here, we show that, in large collections of non-native oak trees at sites across the USA, non-native oaks introduced to regions with greater oak species richness accumulated greater leaf damage than in regions with low oak richness. Underlying this trend was the ability of herbivores to exploit non-native plants that were close relatives to their native host. In diverse oak communities, non-native trees were on average more closely related to native trees and received greater leaf damage than those in depauperate oak communities. Because insect herbivores colonize non-native plants that are similar to their native hosts, in communities with greater native plant diversity, non-natives experience greater herbivory.
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Ornduff, Robert. "Native Plants: Conservation Priorities". Science 243, n. 4898 (24 marzo 1989): 1535. http://dx.doi.org/10.1126/science.243.4898.1535.b.

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ORNDUFF, R. "Native Plants: Conservation Priorities". Science 243, n. 4898 (24 marzo 1989): 1535. http://dx.doi.org/10.1126/science.243.4898.1535-a.

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Sun, Yan, e Aline Junod. "Invasive plants differ from native plants in their impact on native communities". Journal of Vegetation Science 28, n. 6 (novembre 2017): 1250–59. http://dx.doi.org/10.1111/jvs.12582.

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Liu, X. A., Y. Peng, J. J. Li e P. H. Peng. "Enhanced shoot investment makes invasive plants exhibit growth advantages in high nitrogen conditions". Brazilian Journal of Biology 79, n. 1 (gennaio 2019): 15–21. http://dx.doi.org/10.1590/1519-6984.169578.

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Abstract Resource amendments commonly promote plant invasions, raising concerns over the potential consequences of nitrogen (N) deposition; however, it is unclear whether invaders will benefit from N deposition more than natives. Growth is among the most fundamental inherent traits of plants and thus good invaders may have superior growth advantages in response to resource amendments. We compared the growth and allocation between invasive and native plants in different N regimes including controls (ambient N concentrations). We found that invasive plants always grew much larger than native plants in varying N conditions, regardless of growth- or phylogeny-based analyses, and that the former allocated more biomass to shoots than the latter. Although N addition enhanced the growth of invasive plants, this enhancement did not increase with increasing N addition. Across invasive and native species, changes in shoot biomass allocation were positively correlated with changes in whole-plant biomass; and the slope of this relationship was greater in invasive plants than native plants. These findings suggest that enhanced shoot investment makes invasive plants retain a growth advantage in high N conditions relative to natives, and also highlight that future N deposition may increase the risks of plant invasions.
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Wijesundara, D. S. A. "Can native plants become invasive?" Ceylon Journal of Science 46, n. 1 (22 marzo 2017): 1. http://dx.doi.org/10.4038/cjs.v46i1.7412.

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Payne, Jerry A. "IN DEFENSE OF NATIVE PLANTS". HortScience 25, n. 10 (ottobre 1990): 1202a—1202. http://dx.doi.org/10.21273/hortsci.25.10.1202a.

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Koester, Heiko. "Native plants and urban sustainability". Native Plants Journal 9, n. 3 (ottobre 2008): 323–33. http://dx.doi.org/10.2979/npj.2008.9.3.323.

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Roberts, L. "Extinction Imminent for Native Plants". Science 242, n. 4885 (16 dicembre 1988): 1508. http://dx.doi.org/10.1126/science.242.4885.1508.

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Tesi sul tema "Native plants"

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Zuefle, Marion E. "The impact of non-native woody plants on the native herbivorous insect community of northern Delaware". Access to citation, abstract and download form provided by ProQuest Information and Learning Company; downloadable PDF file, 75 p, 2006. http://proquest.umi.com/pqdweb?did=1163239621&sid=7&Fmt=2&clientId=8331&RQT=309&VName=PQD.

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Von, Richter Lotte Victoria. "Native plants of Eastern Australia as bedding plants". Thesis, The University of Sydney, 1996. https://hdl.handle.net/2123/27551.

