Tesi sul tema "Seed bank"
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Tolley, Rebecca. "Seed Bank". Digital Commons @ East Tennessee State University, 2012. https://dc.etsu.edu/etsu-works/5660.
Testo completoTolley, Rebecca. "Seed Banks". Digital Commons @ East Tennessee State University, 2007. https://www.amzn.com/031333725X.
Testo completoYehnjong, Petra Seka. "Paleozoic Seed Bank and Their Ecological Significance". Digital Commons @ East Tennessee State University, 2014. https://dc.etsu.edu/etd/2316.
Testo completoKellerman, Millicent Johanna Susanna. "Seed bank dynamics of selected vegetation types in Maputaland, South Africa". Diss., Connect to this title online, 2004. http://upetd.up.ac.za/thesis/available/etd-02012005-090837.
Testo completoCooper, Cara A. "Melinis repens Seed Bank Longevity in Miami-Dade County". FIU Digital Commons, 2012. http://digitalcommons.fiu.edu/etd/677.
Testo completoMartin, Anna. "Mathematical modeling of seed bank dynamics in population genetics". Thesis, Uppsala universitet, Institutionen för informationsteknologi, 2017. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-321191.
Testo completoDavis, Jessica. "Soil seed bank dynamics in Mediterranean urban vegetation fragments". Thesis, Davis, Jessica (2012) Soil seed bank dynamics in Mediterranean urban vegetation fragments. Masters by Coursework thesis, Murdoch University, 2012. https://researchrepository.murdoch.edu.au/id/eprint/12926/.
Testo completoPassos, Isabel Maria Melo Mendes. "Importance of seed bank for the management of invasive Acacia dealbata". Master's thesis, Universidade de Aveiro, 2014. http://hdl.handle.net/10773/13375.
Testo completoThe management of invasive plants is a hard task, which may be further hampered by the existence of extensive and long-lived seed banks. Acacia dealbata is an Australian tree considered one of the most aggressive invasive plant species in Portugal; the species is known to produce a persistent seed bank, but its extension and viability hasn’t been explored. In this work we aim to characterize the seed bank of A. dealbata, namely its extension, germinability and viability, in order to contribute to the management of the species, but also increase knowledge about its ecology. The extension of the seed bank was assessed by collecting soil samples in invaded stands and adjacent areas and counting the seeds. These were then germinated at 25ºC and some were exposed to an initial temperature of 60ºC, aiming to assess the effect of extreme soil temperature in dormancy breaking. Results showed that beneath canopy the seed bank averaged 4 608 seed/m2 (± 820), but maximum values can reach 62 747 seeds/m2. In areas adjacent to the invaded stands a mean value of 9 seeds/m2 (± 5) was found, with maximum values of 632 seeds/m2. Although only 8,6% of the seeds germinated without any stimulus, in total 89,7% of the seeds found showed to be viable after scarification, with 81% of the seeds remaining dormant in the soil. Of the seeds exposed to 60ºC almost 64% germinated without any physical stimulation, suggesting that extreme soil temperatures, reached in hot days, may break seed dormancy. Multivariate analysis showed that the probability of accumulating high numbers of seeds in soil decreases with higher stoniness and root density, and increases with higher A. dealbata density and with fewer fire events. Our results show that the soil seed bank of A. dealbata is numerous and viable, suggesting that risk of reinvasion after plant removal is very high. It was also shown that the species has the ability to disperse seed beyond invaded stands Although frequently disregarded, this study alerts for the need to include extensive and long-lived seed banks in the management of invasive plants, since these hidden legacies may quickly hamper control efforts. Alternatives to deal with such seed banks are discussed.
O controlo de plantas invasoras é uma tarefa árdua, dificultada pela existência de bancos de sementes extensos e com longa viabilidade. A espécie Acacia dealbata é uma árvore nativa da Austrália, considerada como uma das espécies invasoras mais agressivas em Portugal. Sabe-se que o seu banco de sementes permanece viável no solo por muitos anos, no entanto a sua extensão e a viabilidade das sementes não são ainda conhecidos. O presente trabalho tem como objetivo caracterizar esse banco de sementes, a sua extensão, viabilidade e germinabilidade, de forma a contribuir para a sua gestão e para o conhecimento geral sobre a ecologia da espécie. A extensão do banco de sementes foi avaliada através da recolha de amostras de solo em áreas invadidas e zonas adjacentes não invadidas, realizando-se depois a contagem das sementes. Depois de contabilizadas, as sementes foram postas a germinar a 25ºC, sendo que uma parte foi exposta a uma temperatura inicial de 60ºC, com o objetivo de perceber se temperaturas extremas no solo podem quebrar a dormência das sementes. Os resultados indicam que nas áreas invadidas o banco de sementes tem uma densidade média de 4 608 sementes/m2 (± 820), sendo que os valores máximos observados foram de 62 747 sementes/m2. Nas áreas adjacentes observaram-se em média 9 sementes/m2 (± 5), com um valor máximo de 632 sementes/m2. Apesar de apenas 8,6% das sementes terem germinado sem qualquer estímulo, 89,7% do banco de sementes germinou após a escarificação das sementes, indicando que 81% das sementes armazenadas no solo se encontram dormentes. Das sementes inicialmente expostas a 60ºC, cerca de 64% germinaram sem escarificação, sugerindo que a ocorrência de temperaturas anormalmente altas pode estimular a germinação. De acordo com a análise estatística efetuada a probabilidade o número de sementes acumuladas no solo diminui com o aumento de pedregosidade e com a densidade de raízes; por outro lado, o banco de sementes aumenta com densidade de A. dealbata e em áreas sujeitas a menos incêndios. Os resultados obtidos demonstram a elevada viabilidade e densidade do banco de sementes de A.dealbata, evidenciando o elevado risco de reinvasão de áreas onde se realizam ações de controlo da espécie. Este estudo alerta para a necessidade de incluir a gestão do banco de sementes nos planos de controlo de espécies invasoras,alertando para o facto de a espécie ser capaz de dispersar sementes atém das áreas invadidas. Estas características transformam o banco de sementes numa herança escondida, que pode dificultar as ações de controlo. São discutidos diferentes métodos possíveis para lidar com bancos de sementes.
Goodson, Joanne Marie. "Environmental controls on the colonisation and establishment of vegetation on river banks under varying grazing pressure". Thesis, University of Birmingham, 2002. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.289259.
Testo completoAuffret, Alistair G., e Sara A. O. Cousins. "Past and present management influences the seed bank and seed rain in a rural landscape mosaic". Stockholms universitet, Institutionen för naturgeografi och kvartärgeologi (INK), 2011. http://urn.kb.se/resolve?urn=urn:nbn:se:su:diva-69879.
Testo completoShort, Nicolyn. "Implications of green manure amendments on soil seed bank dynamics". University of Western Australia. School of Earth and Geographical Sciences, 2006. http://theses.library.uwa.edu.au/adt-WU2006.0022.
Testo completoStrydom, Matthys. "A perspective on the seed bank dynamics of Acacia saligna". Thesis, Stellenbosch : Stellenbosch University, 2012. http://hdl.handle.net/10019.1/20389.