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Bedding plants are used extensively in many landscaping situations. The majority of bedding plants marketed commercially are exotic species with only limited propagation material of Australian species available. The objectives of this work was to assess Australian short—lived perennial species as bedding plants with particular reference to their ease of propagation from seed. An extensive survey of Eastern states Australian native annual and short lived perennial species has identified the following species as showing potential as bedding plants.
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White, Annie. "From Nursery to Nature: Evaluating Native Herbaceous Flowering Plants Versus Native Cultivars for Pollinator Habitat Restoration". ScholarWorks @ UVM, 2016. http://scholarworks.uvm.edu/graddis/626.

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There is growing awareness about the value of preserving and restoring floral-rich habitats for the benefit of pollinators, especially native bees. The increasing demand for native plants in pollinator habitat restoration and other ecological landscaping applications, combined with the desire for more robust and predictable plant habits, have led to the selection and breeding of native cultivars. Yet, little is known about how these cultivated varieties differ from the native species in their ability to attract and support pollinators. I compared flower visitation by all insect pollinators to 12 native herbaceous plant species and 14 native cultivars in a replicated field experiment at two sites over two years. I classified insect pollinators during visual field observations into seven taxonomic and functional groups. I found seven native species to be visited significantly more frequently by all insect pollinators (combined) than their cultivars, four were visited equally, and one native cultivar was visited more frequently than the native species. Bees (both native and non-native) and moths/butterflies exhibited similar preferences, whereas flies showed no preference between the native species and the native cultivar. Our study shows that many insect pollinators prefer to forage on native species over cultivated varieties of the native species, but not always, and not exclusively. Some native cultivars may be comparable substitions for native species in pollinator habitat restoration projects, but all cultivars should be evaluated on an individual basis. Plant selection is integral to the value and success of pollinator habitat restorations, yet there is little consistency and overlap in pollinator planting recommendations and very little empirical data to support plant choice. Non peer-reviewed pollinator plant lists are widely available and are often region-specific, but they are typically based on anecdotal rather than empirical data and lack in specificity. To help close the gap between anecdotal and empirical data, and between practice and research, I reviewed the published literature on plant selection for pollinator habitat restoration. I explicitly reviewed and compared the value of native plant species, near-natives, non-natives and native cultivars. From there, I identified gaps in the literature that are most needed in practice and recommended basic strategies for practitioners to navigate plant lists and choose the best plants for a site's success.
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Cerqueira, Nicole. "Pollinator visitation preference on native and non-native congeneric plants". Access to citation, abstract and download form provided by ProQuest Information and Learning Company; downloadable PDF file 2.91 Mb., 84 p, 2005. http://wwwlib.umi.com/dissertations/fullcit/1428175.

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Vodraska, Ellery Ala. "The influence of native plants on arthropod population dynamics can native plants enhance conservation biological control /". College Park, Md.: University of Maryland, 2008. http://hdl.handle.net/1903/8239.

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Thesis (M.S.) -- University of Maryland, College Park, 2008.
Thesis research directed by: Dept. of Entomology. Title from t.p. of PDF. Includes bibliographical references. Published by UMI Dissertation Services, Ann Arbor, Mich. Also available in paper.
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Ruchala, Stacy L. "Propagation of Several Native Ornamental Plants". Fogler Library, University of Maine, 2002. http://www.library.umaine.edu/theses/pdf/RuchalaSL2002.pdf.

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Beilharz, Vyrna Caldwell. "Cercosporoid fungi on Australian native plants /". Connect to thesis, 1994. http://eprints.unimelb.edu.au/archive/00000670.

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Howery, Larry D., Ed Northam, Walt Meyer, Jennifer Arnold, Emilio Carrillo, Kristen Egen e Mary Hershdorfer. "Non-Native Invasive Plants of Arizona". College of Agriculture, University of Arizona (Tucson, AZ), 2016. http://hdl.handle.net/10150/625545.