Testo completoENGLISH ABSTRACT: Acacia saligna, or Port Jackson, is an Australian Acacia which has spread throughout the Western and Eastern Cape provinces of South Africa where it has become invasive and a prominent feature of the vegetation. In areas where A. saligna establishes it replaces natural vegetation, alters ecosystem processes and interferes with agricultural practices. Consequently large management efforts have been made to eradicate this invasive alien tree. However, its large and persistent soil stored seed bank, even in the presence of management and biological control agents, poses a serious obstacle to its successful removal. Furthermore the reproductive output and the size of the seed bank of A. saligna over its whole distribution as well as the variation of seed production and the seed bank with environmental conditions in time and space is poorly known. Understanding the seed bank dynamics of A. saligna in time and space is essential for reducing invasive success and achieving management objectives. This study has filled this knowledge gap through studying the seed production and seed bank of A. saligna over its invaded range in South Africa, including how environmental factors influence these factors in time and space. The seed rain of A. saligna was assessed at 10 sites across its distribution in South Africa. The seed rain of A. saligna at the sites was determined through the use of seed rain traps. Twenty five traps were placed out at every site during November 2010 (pre-dehiscence) which was collected again during April 2011 (postdehiscence). The seed bank of A. saligna was estimated through sampling at 25 sites across its distribution range in South Africa. The seed bank was sampled during April 2010 (postdehiscence), November 2010 (pre-dehiscence) and April 2011 (post-dehiscence) through taking 50 litter and soil samples at every site which gave a total sampling size of 3 750 for both the seed in the soil and litter over its distribution in South Africa. In addition the average tree diameter, tree density, average number of Uromycladium tepperianum induced galls per tree, the summer aridity index, De Martonne aridity index, winter concentration of precipitation, temperature of coldest month and the soil texture for every site was determined. The damage done by the seed feeding weevil, Melanterius compactus, was also estimated for the seed rain study sites. Water availability during the hot summer months was assessed as the most important factor governing seed production and seed bank size. Riparian and non-riparian water regimes were shown to be important in understanding the seed bank dynamics of A. saligna over its distribution range in the Cape Floristic Region. In non-riparian A. saligna populations the seed production and consequently the size of the seed bank and its rate of accumulation is limited by both water and temperature and in riparian A. saligna populations, only by temperature. Therefore, two environmental gradients influence the seed bank dynamics of Port Jackson in South Africa. In non-riparian A. saligna populations the number of seed produced and the accumulation of seed in the seed bank generally increases along the west coast of South Africa from Clanwilliam towards Cape Town and along the south coast from Cape Town towards Port Elizabeth. Seed banks are larger closer to the coast, when A. saligna populations of similar age are compared. In riparian A. saligna populations, the number of seed produced generally increases from Port Elizabeth towards Cape Town and from Cape Town towards Clanwilliam, again, with larger seed banks being accumulated closer to the coast, when populations of similar age are compared. This study provides managers with a useful tool for prioritising management efforts.
AFRIKAANSE OPSOMMING: Acacia saligna of Port Jackson is ‘n indringerplant in Suid-Afrika wat afkomstig is uit Suid-Wes Australië. Acacia saligna is ‘n onmisbare kenmerk van die plantegroei in die Wes en Oos-Kaap. Waar Port Jackson vestig, verplaas dit natuurlike plantegroei, verander dit ekosisteem prossesse en verhinder dit landbou praktyke. Gevolglik is groot bestuurspogings aangewend om hierdie indringer plant uit te roei. In die teenwoordigheid van bestuursprogramme en biologiese beheer bly A. saligna lewensvatbaar as ‘n gevolg van die plant se groot blywende grond saadreserwes. Verder is die saad produksie en saadbank grootte van A. saligna oor sy verspreiding bereike asook hoe dit met omgewingstoestande in tyd en ruimte interreageer en varieer grootendeels onbekend. ‘n Goeie en omvattende begrip van die saadbankdinamika is belangrik om die indringings vermoë van die plant te verlaag en om bestuursdoelwitte te bereik. Hierdie studie vul die bestaande gaping in die kennis aangaande die saadbank dinamika van A. saligna aan deur die saadproduksie en die saadreserves van die indringerplant oor sy verspreiding in Suid-Afrika te bestudeer, insluitend hoe omgewingstoestande die saadbankdinamika beïnvloed in tyd en ruimte. Die saadreën vir 10 A. saligna populasies was bepaal deur die gebruik van saadlokvalle. Vyf-entwintig lokvalle was uitgeplaas in elke bestudeerde Port Jackson perseel gedurende November 2010 (voor-saadval) wat weer gaan haal is gedurende April 2011 (na-saadval). Die saadbank van A. saligna was bepaal in 25 populasies van die boom gedurende April 2010 (na-saadval), November 2010 (voor-saadval) en April 2011 (na-saadval) deur die neem van 50 blaar- en grondmonsters by elke perseel wat ‘n totaal van 3 750 blaar- en grondmonster gee oor die hele verspreiding van A. saligna in Suid-Afrika. Verder is die gemiddelde boomdeursnee, boomdigtheid, gemiddelde Uromycladium tepperianum geinduseerde galle per boom, die somers droogtheids indeks, De Martonnes droogtheids indeks, die winter konsentrasie van presipitasie, die temperatuur van die koudste maand en die grond tekstuur van elke Port Jackson stand bepaal. Die skade wat die saad voedende kewer, Melanterius compactus, aanrig aan die sade van A. saligna is ook vir die persele waar die saadreën eksperiment uitgevoer is, bepaal. Die beskikbaarheid van water vir A. saligna in die droë somermaande is bepaal as die belangrikste faktor wat die grootte van die saadproduksie en saadbank beïnvloed. Oewer en nie-oewer water omgewings is bevind as noodsaaklik om die saadbank dinamika van A. saligna oor die indringerplant se verspreidingareas in die Kaap Floristiese Streek te verstaan. In nie-oewer A. saligna populasies word saadproduksie en gevolglik die grootte en tempo van akkumulasie van die saadbank deur beide water en temperatuur omstandighede beperk, terwyl in oewer A. saligna populasies word die indringerplant slegs deur temperatuur omstandighede beperk. Gevolglik blyk dit dat twee water beskikbaarheids gradiënte bestaan waarop die plant reageer wat dan uitgedruk word in die plant se saad produksie en gevolglik ook die plant se saadbank. In nie-oewer Port Jackson populasies neem die saadproduksie en die tempo waarteen die saadbank akkumuleer algemeen toe langs die weskus van Clanwilliam na Kaapstad en van Kaapstad na Port Elizabeth, met grootter saadproduksie en saadbank akkumulasie nader aan die kusgebiede, wanneer A. saligna populasies van dieselfde ouderdom vergelyk word. In oewer Port Jackson populasies neem die saadproduksie en die tempo waarteen die saadbank akkumuleer algemeen toe van Port Elizabeth na Kaapstad en van Kaapstad na Clanwilliam, met grootter saadproduksie en saadbank akkumulasie nader aan die kusgebiede, wanneer A. saligna populasies van dieselfde ouderdom vergelyk word. Hierdie studie verskaf bestuursplanne met ‘n nuttige raamwerk waarvolgens uitroeiing en beheer programme vir A. saligna beplan kan word.
Fowler, William. "Soil seed bank dynamics in transferred topsoil: Evaluating restoration potentials". Thesis, Fowler, William (2012) Soil seed bank dynamics in transferred topsoil: Evaluating restoration potentials. Honours thesis, Murdoch University, 2012. https://researchrepository.murdoch.edu.au/id/eprint/13389/.
Testo completoHolmes, P. M. "A comparative study of the seed bank dynamics of two congeneric alien invasive species". Doctoral thesis, University of Cape Town, 1989. http://hdl.handle.net/11427/17724.
Testo completoThe unique vegetation in the lowlands of the fynbos biome is threatened by alien Acacia encroachment. The seed bank dynamics of the two most widespread invaders in the region, Acacia saligma and A. cyclops, was studied to elucidate those factors contributing most to their invasive success. This information was then used to assist in developing optimal control methods. On the basis of information available prior to this study, it was predicted that both species would have large, persistent seed banks in the so.il, and that seed bank processes would provide the - key to invasive success: namely, high seed longevity and heat-stimulated germination. Seed banks were monitored for several years following clearing of the parent stand, using either sites sampled in an earlier study, or sites providing chronosequences of clearing dates. Concurrently, a demographic study of the species' seed banks, including processes from seed rain through to seedling emergence and survival, was done in dense Acacia stands and in fynbos vegetation. Acacia saligma seed banks conformed to predictions, being large and persistent owing to high percentage viability and water-impermeable dormancy. Seed banks accumulate rapidly under dense stands and are "disturbance-coupled" as they have potentially high longevity unless stimulated to germinate by fire. Although A. cyclops seed banks also may be large and long-lived, they display variable percentage viability and dormancy, with the majority of a seed cohort surviving less than a year. Acacia cyclops seed banks do not respond to heat treatment and appear to be "disturbance-uncoupled".
Rossiter, Stephen Cary. "Effects of the seed bank and interseeding in reconstructed tallgrass prairies". Thesis, The University of North Dakota, 2014. http://pqdtopen.proquest.com/#viewpdf?dispub=1552216.