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84 pp. / First Edition Published 2001
The noxious weed problem in the western United States has been described as, a biological forest fire racing beyond control because no one wants to be fire boss. Indeed, when small weed infestations are left unchecked, they can grow exponentially and spread across the land much like a slow-moving biological wildfire. However, land consumed by fire usually recovers and is often more productive than before the fire occurred. On the other hand, land consumed by noxious weeds may be irreversibly changed and never again reach its full biological potential. Reviewed 12/2016, First Edition Published 2001
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Howery, Larry D., Ed Northam, Walt Meyer, Jennifer Arnold, Emilio Carrillo, Kristen Egen e Mary Hershdorfer. "Non-Native Invasive Plants of Arizona". College of Agriculture and Life Sciences, University of Arizona (Tucson, AZ), 2009. http://hdl.handle.net/10150/146922.

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Abstract (sommario):
84 pp.
First Edition Published, 2001
The noxious weed problem in the western United States has been described as, a biological forest fire racing beyond control because no one wants to be fire boss. Indeed, when small weed infestations are left unchecked, they can grow exponentially and spread across the land much like a slow-moving biological wildfire. However, land consumed by fire usually recovers and is often more productive than before the fire occurred. On the other hand, land consumed by noxious weeds may be irreversibly changed and never again reach its full biological potential.
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GOODWIN, TROY LAWRENCE. "PRESERVING NATIVE PLANTS THROUGH REGULATION: A CASE STUDY OF THE CITY OF TUCSON'S NPPO (NATIVE PLANT PRESERVATION ORDINANCE)". Thesis, The University of Arizona, 2001. http://hdl.handle.net/10150/555346.

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Libri sul tema "Native plants"

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Sultanbawa, Yasmina, e Fazal Sultanbawa, a cura di. Australian Native Plants. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635.

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Dunne, Niall. A native plants reader. A cura di Brooklyn Botanic Garden. Brooklyn, NY: Brooklyn Botanic Garden, 2012.

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L, Greenberg Katherine, e Merrick Beth D, a cura di. Growing California native plants. 2a ed. Berkeley: University of California Press, 2012.

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Abouguendia, Zoheir M. Seeded native range plants. [Saskatchewan]: Grazing and Pasture Technology Program and Extension Service, Saskatchewan Agriculture and Food, 1995.

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Wasowski, Sally. Landscaping with native Texas plants. Austin, Tex: Texas Monthly Press, 1985.

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Judith, Phillips. Southwestern landscaping with native plants. Santa Fe, N.M: Museum of New Mexico Press, 1987.

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Huddleston, S. Grow native: Landscaping with native and apt plants of the Rocky Mountains. Golden, Colo: Fulcrum Pub., 1998.

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Huddleston, S. Grow native: Landscaping with native and apt plants of the Rocky Mountains. Boulder, Colo: Pruett Pub. Co., 1988.

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Douglas, George W. Rare native vascular plants of British Columbia. [Victoria]: BC Environment, 1998.

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1953-, Meidinger Dellis Vern, Penny J. L. 1971- e British Columbia. Conservation Data Centre., a cura di. Rare native vascular plants of British Columbia. 2a ed. Victoria: British Columbia [Conservation Data Centre], 2002.

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Capitoli di libri sul tema "Native plants"

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Wandrag, Elizabeth M., e Jane A. Catford. "Competition between native and non-native plants." In Plant invasions: the role of biotic interactions, 281–307. Wallingford: CABI, 2020. http://dx.doi.org/10.1079/9781789242171.0281.

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Abstract The introduction of species to new locations leads to novel competitive interactions between resident native and newly-arriving non-native species. The nature of these competitive interactions can influence the suitability of the environment for the survival, reproduction and spread of non-native plant species, and the impact those species have on native plant communities. Indeed, the large literature on competition among plants reflects its importance in shaping the composition of plant communities, including the invasion success of non-native species. While competition and invasion theory have historically developed in parallel, the increasing recognition of the synergism between the two themes has led to new insights into how non-native plant species invade native plant communities, and the impacts they have on those plant communities. This chapter provides an entry point into the aspects of competition theory that can help explain the success, dominance and impacts of invasive species. It focuses on resource competition, which arises wherever the resources necessary for establishment, survival, reproduction and spread are in limited supply. It highlights key hypotheses developed in invasion biology that relate to ideas of competition, outlines biotic and abiotic factors that influence the strength of competition and species' relative competitive abilities, and describes when and how competition between non-native and native plant species can influence invasion outcomes. Understanding the processes that influence the strength of competition between non-native and native plant species is a necessary step towards understanding the causes and consequences of biological invasions.
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Garner, Amanda, e La Vergne Lehmann. "Overview of Australian Native Plants". In Australian Native Plants, 1–4. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-1.