Testo completoDisturbances such as fire and mowing temporarily increase available resources for plants, opening a window of opportunity for establishment. During the recovery of vegetation after disturbance in remnant prairies, seedling establishment is often negligible compared to vegetative regrowth. It is unclear if this is the case in reconstructions. I tested the contribution of seedlings to diversity after disturbance in two, 25-year-old, low diversity reconstructed prairies by removing seedlings, allowing seedlings, and adding seed in 1 m 2 plots. Disturbance frequency effects were tested by clipping each treatment zero, one, or multiple times. After two growing seasons, in the wetter field site, seedlings removed plots had the lowest species richness and highest evenness, plots with seedlings from the seed bank were intermediate, and plots with added seed had the highest richness and lowest evenness. In the drier site, only adding seed impacted richness (higher) and evenness (lower). In both sites, the seeds present in the seed bank were over 80% from non-native species. Seedling establishment was quantified along with light, water, and nitrate availability within each seeded plot. In the wetter site, resource levels did not predict seedling numbers, but seedlings were more numerous in more frequently clipped, lighter plots. In the drier site, seedlings were more numerous in less frequently clipped plots which received less light and may have remained moister. Seedling establishment from any source never affected community diversity suggesting that while some seeds establish, reconstructions are primarily maintained by vegetative reproduction. The inconsistent effect of clipping highlights the need for management to adapt to varying precipitation, however, given the non-native dominated seed banks, any management intended to increase seedling establishment could result in increased non-native cover.
Jones, Naomi Elizabeth. "Temporal and spatial variation of the vegetation seed bank and seed-rain in set-aside and adjacent habitats". Thesis, University of Aberdeen, 1995. http://digitool.abdn.ac.uk/R?func=search-advanced-go&find_code1=WSN&request1=AAIU068101.
Testo completoWelling, P. (Pirjo). "Regeneration by seeds and vegetation structure in alpine plant communities, subarctic Finland". Doctoral thesis, University of Oulu, 2002. http://urn.fi/urn:isbn:951426861X.
Testo completoSilva, Carla Antónia Mendes. "Optimização dos testes de germinação para monitorização das colecções de plantas autóctones conservadas em bancos de sementes". Master's thesis, ISA/UTL, 2012. http://hdl.handle.net/10400.5/5364.
Testo completoWith the aim to contribute to the optimization of germination tests to monitor the seed collections of native plants conserved in seed banks, germination percentage, germination rate (T50) and lenght of the germination period (T10-90) were evaluated in 16 species studied on four temperatures 15°C, 20°C, 25ºC and 15º/25 ºC. The species were subject to pre-germination treatments to break dormancy: cold stratification (30 days) at 4°C in Scrophulariaceae and Umbelliferae, mechanical scarification in Malvaceae, and Fabaceae, and thermal scarification (115ºC, 10 min.) in Cistaceae. Seeds were incubated in a photoperiod of 8 hours light/16 hours dark. According to results, the species germinated better for the following pretreatements and temperatures: in Cistaceae (thermal scarification): Tuberaria lignosa at 20°C and Halimium lasianthum to 15º/25ºC; in the Fabaceae (mechanical scarification): Adenocarpus complicatus at 15°C and 20°C, Cytisus villosus at 15°C and Vicia sativa subsp.nigra at 20°C; in Malvaceae (mechanical scarification): Alcea rosea at 20°C, Lavatera arborea and Lavatera cretica at 15°C. Pretreatements did not promote the germination of species of the families Scrophulariaceae and Umbelliferae.
Schelling, Lisa R. "Soil seed banks in mixed oak forests in Southeastern Ohio". Ohio : Ohio University, 2006. http://www.ohiolink.edu/etd/view.cgi?ohiou1141850222.
Testo completoNicol, Jason. "Vegetation dynamics of the Menindee Lakes with reference to the seed bank". Title page, table of contents and summary only, 2004. http://web4.library.adelaide.edu.au/theses/09PH/09phn633.pdf.
Testo completoHoraist, David W. "Estimating Seed Bank Responses to Changing Environmental Conditions in the Louisiana Coastal Zone". Thesis, University of Louisiana at Lafayette, 2016. http://pqdtopen.proquest.com/#viewpdf?dispub=10002484.
Testo completoThe coastal zone of Louisiana is changing due to multiple pressures associated with sea-level rise, subsidence, and the inability of sediment or organic accretion to keep pace. The expected increases in sea level and salinity may affect the distribution of the existing plant communities. In addition, these changes in the environment could lead to shifts in plant community composition. During the summer of 2014, I researched how changes in salinity and water levels may change the establishment of vegetation in Louisiana marshes. Randomly selected Coastwide Reference Monitoring System (CRMS) sites were used to collect vegetation data and soil samples. The collected soil samples from fresh, intermediate, brackish, and saline marsh sites were used in a seed bank study. The seed bank study evaluated the effects of different levels of salinity and flooding on seed germination and species richness. Seed germination was highest in soil samples collected from fresh and intermediate sites when these samples were exposed to low salinity (0.0 ppt) and non-flooded conditions. My study only found 43 seedlings in the 10 ppt treatment of 336 total seed germinations, and only 2 seedlings were found in the 20 ppt salinity treatment. Salinity was the dominant factor governing seed germinations and species richness. I also determined that the parent plants for the species found in my seed bank study were more likely to be found within the study site. However, the species data showed at least one species or genus was not present in either the historical or the field collected data. Therefore, the dispersal distance of some seeds from their parental seed provider could have been several hundred meters.
Prigmore, Deborah Susan. "Ground flora variation and management in Forestry Commission plantations at Thetford, East Anglia". Thesis, University of East Anglia, 1994. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.297049.
Testo completoMaighel, Mahmood [Verfasser]. "Effect of Arbuscular mycorrhizal fungi and biochar on soil seed bank viability / Mahmood Maighel". Berlin : Freie Universität Berlin, 2016. http://d-nb.info/1117028453/34.
Testo completoPessoa, Carla Daniela de Sales. "Soil Seed Bank in a Caatinga area in Regeneration, Center for Desertification IrauÃuba, CearÃ". Universidade Federal do CearÃ, 2008. http://www.teses.ufc.br/tde_busca/arquivo.php?codArquivo=9200.
Testo completoO presente trabalho tem como objetivo conhecer os atributos do banco de sementes no solo e verificar quais desses refletem melhor a regeneraÃÃo da caatinga em Ãreas de desertificaÃÃo. Para tanto, investigou-se o banco de sementes no final da estaÃÃo seca, em uma Ãrea de caatinga em processo de degradaÃÃo/desertificaÃÃo, no municÃpio de IrauÃuba, CearÃ. Foram analisados os atributos densidade, composiÃÃo, diversidade e riqueza de espÃcies e cinÃtica de germinaÃÃo. As coletas foram realizadas em trÃs Ãreas, nas fazendas Formigueiro, Cacimba Salgada I e Cacimba Salgada II. Em cada Ãrea foi amostrado o banco de sementes no solo na parcela experimental (pousio) e na parcela em uso contÃnuo (controle). Cada parcela de cada Ãrea foi subdividida em dezesseis parcelas de 10x10m, das quais foram sorteadas cinco para estudo do banco de sementes no solo. No centro de cada uma das cinco parcelas de 100m2 foi retirada amostra de solo de 0,25m2 de Ãrea. A densidade e a composiÃÃo do banco de sementes no solo foram analisadas atravÃs da tÃcnica de emergÃncia de plÃntulas em casa de vegetaÃÃo. O banco foi composto prioritariamente por terÃfitos. As densidades encontradas foram 592, 1804, 2080 sem/m2 para as parcelas experimentais 1, 2 e 3, respectivamente e 680, 1288 e 1408 sem/m2, para as parcelas controle 1, 2 e 3, respectivamente. No parÃmetro riqueza, foram encontrados iguais valores para as parcelas experimento e controle (8 e 2 para as Ãreas 1 e 2, respectivamente), a Ãrea 3 apresentou maior riqueza na parcela em pousio (15 e 10 para as parcelas controle e experimento, respectivamente). Os valores de equabilidade nas parcelas experimento foram de 0,751, 0,041 e 0,740 para as Ãreas 1, 2 e 3, respectivamente, e de 0,613, 0,054 e 0,603 para as Ãreas 1, 2 e 3 das parcelas controle. Em relaÃÃo à diversidade, os valores para as parcelas experimentais 1, 2 e 3 foram 1,562, 0,028, 2,004, respectivamente, e 1274, 0,038 e 1,388 para as parcelas controle, 1, 2 e 3, respectivamente, o que revela uma maior diversidade nas Ãreas em pousio, com exceÃÃo da Ãrea 2. Os aumentos da diversidade e da densidade demonstram a ocorrÃncia de regeneraÃÃo do componente herbÃceo nas Ãreas em pousio.
The objective of this study is to gather knowledge about the attributes of a seed bank at soil level and to verify which of these attributes reflect the best regeneration of the caatinga in areas of desertification. In order to do that, we investigated the seed bank at the end of the dry season in a area of caatinga suffering the process of degradation/desertification, at the municipality of IrauÃuba, CearÃ. We analysed the attributes of density, composition, diversity and richness of species as well as germination dynamics. The collections were realized in three areas, at Formigueiro, Cacimba Salgada I and Cacimba Salgada II farms. In each area, we sampled a seed bank at soil level in the experimental portion (fallow) and at the continuous use portion (control). Each portion of each area was divided in sixteen portions of 10 x 10 m, from which were drawn five portions for the study of the seed bank at soil level. In the center of each one of the five portions of 100 m2, a soil sample of 0,25 m2 was removed. The density and the composition of the seed bank at the soil level were analysed using the plantule outgrowth in greenhouse. The bank was composed primarily by therophytes. The densities found were 592, 1804, 2080 seeds/m2 for the experimental portions 1, 2 and 3, respectively, and 680, 1288 and 1408 seeds/m2 for the control portions 1, 2 and 3, respectively. Regarding the richness parameter, we found equal values for both the experimental and control portions (8 and 2 for areas 1 and 2, respectively); area 3 presented greater richness in the fallow portion (15 and 10 for the control and experimental portions, respectively). The equability values of the experimental portions were equal to 0,751, 0,041 and 0,740 for areas 1,2 and 3 respectively and of 0,613, 0,054 and 0,603 for areas 1,2 and 3 of the control portions. Regarding diversity, the values for the experimental portions 1, 2 and 3 were 1,562, 0,028 and 2,004, respectively, and 1274, 0,038 and 1,388 for the control portions 1,2 and 3, respectively, which reveals a major diversity for the areas of fallow, with exception of area 2. The raising diversity and density demonstrate the occurrence of regeneration of the herbaceous component in the fallow areas.
Maze, Kristal E. "Seed bank depletion effects on post-fire recruitment of two co-occurring Protea species". Thesis, University of Cape Town, 1993. http://hdl.handle.net/11427/23937.
Testo completoSearle, Allyson B. "Reproductive Success and Soil Seed Bank Characteristics of Astragalus ampullarioides and A. holmgreniorum (Fabaceae): Two Rare Endemics of Southwestern Utah". BYU ScholarsArchive, 2011. https://scholarsarchive.byu.edu/etd/3044.
Testo completoCoulombe, Anne-Marie. "Evaluation of the seed bank content as a predictor of weed infestations in crop fields". Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1997. http://www.collectionscanada.ca/obj/s4/f2/dsk2/ftp04/mq21063.pdf.
Testo completoJarvis, Jessie C. "Function of seed-bank ecology in mid-Atlantic semi-annual and perennial Zostera marina beds". W&M ScholarWorks, 2009. https://scholarworks.wm.edu/etd/1539616708.
Testo completoCamara, Armando Tadeo Rodriguez da [UNESP]. "Armazenamento de sementes pré-germinadas de Inga vera Willd". Universidade Estadual Paulista (UNESP), 2011. http://hdl.handle.net/11449/99770.
Testo completoFundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
Sementes recalcitrantes sempre apresentam dificuldades em seu armazenamento, tornandose um problema para produtores de mudas que muitas vezes não têm como realizar a semeadura logo após a colheita das sementes ou necessitam produzir mudas em diferentes épocas do ano, além de dificultar a conservação de germoplasma. As sementes de ingá, depois de colhidas, perdem sua viabilidade rapidamente, geralmente não ultrapassando 15 dias. As espécies de sementes recalcitrantes normalmente não utilizam bancos de sementes como estratégia de regeneração em condições naturais. Observações ecológicas têm mostrado que é mais comum sua regeneração natural ser por meio de bancos de plântulas. O objetivo do trabalho foi avaliar o armazenamento de sementes pré-germinadas de Inga vera Willd., provenientes de frutos em dois estádios diferentes de maturação, em três condições diferentes de umidade de substrato e em baixa temperatura. Os frutos de Inga vera Willd. colhidos foram separados em duas categorias, de acordo com sua coloração de casca, entre verdes e maduros. Após seu beneficiamento, as sementes foram prégerminadas e armazenadas em substrato sem adição de água (testemunha), com 30 e 60% de umidade sob baixa temperatura (10°C), por um ano. O armazenamento feito a 30 e 60% de umidade mostrou-se com melhor eficiência, tanto para plântulas provenientes de frutos verdes, como as de frutos maduros. Entre os dois tipos de frutos, observou-se que as plântulas obtidas de vagem verde, obtiveram melhor desempenho sob as condições de armazenamento, em relação àquelas obtidas de vagem madura. Podem ser armazenadas por até quatro meses, mantendo 50% de sobrevivência das plântulas do lote, quando o armazenamento é feito sob baixa temperatura (10 ± 5°C) e em substrato com 30 e 60% de umidade. Após um período de armazenamento...
Recalcitrant seeds always present difficulties for storage procedures, becoming a problem for seedling producers that often have no choice to sow them immediately after seed harvest or when they need to produce seedlings through different times by the year. Inga seeds, once harvested, lose quickly their viability, often not exceeding a period of 15 days. Species of recalcitrant seeds do not use seed banks as regeneration strategy into the natural environment. Ecological observations have shown that is common occur their natural regeneration through seedling banks. The objective of this work was to evaluate pregerminated seed storage of Inga vera Willd. from two fruit maturation stages, under different conditions of substrate humidity, and under low temperature. The collected fruits of I. vera 9were splited into two types, according to their color, between unripe and ripe. After the processing of those seeds, they were pre-germinated on substrate and stored in substrate with no water addition (control), 30, and 60% humidity under low temperature (10°C) for a year. The storage made under 30 and 60% humidity showed to be the best for both, seedlings from unripe and ripe fruits. Between two types of fruits, we observed that the seedlings from unripe fruits, presented better performance under storage conditions, when compared to those obtained from mature fruits. They can be stored for until four months, with 50% of seedling survivals when stored under low temperature (10 ± 5°C) and with 30 and 60% of substrate humidity. After a year of seedling storage it was possible to get until 10% of survival... (Complete abstract click electronic access below)
Santos, Sandy Lia dos. "Dinamica de clareiras : comportamento de especies pioneiras e fatores que afetam sua colonização". [s.n.], 2005. http://repositorio.unicamp.br/jspui/handle/REPOSIP/315170.