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Mazzorana, Gary, e Melissa Mazzorana. "Cultivation of Lemon Myrtle (Backhousia citriodora)". In Australian Native Plants, 113–26. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-10.

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Sultanbawa, Fazal. "Cultivation of Muntries (Kunzea pomifera F. Muell.)". In Australian Native Plants, 127–32. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-11.

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Read, Christopher D. "Cultivation of Native Pepper (Tasmannia lanceolata)". In Australian Native Plants, 133–45. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-12.

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Lethbridge, Ben. "Cultivation of Quandong (Santalum acuminatum)". In Australian Native Plants, 147–53. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-13.

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Glover, Rus. "Cultivation of Riberry (Syzygium luehmannii)". In Australian Native Plants, 155–63. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-14.

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Dudley, Lyle. "Production of Wattle Seed (Acacia victoriae)". In Australian Native Plants, 165–72. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-15.

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Savigni, Donna. "Alternative Medicines Based on Aboriginal Traditional Knowledge and Culture". In Australian Native Plants, 175–221. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-16.

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Williams, David J., e Mridusmita Chaliha. "Nutritional Characteristics and Bioactive Compounds in Australian Native Plants: A Review". In Australian Native Plants, 223–36. Boca Raton, FL : CRC Press, Taylor & Francis Group, 2016. | Series: Traditional herbal medicines for modern times ; 17: CRC Press, 2017. http://dx.doi.org/10.1201/b20635-17.

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Atti di convegni sul tema "Native plants"

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Gibson, Dan. "Native perennial plants to attract natural enemies". In 2016 International Congress of Entomology. Entomological Society of America, 2016. http://dx.doi.org/10.1603/ice.2016.114440.

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Koppel, L. A., C. Bolle, J. I. Kim e V. A. Sineshchekov. "Native phytochrome A pools differ in serine phosphorylation at the N-terminus of the molecule and mediate different types of photoresponders". In IX Congress of society physiologists of plants of Russia "Plant physiology is the basis for creating plants of the future". Kazan University Press, 2019. http://dx.doi.org/10.26907/978-5-00130-204-9-2019-227.

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Fontowicz, Louis. "Response of four native wetlands plants species to drought and nitrogen imbalances". In ASPB PLANT BIOLOGY 2020. USA: ASPB, 2020. http://dx.doi.org/10.46678/pb.20.1053451.

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Shchegoleva, N. V. "NON-NATIVE PLANTS IN THE TERRITORY OF KUZBASS BOTANICAL GARDEN". In VI Международная конференция "Проблемы промышленной ботаники индустриально развитых регионов". Кемерово: Федеральный исследовательский центр угля и углехимии Сибирского отделения Российской академии наук, 2021. http://dx.doi.org/10.53650/9785902305606_39.

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Mavi, Kazim, Durmus Alpaslan Kaya, Musa Turkmen e Filiz Ayanoglu. "The variation of essential oil and carvacrol contents of native grown Thymbra Spicata var. Spicata L." In The 8th International Conference on Advanced Materials and Systems. INCDTP - Leather and Footwear Research Institute (ICPI), Bucharest, Romania, 2020. http://dx.doi.org/10.24264/icams-2020.ii.18.