Testo completoTese (doutorado) - Universidade Estadual de Campinas, Instituto de Biologia
Made available in DSpace on 2018-08-05T07:52:23Z (GMT). No. of bitstreams: 1 Santos_SandyLiados_D.pdf: 2051849 bytes, checksum: 71014a56afed5c101f1117b77209e2cc (MD5) Previous issue date: 2005
Resumo: A Mata Santa Genebra é um fragmento isolado de Floresta Atlântica. Por se encontrar muito próximo a áreas urbanas, seu ecossistema está sujeito ao resultado das ações humanas. Devido a constante formação de clareiras em seu interior a floresta torna-se de fundamental importância para o conhecimento da dinâmica destas clareiras, visando sua preservação. O objetivo deste trabalho foi registrar e analisar alguns fatores que pudessem limitar a presença das espécies pioneiras nas clareiras. Para tanto, dados climáticos como irradiância solar, razão V:VE, temperatura e umidade do solo e do ar e precipitação pluviométrica foram registrados durante as estações seca e chuvosa. Também foram registrados dados sobre o banco e a chuva de sementes, a germinação de sementes, o recrutamento de plântulas, o crescimento e a sobrevivência de espécies pioneiras plantadas nas clareiras da MSG. Três clareiras com áreas aproximadas de 82m², 186m² e 660m² foram estudadas. Os mesmos dados foram observados nas três clareiras. No total, 49 espécies de 23 famílias foram registradas. Destas, 21 espécies estiveram presente no estudo do recrutamento, 35 espécies no estudo sobre o banco de sementes e 36 espécies no estudo sobre a chuva de sementes. As famílias mais representativas nos três estudos foram Asteraceae (27%) e Poaceae (14%). Das 49 espécies identificadas, 49% foram nativas, 27% ruderais, 2% exóticas e 22% não foram classificadas. O hábito herbáceo predominou com 49%, seguido pelo arbóreo (20%), arbustivo (12%) e trepadeiras (6%). A dispersão de 43% das espécies foi por anemocoria, 24% por zoocoria, 12% por autocoria e 21% não foram classificadas. Há uma fase da regeneração das clareiras de florestas tropicais onde as lianas predominam e permanecem por vários anos formando um dossel baixo e bastante fechado. A escassez de árvores nas clareiras se deve provavelmente à proliferação rápida das lianas, que reduzem o crescimento de outras plantas e aumentam a mortalidade de árvores. O manejo das lianas nas clareiras necessita de atenção e cuidados, pois, apesar da presença destas reduzir drasticamente a diversidade de espécies vegetais nas clareiras, sua presença é fundamental para a sobrevivência e equilíbrio ecológico, das espécies de animais que habitam nesta mata. Neste estudo à exposição do solo foi feita através do recuo para as margens das clareiras, da massa vegetal das lianas. O plantio de espécies nativas acelera a recuperação das clareiras e exige poucos cuidados quando realizado na estação chuvosa
Abstract: The Mata Santa Genebra (22°49¿45¿S 47°06¿33¿W) is an isolated fragment of the Atlantic Forest. Due to the constant formation of gaps in the interior of the forest it becomes of fundamental importance the knowledge of the dynamics of these gaps for the preservation of the forest. The objectives of this paper were to record and analyze factors which could limit the presence of pioneer species in the gaps. Then, climatic data such as solar irradiance, red: far-red ratio, air and soil temperatures and humidity were recorded during the dry and rainy season, beside pluviometric precipitation. Data were also recorded on seed bank, seed rain, seed germination, recruitment, growth and survival of pioneer species planted in gaps of the Mata Santa Genebra. Three gaps were studied with areas approximately of 82m², 186m² and 660m². Some observed data were very closed in the three gaps. In the three gaps 49 species were identified from 23 families. From that, 21 species were present in the recruitment, 35 in the seed bank and 36 in the seed rain. The most representative families were Asteraceae (27%) and Poaceae (14%). From the 49 identified species 49% were native, 27% were weed, 2% were exotic and 22% unclassified. Herbs were predominant (49%), followed by trees (20%), shrubs (12%) and lianas (6%). The dispersion of 43% of species was by anemocory, 24% by zoocory and 12% by autocory and 21% unclassified. There is a stage of gap regeneration in Tropical Forest where lianas are predominant and remain for many years as a low dense canopy. The rarity of trees in these gaps is probably due to the fast proliferation of lianas that besides reducing growth of other plants increases mortality of trees. The management of lianas in the gaps needs to be made very cautiously. Although their presence causes drastic reduction in the species diversity in the gaps, their presence is of fundamental importance to survival and ecological equilibrium of animals which live in the forest. In this paper some intervention was done in the gaps, in relation to bare soil by moving aside herbs and lianas. Planting local native species accelerates the recovery of gaps and do not require much attention when done during rainy season
Doutorado
Doutor em Biologia Vegetal
Osei, Nana Akwasi. "Large wood in fluvial systems : quantity, structure and landforms, sediment retention, and riparian seed bank development". Thesis, Queen Mary, University of London, 2014. http://qmro.qmul.ac.uk/xmlui/handle/123456789/8813.
Testo completoNave, André Gustavo. "Banco de sementes autóctone e alóctone, resgate de plantas e plantio de vegetação nativa na fazenda Intermontes, município de Ribeirão Grande, SP". Universidade de São Paulo, 2005. http://www.teses.usp.br/teses/disponiveis/11/11150/tde-02062005-153506/.
Testo completoSignificant accumulation of know-how about restoration ecology has been changing forest restoration management programs trends during the last years. Choosing or elaborating a restoration model is a process that requires constant improvement and ecological studies that not only reduces the costs involved but also warrants the achievement of the aimed proposal. This study explores new restoration methodologies, searching for technical information about: A) autochthonous and allochthonous seed bank expression on forest restoration at different situations degraded by anthropogenic disturbances; B) seedlings and woody growing individuals rescue; C) efficiency of a planting model based on fulfillment and diversity concept; D) landscape development. The autochthonous and allochthonous seed bank were analyzed through regenerating woody species and density scouting. For the rescue of regenerating woody species, seedling and young individuals were taken from a forest and transferred to a plant nursery for adjustment, where number and species were counted regarding density and survival. In this studied planting model, species were organized and gathered into a fulfillment or diversity group, and each individual had its crown area quantified. Landscape development was analyzed by photointerpretation and specially by periodical field checking. Results from these methodologies showed that: A) Identified degraded situations at Intermontes farm displayed distinguished natural regeneration expression, influenced by the number of germinated seeds of the autochthonous seed bank. Advantage can be taken from these different outcomes by using distinct restoration methodologies for each studied situation. B) For the autochthonous seed bank study, germinated seed density was 409,334 ind./ha, indicating its potential role on restoration programs. Woody individuals at fertilized sites had a medium height enhancement of 137,7% when compared to those at non fertilized sites. C) For seedlings and woody growing individuals rescue, individual density was similar for both seasons (38700ind./ha and 37900ind./ha) but significantly distinct for individual survivor, with values of 16500ind./ha for July and 2600ind./ha for December. Rescue technique turned out to be a viable possibility since it achieved survival of 70,9% for rescued individuals. D) This planting model study registered 143 species, indicating that the diversity groups role has been maintained and enhances the chance of successional process success. The fulfilling group had a significant higher percentage of crown area than the diversity group, with 73,6% and 83,3% for 1,5 and 2,5 years, respectively.
Bobowski, Benny R. "Identification of Belowground Woody Structures Using Molecular Biomarkers". DigitalCommons@USU, 1997. https://digitalcommons.usu.edu/etd/6540.
Testo completoKlein, Débora Kestring [UNESP]. "Ecologia do banco de sementes de trecho de floresta estacional semidecidual e germinação de sementes de Peltophorum dubium (Sprenge) Taubert (Fabaceae: Caesalpinioidea) em diferentes condições de alagamento". Universidade Estadual Paulista (UNESP), 2011. http://hdl.handle.net/11449/104005.
Testo completoPara um melhor entendimento dos processos que determinam a dinâmica das florestas tropicais, estudos que investigam tanto a vegetação (parte aérea) como o banco de sementes do solo, são necessários. Através de estudos de banco de semente pode-se avaliar, por exemplo, a capacidade de regeneração natural de uma dada vegetação, a viabilidade das sementes existentes no solo e sua influência na estrutura da vegetação. No entanto, pouco se sabe sobre os processos que podem provocar variações na estrutura do banco de sementes, especialmente em florestas semideciduais. O presente estudo teve como objetivo conhecer a composição do banco de sementes do solo em um trecho de Floresta Estacional Semidecídual, bem como investigar possíveis processos capazes de gerar variações em sua estrutura. Além disso, determinou-se o grau de similaridade entre a parte aérea e o banco de sementes. Primeiramente, a densidade (número de plântulas), a riqueza, a diversidade e a composição de espécies foram comparadas entre áreas em diferentes estágios sucessionais, bem como entre diferentes profundidades do solo e estações do ano (chuvosa e seca). Em seguida, a similaridade entre o banco de sementes e a vegetação local foi comparada. Constatou-se que a principal fonte de variação do número de plântulas, da riqueza e da diversidade de espécies presentes no banco de sementes foi a profundidade na qual as sementes foram amostradas. De forma geral, as amostras obtidas da serrapilheira continham, significativamente, um maior número de plântulas, uma maior riqueza e maior diversidade de espécies do que as amostras provenientes das profundidades de 0-10cm e 10-20cm, tanto na estação chuvosa como seca. Comparações da riqueza e da diversidade de espécies entre a estação seca e chuvosa...
For a better understanding of the processes that determine tropical forest dynamics, studies that investigate vegetation both above and below ground are needed. By studying seed banks it is possible to determine, for example, the natural regeneration capacity of vegetation, the viability of the soil seed bank as well as its influence at structuring plant communities. However, little is known about the processes that can generate variation in the seed bank structure, particularly in semideciduous forests. The main aim of this study was to know the soil seed bank composition in a semideciduous seasonal forest fragment, and also to investigate some processes that may generate variations in this structure. Besides, it was determined below (seed bank) and above ground (vegetation) similarity. Firstly, the density (seedling numbers), the richness, and the diversity and species composition were compared among areas of different sucessional stages, and among different soil depths and season (rainy and dry season). After that, the similarity between the soil seed bank and local vegetation was compared. It was observed that the main source of variation of seedling numbers, richness, and species diversity was the depth at which seed samples were obtained. In overall, samples from the litterfall had significantly higher seedling numbers, species richness and diversity than the other depths (0-10cm and 10-20cm); this difference occurred at both in the rainy and dry season. Comparisons of species richness and diversity between the rainy and dry season showed that both significantly differed between seasons, and higher values were observed in the rainy season. Seedling numbers did not differ between seasons. Species composition was more similar between pairs of samples from depths near to each other; for example, for both seasons... (Complete abstract click electronic access below)
Auffret, Alistair G. "Seed mobility and connectivity in changing rural landscapes". Doctoral thesis, Stockholms universitet, Institutionen för naturgeografi och kvartärgeologi (INK), 2013. http://urn.kb.se/resolve?urn=urn:nbn:se:su:diva-89105.
Testo completoAt the time of the doctoral defense, the following papers were unpublished and had a status as follows: Paper 3: Accepted. Paper 4: In press. Paper 5: Manuscript.
Klein, Débora Kestring. "Ecologia do banco de sementes de trecho de floresta estacional semidecidual e germinação de sementes de Peltophorum dubium (Sprenge) Taubert (Fabaceae: Caesalpinioidea) em diferentes condições de alagamento /". Botucatu : [s.n.], 2011. http://hdl.handle.net/11449/104005.
Testo completoCoorientador: Renata Cristina Batista Fonseca
Coorientador: Vera Lex Engel
Banca: Maria Tereza Grombone Guaratini
Banca: Wesley Augusto Conde Godoy
Banca: Rita de Cássia S. Maimoni Rodella
Banca: João Nakagawa
Resumo: Para um melhor entendimento dos processos que determinam a dinâmica das florestas tropicais, estudos que investigam tanto a vegetação (parte aérea) como o banco de sementes do solo, são necessários. Através de estudos de banco de semente pode-se avaliar, por exemplo, a capacidade de regeneração natural de uma dada vegetação, a viabilidade das sementes existentes no solo e sua influência na estrutura da vegetação. No entanto, pouco se sabe sobre os processos que podem provocar variações na estrutura do banco de sementes, especialmente em florestas semideciduais. O presente estudo teve como objetivo conhecer a composição do banco de sementes do solo em um trecho de Floresta Estacional Semidecídual, bem como investigar possíveis processos capazes de gerar variações em sua estrutura. Além disso, determinou-se o grau de similaridade entre a parte aérea e o banco de sementes. Primeiramente, a densidade (número de plântulas), a riqueza, a diversidade e a composição de espécies foram comparadas entre áreas em diferentes estágios sucessionais, bem como entre diferentes profundidades do solo e estações do ano (chuvosa e seca). Em seguida, a similaridade entre o banco de sementes e a vegetação local foi comparada. Constatou-se que a principal fonte de variação do número de plântulas, da riqueza e da diversidade de espécies presentes no banco de sementes foi a profundidade na qual as sementes foram amostradas. De forma geral, as amostras obtidas da serrapilheira continham, significativamente, um maior número de plântulas, uma maior riqueza e maior diversidade de espécies do que as amostras provenientes das profundidades de 0-10cm e 10-20cm, tanto na estação chuvosa como seca. Comparações da riqueza e da diversidade de espécies entre a estação seca e chuvosa... (Resumo completo, clicar acesso eletrônico abaixo)
Abstract: For a better understanding of the processes that determine tropical forest dynamics, studies that investigate vegetation both above and below ground are needed. By studying seed banks it is possible to determine, for example, the natural regeneration capacity of vegetation, the viability of the soil seed bank as well as its influence at structuring plant communities. However, little is known about the processes that can generate variation in the seed bank structure, particularly in semideciduous forests. The main aim of this study was to know the soil seed bank composition in a semideciduous seasonal forest fragment, and also to investigate some processes that may generate variations in this structure. Besides, it was determined below (seed bank) and above ground (vegetation) similarity. Firstly, the density (seedling numbers), the richness, and the diversity and species composition were compared among areas of different sucessional stages, and among different soil depths and season (rainy and dry season). After that, the similarity between the soil seed bank and local vegetation was compared. It was observed that the main source of variation of seedling numbers, richness, and species diversity was the depth at which seed samples were obtained. In overall, samples from the litterfall had significantly higher seedling numbers, species richness and diversity than the other depths (0-10cm and 10-20cm); this difference occurred at both in the rainy and dry season. Comparisons of species richness and diversity between the rainy and dry season showed that both significantly differed between seasons, and higher values were observed in the rainy season. Seedling numbers did not differ between seasons. Species composition was more similar between pairs of samples from depths near to each other; for example, for both seasons... (Complete abstract click electronic access below)
Doutor
Navarra, Jennifer J. "Species composition and spatiotemporal pattern of the seed bank and vegetation in native and degraded Florida rosemary scrub". Master's thesis, University of Central Florida, 2010. http://digital.library.ucf.edu/cdm/ref/collection/ETD/id/4645.
Testo completoID: 028917091; System requirements: World Wide Web browser and PDF reader.; Mode of access: World Wide Web.; Thesis (M.S.)--University of Central Florida, 2010.; Includes bibliographical references (p. 108-123).
M.S.
Masters
Department of Biology
Sciences
Delong, Michael. "Metapopulations and metacommunities in dry forest openings in southern Illinois". OpenSIUC, 2009. https://opensiuc.lib.siu.edu/dissertations/90.
Testo completoKalk, Hannah June. "The role of coastal plant community response to climate change: implications for restoring ecosystem resiliency". OpenSIUC, 2011. https://opensiuc.lib.siu.edu/theses/742.
Testo completoSANTOS, Danielle Melo dos. "Variação espacial na dinâmica do banco de sementes em uma área de caatinga em Pernambuco durante três anos consecutivos". Universidade Federal Rural de Pernambuco, 2010. http://www.tede2.ufrpe.br:8080/tede2/handle/tede2/4755.
Testo completoMade available in DSpace on 2016-06-15T14:25:03Z (GMT). No. of bitstreams: 1 Danielle Melo dos Santos.pdf: 428920 bytes, checksum: 322bb464473f572f27942b042957d2dc (MD5) Previous issue date: 2010-06-15
Conselho Nacional de Pesquisa e Desenvolvimento Científico e Tecnológico - CNPq
Space-time heterogeneity that occurs in dry forests changes seedling emergence rates and habitat’s species richness by influencing soil seed bank density. Therefore, considering the importance of understanding how these space-time variations influence seed bank dynamics in an area of caatinga, this study aims to answer the following questions: 1. Do soil bank species richness and seed density differ according to the microhabitat type and annual precipitation totals? 2. Is there an interaction between annual precipitation totals and microhabitat types in determining soil bank species richness and seed density? The study was performed in a fragment of caatinga in Caruaru-PE. Three microhabitat types are easily found in the study area. The riparian corresponds to the terrain zone with a smooth inclination on the margins of Olaria stream, not considering the part of the stream bed where water runs during high precipitation periods; the flat microhabitat corresponds to the somewhat flat terrains, with no significant elevations and up to 150 m distant from the stream bed margins; the rocky microhabitat corresponds to the places with small rock outcrops, within an area varying from 2 to 5 m², which occur as distinct patches dispersed in the flat microhabitat. In the interior of the study area there are 105 1 x 1 m randomly placed parcels for the study of herbaceous vegetation, 35 in each microhabitat. Soil was collected around the 1x 1m parcels (35 samples for each microhabitat) in a 5 cm depth considering litter. These collections were performed in the end of rainy and dry seasons during three consecutive years (2006, 2007 and 2008), summing 630 samples. Differences in log-transformed data of species richness and seedling emergence in the soil bank between years and microhabitats were evaluated with a two-way ANOVA, with a 5% probability and using Turkey as a posteriori test. During the three years of the study, a total of 79 species emerged from the soil bank, 63 species in the riparian microhabitat, 43 in the flat one and 42 in the rocky microhabitat. There was a significant difference for both average species richness and average seedling emergence between microhabitats and between monitoring years, with a significant interaction between them. The influence of microhabitat and annual precipitation on the soil bank species richness and seed density was not the same, or at least did not act with the same intensity, since while precipitation explained 48% of soil bank species richness, microhabitat only explained 7%. Regarding seed density, the opposite was recorded, since while microhabitat explained 31% of seedling emergence, precipitation only accounted for 5%. The results of this study showed that, in order to better understand seed bank dynamics of semi-arid environments, it is also necessary to consider variations inducted by microhabitat conditions, which help for a better adjusting of predictions about seed availability in the soil bank for population renewal and conservation of these environments.