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In the study, it is aimed to create breeding lines of thyme (Thymbra spicata L.), which is important both culturally and economically, by selecting a single plant among the plants grown in different regions in Hatay. For this purpose, a genetic pool was created for Thymbra spicata L. plant in the plant samples taken from the locations where the plants are densely grown, and these plants were examined in terms of leaf characteristics, number of oil glands per unit area, oil gud size and essential oil components. Plants were propagated and preserved with cuttings taken from these single plants. In this study, which includes the pre-selection stage, 213 plants from 68 different locations were determined in the province of Hatay. The essential oil ratios of the plants varied between 0.70% and 3.90% and showed a wide variation. The rate of carvacrol, which is the main component of the essential oil of the thyme plant, was between 28.12% and 78.48%. Plants with code number Z14, Z3, Z25, Z38, Z77, Z104, Z35 and Z43 with an essential oil ratio of 3.5% and above and plants with code number Z167, Z165 and Z64 with a high carvacrol ratio were selected to be used in future breeding studies.
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Varga, E., I. Fülöp, L. Farczádi, M. Fazakas e MD Croitoru. "Polyphenolics from Romanian native medicinal plants and used in veterinary medicine". In 67th International Congress and Annual Meeting of the Society for Medicinal Plant and Natural Product Research (GA) in cooperation with the French Society of Pharmacognosy AFERP. © Georg Thieme Verlag KG, 2019. http://dx.doi.org/10.1055/s-0039-3399746.

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Constantinou, George, Onur Orhan, Roopal Kondepudi, Hyunjae Cho, Seon Ho Kim, Abdullah Alfarrarjeh e Cyrus Shahabi. "FloraVision: A Spatial Crowd-based Learning System for California Native Plants". In 2021 IEEE 37th International Conference on Data Engineering (ICDE). IEEE, 2021. http://dx.doi.org/10.1109/icde51399.2021.00313.

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Qian, Jiangfei, Tianyu Li, Lidan Mu, Yuankai Xia, Qing Ji e Ruifang Wang. "The Diversity and Natural Enemies of Eupatorium adenophorum and Native Plants". In The International Conference on Biomedical Engineering and Bioinformatics. SCITEPRESS - Science and Technology Publications, 2022. http://dx.doi.org/10.5220/0011280900003443.

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Rowe, Logan. "Identifying native plants to enhance pollination services for sustainable crop production in Michigan". In 2016 International Congress of Entomology. Entomological Society of America, 2016. http://dx.doi.org/10.1603/ice.2016.115148.

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Dierks, Scott. "The BMP That Keeps on Giving: Quantifying the Impact of Native Plants on Soil Water Properties". In 2011 Low Impact Development Conference. Reston, VA: American Society of Civil Engineers, 2015. http://dx.doi.org/10.1061/9780784413883.004.

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Rapporti di organizzazioni sul tema "Native plants"

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Dumroese, R. Kasten, Thomas D. Landis e Tara Luna. Raising native plants in nurseries: basic concepts. Ft. Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, 2012. http://dx.doi.org/10.2737/rmrs-gtr-274.

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Guyton, John, Jeanne C. Jones e Edward Entsminger. Alternative Mowing Regimes’ Influence on Native Plants and Deer. Mississippi State University, luglio 2014. http://dx.doi.org/10.54718/bybx1010.

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This study evaluated mowing regimes, changes in native and non-native plant communities, deer presence in the research plots,and public perception of various management practices on ROWs. No significant difference was found in the height of vegetation 3 weeks after each mowing between research plots mowed 4 times per year and plots mowed only once per year in uplands or lowlands. Native plants increased in plots mowed once per year and deer preferred the frequently mowed plots where clovers and vetches had been seeded. Increasing the carrying capacity of the lowlands with more extensive plantings of clover and vetch may attract deer, thus encouraging them to browse and use the underpasses beneath bridges and making the ROWs safer. The public survey found strong support for wildflowers on ROWs and a distaste for litter. Further, respondents would tolerate a less manicured ROW if it saved money, made the roads safer, and hid litter.
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Dick, Gary O., R. M. Smart e Lynde L. Dodd. Propagation and Establishment of Native Plants for Vegetative Restoration of Aquatic Ecosystems. Fort Belvoir, VA: Defense Technical Information Center, giugno 2013. http://dx.doi.org/10.21236/ada582960.

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Smith, Thomas, e Ann L. Hild. Effectiveness of Selected Native Plants as Competitors with Non-indigenous and Invasive Knapweed and Thistle Species. Fort Belvoir, VA: Defense Technical Information Center, settembre 2011. http://dx.doi.org/10.21236/ada553671.