A heterogeneidade espaço-temporal que ocorre nas florestas tropicais secas, altera a taxa de emergência de plântulas e a riqueza de espécies dos habitats por influenciar a densidade do banco de sementes do solo. Deste modo, considerando a importância de se entender como estas variações espaço-temporal vão influenciar a dinâmica do banco de sementes de uma área de caatinga, este estudo objetiva responder as seguintes perguntas: 1. A riqueza de espécies e a densidade de sementes no banco do solo diferem em relação ao tipo de microhabitat e os totais de precipitação de cada ano? 2. Existe interação entre os totais de precipitação anuais e os tipos de microhabitats na determinação da riqueza de espécies e densidade de sementes do banco do solo? O estudo foi realizado em um fragmento de caatinga, em Caruaru, PE. Na área de estudo, três tipos de microhabitats são facilmente visualizados, o ciliar corresponde à faixa de terreno com inclinação suave às margens do riacho Olaria, sem considerar a parte do leito onde corre água do riacho na época de maior precipitação; o microhabitat plano corresponde aos terrenos razoavelmente planos, sem maiores elevações e que distam até 150 m das margens do leito do Riacho; o rochoso corresponde aos locais com pequenos afloramentos rochosos, com área variando de 2 a 5 m2 e altura 0,1 a 1 m, que ocorrem como manchas distintas dispersas no microhabitat plano. No interior da área estudada existem aleatoriamente alocadas 105 parcelas de 1x1 m para o estudo da vegetação herbácea, sendo 35 em cada microhabitat. O solo foi coletado no entorno das parcelas de 1x1 m (35 amostras em cada microhabitat), a 5 cm de profundidade e considerando a serrapilheira. Estas coletas foram realizadas nos finais das estações chuvosas e secas, durante três anos consecutivos (2006, 2007 e 2008), totalizando 630 amostras. Diferenças nos dados logaritmizados de riqueza de espécies e de emergência de plântulas do banco do solo entre anos e microhabitats foram avaliadas através de uma Anova-two way, a 5% de probabilidade com teste a posteriori de Tukey. Durante os três anos de estudos, um total de 79 espécies emergiu do banco do solo, sendo 63 espécies no microhabitat ciliar, 43 no plano e 42 no rochoso. Houve diferença significativa tanto na riqueza média de espécies bem como na emergência média de plântulas entre microhabitats e entre anos de monitoramento, com interação significativa entre os mesmos. A influência do microhabitat e da precipitação anual sobre a riqueza de espécies e a densidade de sementes do banco do solo não foi à mesma, ou pelo menos não atuou na mesma intensidade, pois enquanto a precipitação explicou 48% da riqueza de espécies do banco do solo, microhabitat explicou apenas 7%. Já em relação à densidade de sementes, o inverso foi registrado, pois enquanto microhabitat explicou 31% da emergência de plântulas, precipitação explicou apenas 5%. Por fim, os resultados deste estudo mostram que para compreender bem a dinâmica do banco de sementes de ambientes semi-áridos torna-se necessário também considerar as variações induzidas pelas condições de microhabitats, as quais possibilitam ajustar melhor as predições sobre a disponibilidade de sementes no banco solo para renovação das populações e conservação destes ambientes.
Hacker, Molly. "ASSESSING SEED BANK CONTRIBUTION TO LANDWARD EXPANSION OF COASTAL WETLAND COMMUNITIES AND RESPONSES TO FIRE AND TRANSLOCATION ALONG COENOCLINE". OpenSIUC, 2018. https://opensiuc.lib.siu.edu/theses/2332.
Testo completoCamara, Armando Tadeo Rodriguez da 1985. "Armazenamento de sementes pré-germinadas de Inga vera Willd. /". Botucatu : [s.n.], 2011. http://hdl.handle.net/11449/99770.
Testo completoBanca: Marcia Balistiero Figliolia
Banca: Edvaldo Aparecido Amaral da Silva
Resumo: Sementes recalcitrantes sempre apresentam dificuldades em seu armazenamento, tornandose um problema para produtores de mudas que muitas vezes não têm como realizar a semeadura logo após a colheita das sementes ou necessitam produzir mudas em diferentes épocas do ano, além de dificultar a conservação de germoplasma. As sementes de ingá, depois de colhidas, perdem sua viabilidade rapidamente, geralmente não ultrapassando 15 dias. As espécies de sementes recalcitrantes normalmente não utilizam bancos de sementes como estratégia de regeneração em condições naturais. Observações ecológicas têm mostrado que é mais comum sua regeneração natural ser por meio de bancos de plântulas. O objetivo do trabalho foi avaliar o armazenamento de sementes pré-germinadas de Inga vera Willd., provenientes de frutos em dois estádios diferentes de maturação, em três condições diferentes de umidade de substrato e em baixa temperatura. Os frutos de Inga vera Willd. colhidos foram separados em duas categorias, de acordo com sua coloração de casca, entre verdes e maduros. Após seu beneficiamento, as sementes foram prégerminadas e armazenadas em substrato sem adição de água (testemunha), com 30 e 60% de umidade sob baixa temperatura (10°C), por um ano. O armazenamento feito a 30 e 60% de umidade mostrou-se com melhor eficiência, tanto para plântulas provenientes de frutos verdes, como as de frutos maduros. Entre os dois tipos de frutos, observou-se que as plântulas obtidas de vagem verde, obtiveram melhor desempenho sob as condições de armazenamento, em relação àquelas obtidas de vagem madura. Podem ser armazenadas por até quatro meses, mantendo 50% de sobrevivência das plântulas do lote, quando o armazenamento é feito sob baixa temperatura (10 ± 5°C) e em substrato com 30 e 60% de umidade. Após um período de armazenamento... (Resumo completo, clicar acesso eletrônico abaixo)
Abstract: Recalcitrant seeds always present difficulties for storage procedures, becoming a problem for seedling producers that often have no choice to sow them immediately after seed harvest or when they need to produce seedlings through different times by the year. Inga seeds, once harvested, lose quickly their viability, often not exceeding a period of 15 days. Species of recalcitrant seeds do not use seed banks as regeneration strategy into the natural environment. Ecological observations have shown that is common occur their natural regeneration through seedling banks. The objective of this work was to evaluate pregerminated seed storage of Inga vera Willd. from two fruit maturation stages, under different conditions of substrate humidity, and under low temperature. The collected fruits of I. vera 9were splited into two types, according to their color, between unripe and ripe. After the processing of those seeds, they were pre-germinated on substrate and stored in substrate with no water addition (control), 30, and 60% humidity under low temperature (10°C) for a year. The storage made under 30 and 60% humidity showed to be the best for both, seedlings from unripe and ripe fruits. Between two types of fruits, we observed that the seedlings from unripe fruits, presented better performance under storage conditions, when compared to those obtained from mature fruits. They can be stored for until four months, with 50% of seedling survivals when stored under low temperature (10 ± 5°C) and with 30 and 60% of substrate humidity. After a year of seedling storage it was possible to get until 10% of survival... (Complete abstract click electronic access below)
Mestre
Postma, Froukje M. "Selection during Early Life Stages and Local Adaptation in Arabidopsis thaliana". Doctoral thesis, Uppsala universitet, Växtekologi och evolution, 2016. http://urn.kb.se/resolve?urn=urn:nbn:se:uu:diva-302862.
Testo completoVanderWeide, Benjamin Lee. "Grazing and drought in tallgrass prairie: the role of belowground bud banks in vegetation dynamics". Diss., Kansas State University, 2013. http://hdl.handle.net/2097/16622.