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5

Freedman, Jan E., Michael J. Grodowitz, Robin Swindle e Julie G. Nachtrieb. Potential Use of Native and Naturalized Insect Herbivores and Fungal Pathogens of Aquatic and Wetland Plants. Fort Belvoir, VA: Defense Technical Information Center, agosto 2007. http://dx.doi.org/10.21236/ada471715.

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6

Bortz, Tyler, Molly Davis e Ryan Manuel. Plant community composition and structure monitoring at Fort Laramie National Historic Site: 2020 data report. National Park Service, aprile 2022. http://dx.doi.org/10.36967/nrds-2293003.

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Abstract (sommario):
This report presents the results of vegetation monitoring efforts in 2020 at Fort Laramie National Historic Site (FOLA) by the Northern Great Plains Inventory and Monitoring Network (NGPN) and the United States Geological Survey (USGS). This was the tenth year of combined monitoring efforts. Crew members from USGS visited 9 long-term monitoring plots to collect data on the plant communities at FOLA. This work is part of a long-term monitoring effort designed to provide a better understanding of the condition of the vegetation community at FOLA and how it changes over time. USGS staff measured species richness, herb-layer height, native and non-native species abundance, ground cover, and site disturbance at each of the nine plots. In plots where woody species were present, tree regeneration, tall shrub density, tree density, and woody fuel loads were also measured. Data collection at seven plots was incomplete, where only point-intercept, site disturbance, and invasive species presence data were collected, while in two plots the previously listed protocols as well as the quadrat protocol were performed. In 2020, the monitoring crews identified 44 unique plant species in 9 monitoring plots. Of those species, 19 were exotic species. In a majority of plots (5 of 9), there was a greater percent of native species cover compared to exotic species cover. However, exotic plants were found at every plot in FOLA. No rare species were observed during our surveys
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Shamblin, Robert, Kevin Whelan, Mario Londono e Judd Patterson. South Florida/Caribbean Network early detection protocol for exotic plants: Corridors of invasiveness. National Park Service, luglio 2022. http://dx.doi.org/10.36967/nrr-2293364.

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Exotic plant populations can be potentially catastrophic to the natural communities of South Florida. Aggressive exotics such as Brazillian Pepper (Schinus terebinthifolius) and Melaleuca (Melaleuca quinquinervia) have displaced native habitats and formed monocultures of exotic stands (Dalrymple et al. 2003). Nearby plant nurseries, especially the ones outside the boundaries of Biscayne National Park (BISC) and Everglades National Park (EVER), are a continuous source of new exotic species that may become established within South Florida’s national parks. Early detection and rapid response to these new species of exotic plants is important to maintaining the integrity of the parks’ natural habitats and is a cost-effective approach to management. The South Florida/Caribbean Network (SFCN) developed the South Florida/Caribbean Network Early Detection Protocol for Exotic Plants to target early detection of these potential invaders. Three national parks of South Florida are monitored for invasive, exotic plants using this protocol: Big Cypress National Preserve (BICY), Biscayne National Park (BISC), and Everglades National Park (EVER). These national parks include some 2,411,000 acres (3,767.2 square miles [mi2]) that encompass a variety of habitat types. To monitor the entire area for new species would not be feasible; therefore the basic approach of this protocol is to scan major “corridors of invasiveness,” e.g., paved and unpaved roads, trails, trail heads, off road vehicle (ORV) trails, boat ramps, canals, and campgrounds, for exotic plant species new to the national parks of South Florida. Sampling is optimized using a two- to three-person crew: a trained botanist, a certified herbicide applicator, and optionally a SFCN (or IPMT [Invasive Plant Management Team]) staff member or park staff to take photographs and help with data collection. If infestations are small, they are treated immediately by the herbicide applicator. If large, they are reported to park staff and the Invasive Plant Management Team. The sampling domain is partitioned into five regions, with one region sampled per year. Regions include the terrestrial habitats of Biscayne National Park, the eastern region of Everglades National Park, the western region of Everglades National Park, the northern region of Big Cypress National Preserve, and the southern region of Big Cypress National Preserve. Monitoring of roads, trails, and canals occurs while traveling into and through the parks (i.e., travel at 2–10 mph) using motorized vehicles, airboats, and/or hiking. Campgrounds, boat launches, trailheads, and similar areas, involve complete searches. When an exotic plant is observed, a GPS location is obtained, and coordinates are taken of the plant. Photographs are not taken for every exotic plant encountered, but photographs will be taken for new and unusual species (for example a coastal exotic found in inland habitats). Information recorded at each location includes the species name, size of infestation, abundance, cover class, any treatment/control action taken, and relevant notes. During the surveys, a GPS “track” is also recorded to document the areas surveyed and a field of view is estimated. Field notes, pictures, and GPS data are compiled, entered, and analyzed in a Microsoft Access database. Resource briefs (and optional data summary reports) and associated shapefiles and data are then produced and sent to contacts within the corresponding national parks.
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Kull, Kathleen, Craig Young, Jennifer Haack-Gaynor, Lloyd Morrison e Michael DeBacker. Problematic plant monitoring protocol for the Heartland Inventory and Monitoring Network: Narrative, version 2.0. National Park Service, maggio 2022. http://dx.doi.org/10.36967/nrr-2293355.

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Abstract (sommario):
Problematic species, which include invasive, exotic, and harmful species, fragment native ecosystems, displace native plants and animals, and alter ecosystem function. In National Parks, such species negatively affect park resources and visitor enjoyment by altering landscapes and fire regimes, reducing native plant and animal habitat, and increasing trail maintenance needs. Recognizing these challenges, Heartland Inventory and Monitoring (I&M) Network parks identified problematic plants as the highest-ranking vital sign across the network. Given the need to provide early detection of potential problematic plants (ProPs) and the size of network parks, the Heartland I&M Network opted to allocate available sampling effort to maximize the area searched. With this approach and the available sampling effort in mind, we developed realistic objectives for the ProP monitoring protocol. The monitoring objectives are: 1. Create a watch list of ProPs known to occur in network parks and a watch list of potential ProPs that may invade network parks in the future, and occasionally update these two lists as new information is made available. 2. Provide early detection monitoring for all ProPs on the watch lists. 3. Search at least 0.75% and up to 40% of the reference frame for ProP occurrences in each park. 4. Estimate/calculate and report the abundance and frequency of ProPs in each park. 5. To the extent possible, identify temporal changes in the distribution and abundance of ProPs known to occur in network parks. ProP watch lists are developed using the best available and most relevant state, regional, and national exotic plant lists. The lists are generated using the PriorityDB database. We designed the park reference frames (i.e., the area to be monitored) to focus on accessible natural and restored areas. The field methods vary for small parks and large parks, defined as parks with reference frames less than and greater than 350 acres (142 ha), respectively. For small parks, surveyors make three equidistant passes through polygon search units that are approximately 2-acres (0.8 ha) in size. For large parks, surveyors record each ProP encountered along 200-m or 400-m line search units. The cover of each ProP taxa encountered in search units is estimated using the following cover scale: 0 = 0, 1 = 0.1-0.9 m2, 2 = 1-9.9 m2, 3 = 10-49.9 m2, 4 = 50-99.9 m2, 5 = 100-499.9 m2, 6 = 499.9-999.9 m2, and 7 = 1,000-4,999.9 m2. The field data are managed in the FieldDB database. Monitoring is scheduled to revisit most parks every four years. The network will report the results to park managers and superintendents after completing ProP monitoring.
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Marks, David R. Mute Swans. U.S. Department of Agriculture, Animal and Plant Health Inspection Service, febbraio 2018. http://dx.doi.org/10.32747/2018.7208745.ws.

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Mute swans (Cygnus olor) are an invasive species originally brought to the United States in the late 19th and early 20th centuries for ornamental ponds and lakes, zoos and aviculture collections. Original populations were located in northeastern states along the Hudson Valley but have since expanded to several Midwestern states and portions of the western U.S. and Canada. Mute swan damage includes competing with native waterfowl, destroying native plants, spreading disease, and colliding with aircraft. They are also considered a nuisance in some areas due to their abundant fecal droppings and aggressiveness towards people. Some have questioned the status of mute swans as an introduced species, but multiple reviews by scientists and the U.S. Fish and Wildlife Service clearly support the conclusion that mute swans are not native to North America. The Migratory Bird Treaty Act, therefore, does not protect mute swans, and management authority falls under jurisdiction of the states and Tribes.
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Chamovitz, Daniel A., e Albrecht G. Von Arnim. eIF3 Complexes and the eIF3e Subunit in Arabidopsis Development and Translation Initiation. United States Department of Agriculture, settembre 2009. http://dx.doi.org/10.32747/2009.7696545.bard.

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The original working hypothesis of our proposal was that The “e” subunit of eIF3 has multiple functions from both within the nucleus and in the cytoplasm. Within this model, we further hypothesized that the “e” subunit of eIF3 functions in translation as a repressor. We proposed to test these hypotheses along the following specific aims: 1) Determine the subcellular localization of the interaction between eIF3e and other eIF3 subunits, or the COP9 signalosome. 2) Elucidate the biological significance of the varied subcellular localizations of eIF3e through generating Arabidopsis eIF3e alleles with altered subcellular localization. 3.) Purify different eIF3e complexes by tandem affinity purification (TAP). 4) Study the role of eIF3e in translational repression using both in vitro and in planta assays. eIF3 is an evolutionarily ancient and essential component of the translational apparatus in both the plant and animal kingdoms. eIF3 is the largest, and in some ways the most mysterious, of the translation factors. It is a multi-subunit protein complex that has a structural/scaffolding role in translation initiation. However, despite years of study, only recently have differential roles for eIF3 in the developmental regulation of translation been experimentally grounded. Furthermore, the roles of individual eIF3 subunits are not clear, and indeed some, such as the “e” subunit may have roles independent of translation initiation. The original three goals of the proposal were technically hampered by a finding that became evident during the course of the research – Any attempt to make transgenic plants that expressed eIF3e wt or eIF3e variants resulted in seedling lethality or seed inviability. That is, it was impossible to regenerate any transgenic plants that expressed eIF3e. We did manage to generate plants that expressed an inducible form of eIF3e. This also eventually led to lethality, but was very useful in elucidating the 4th goal of the research (Yahalom et al., 2008), where we showed, for the first time in any organism, that eIF3e has a repressory role in translation. In attempt to solve the expression problems, we also tried expression from the native promoter, and as such analyzed this promoter in transgenic plants (Epel, 2008). As such, several additional avenues were pursued. 1) We investigated protein-protein interactions of eIF3e (Paz-Aviram et al., 2008). 2) The results from goal #4 led to a novel hypothesis that the interaction of eIF3e and the CSN meets at the control of protein degradation of nascent proteins. In other words, that the block in translation seen in csn and eIF3e-overexpressing plants (Yahalom et al., 2008) leads to proteasome stress. Indeed we showed that both over expression of eIF3e and the csn mutants lead to the unfolded protein response. 3) We further investigated the role of an additional eIF3 subunit, eIF3h, in transalational regulation in the apical meristem (Zhou et al., 2009). Epel, A. (2008). Characterization of eIF3e in the model plant Arabidopsis thaliana. In Plant Sciences (Tel Aviv, Tel Aviv University). Paz-Aviram, T., Yahalom, A., and Chamovitz, D.A. (2008). Arabidopsis eIF3e interacts with subunits of the ribosome, Cop9 signalosome and proteasome. Plant Signaling and Behaviour 3, 409-411. Yahalom, A., Kim, T.H., Roy, B., Singer, R., von Arnim, A.G., and Chamovitz, D.A. (2008). Arabidopsis eIF3e is regulated by the COP9 signalosome and has an impact on development and protein translation. Plant J 53, 300-311. Zhou, F., Dunlap, J.R., and von Arnim, A.G. The translation initiation factor subunit eIF3h is .1 involved in Arabidopsis shoot apical meristem maintenance and auxin response. (submitted to Development).
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