Testo completoDepartment of Biology
David C. Hartnett
Grazing and drought are instrumental in the development and maintenance of perennial grasslands. In this research I tested the belowground bud bank contribution to tallgrass prairie resistance and resilience when perturbed by grazing and drought. First, I tested the bud bank role in vegetation response to and recovery from severe drought (Chapter 2). I compared above- and belowground responses of experimentally droughted plots to ambient controls and irrigated plots during two years of severe drought and two years of recovery. I found that although aboveground net primary productivity declined 30-60% during drought, bud bank density and demography were insensitive to drought. These results suggest that grassland resistance and resilience when perturbed by drought may be mediated by stability of belowground bud banks. Second, I investigated vegetation and soil nutrient legacies following release from long-term grazing (Chapter 3). I documented a relatively rapid shift in aboveground vegetation within four years of grazer exclusion, with productivity, stem density, and diversity becoming relatively more similar to ungrazed than grazed prairie. The density and composition of the belowground bud bank and soil seed bank shifted more slowly, remaining more similar to grazed than ungrazed prairie. Responses of soil nutrients to removal of grazers varied, and in some cases was affected by recent fire history. These results demonstrate the contribution of belowground propagules to the maintenance of a diverse plant community both during grazing and after grazers are removed. Finally, I examined short-term vegetation responses to both drought and grazing (Chapter 4). Despite extreme drought and simulated grazing that reduced productivity and increased mortality of individual stems, the dominant C4 grasses maintained a stable bud bank. Aboveground net primary productivity and bud bank density of sedges and forbs, however, were reduced by both drought and grazing. This differential response of species to extreme drought and grazing led to shifts in community composition and species diversity over one growing season. Across drought and grazing treatments, live rhizome biomass was highly correlated with bud bank density and may be a useful, more easily measured index of bud bank density.
Nielsen, Michele Erin. "Seed and seedling dynamics of the seagrass, Zostera japonica Aschers. and Graebn. and the influence of Zostera marina L". Thesis, University of British Columbia, 1990. http://hdl.handle.net/2429/30172.
Testo completoScience, Faculty of
Botany, Department of
Graduate
McCue, Kimberlie A. "The ecological genetics of rarity : a study of genetic structure, inbreeding and seed bank dynamics in a rare annual plant /". free to MU campus, to others for purchase, 1997. http://wwwlib.umi.com/cr/mo/fullcit?p9841324.
Testo completoFowers, Beth. "Ecologically-Based Manipulation Practices for Managing Bromus tectorum-infested Rangelands". DigitalCommons@USU, 2011. https://digitalcommons.usu.edu/etd/1019.
Testo completoTilini, Kassie Lorraine. "The Seed Ecology of Rare and Endangered Gibbens' Beardtongue (Penstemon gibbensii) and Blowout Penstemon (Penstemon haydenii)". BYU ScholarsArchive, 2013. https://scholarsarchive.byu.edu/etd/4065.
Testo completoKeammerer, Holly Barton 1983. "Community structure, plant interactions, seedling performance and seed bank composition of salt marshes along an estuarine gradient in Coos Bay, Oregon". Thesis, University of Oregon, 2011. http://hdl.handle.net/1794/11256.
Testo completoSalt marshes are intertidal communities dominated by halophytic vascular plants that are subjected periodically to tidal inundation. These species have developed various adaptations to this stress, including tolerances of fluctuating salinity, extended periods of inundation and intervals of anoxic conditions. The marshes are divided into zones of different plant communities based on species' tolerances of ambient estuarine conditions. Abiotic stresses change along the estuarine salinity gradient (marine to riverine), potentially altering development and composition of plant communities. Abiotic gradients associated with tides are not the only factors that contribute to development of plant community composition in salt marshes. Both negative (competition) and positive (facilitation) biological interactions are also important. Factors that influence community structure in salt marshes, particularly on the eastern North American seaboard, have been well studied. In contrast, salt marshes along the Oregon coast are smaller and more discrete and have received comparatively little attention. The community structure and seed bank composition of six marshes along an estuarine salinity gradient were evaluated. Four major community types dominated marshes that varied in the salinity of inundating tidal waters. Community types were relatively consistent throughout the estuary despite the distances between the marshes. Unlike the emergent plant communities, marsh seed bank composition was more similar within a marsh than within a community type. The low and high marsh community types were separated by a distinct boundary in the marine marshes. Although abiotic factors influence the physical separation of communities, competitive interactions commonly determine the upper limit of a species. In Metcalf marsh, however, the upper boundary for two dominant low marsh species was not determined by competition with the high marsh dominant species. Positive biotic interactions between seedlings and existing vegetation in a community are important factors in determining species distributions, particularly in stressful estuarine environments. In salt marshes, where abiotic stress can be harsh, presence of existing vegetation can ameliorate these conditions and enhance germination and seedling establishment. However, interaction between seedlings and the emergent marsh community was highly competitive, though germination of one species was enhanced in the presence of existing vegetation. This dissertation includes un-published co-authored material.
Committee in charge: Dr. Scott Bridgham, Chairperson; Dr. Richard Emlet, Advisor; Dr. Steven Rumrill, Member; Dr. Alan Shanks, Member; Dr. Gregory Retallack Outside Member
Andrade, Greice Kelly Oliveira. "Avaliação da regeneração natural em áreas de reflorestamento, no município de Laranjeiras-SE". Universidade Federal de Sergipe, 2015. https://ri.ufs.br/handle/riufs/3004.
Testo completoMany researches have been focused on reforestation projects, taking advantages on the self recuperation mechanism of the frorest such as seed rain, soil seed bank and seedling banks. Seed rain is an initial process which develops the dynamic, organization and structuration of the forest. However, the seed bank is one of the most important factors for natural recolonization of affected areas which start the succession process. Through this natural regeneration, a set of individuals are able to be recruited to the upper stages. In this way, the present study was performed aiming to evaluate the plant species establishment strategies through natural regeneration, in an area in the city of Laranjeiras-SE. Thirty plots were installed, and in center of these plots, collectors were installed (1m x 1m) to estimate the seed rain. To characterize the seed bank, was collected from August 2014 (corresponding to the rainy season in the region) to February 2015 (dry season), a soil sample from the center of each subplot (1m x 1m) through a metal jig which was introduced into the soil to remove a 5 cm layer. In the seedling bank evaluation, height and diameter of seedlings were analyzed between August 2014 (rainy season) and Februare 2015 (dry season) in subplots (1m x 1m). In seed rain were found 7,788 seeds, in which Shinus terebinthifollius Raddi (aroeira) presented a higher number of seeds collected with 6,799 samples and its frequency was 87.84% in relation with others species. The autochoric syndrome of dispersion was observed to Centrosema brasilianum (L.) Benth., Fabaceae 2 and Anadenanthera colubrina (Vell.) Brenan, for Asteraceae 1 and Bignoniaceae 1 the dispersion syndrome observed was anemocoric and to Schinus terebinthifollius and Passiflora mansoi (Mart.) Mast, the dispersion syndrome was zoochoric. In the study of seed bank, it was found a total of 171 seeds. The seed bank analyzes by the rainy season and dry season, Schinus terebinthifollius prevailed with more individuals in the rainy season. However, Fabaceae sp prevailed in the dry season. The distribution of species per plot was heterogeneous in both seasons, but presented a better distribution in the rainy season. In the study of seedlings bank, samples were found belonging to seven families and thirteen species. Shinus terebinthifollius represented 28% of total specimen, followed by Genipa Americana L. with 20%. The rainy season showed better seedling distribution along the plots. The processes of natural regeneration at studied area have presented a diversity of species into three regeneration kinds evaluated in different fructification seasons, establishing int this way, a steady supply of seeds, enabling the development of new individuals for future process.
Inúmeras pesquisas têm sido voltadas a projetos de reflorestamentos, aproveitando o próprio mecanismo de recuperação da floresta como chuvas de sementes, bancos de sementes do solo e bancos de plântulas. A chuva de sementes é um processo inicial que desenvolve a dinâmica, organização e estruturação da floresta. No entanto, o banco de sementes é um dos fatores mais importantes para a recolonização natural das áreas afetadas dando início ao processo sucessional. Por meio dessa regeneração natural, um conjunto de indivíduos são capazes de ser recrutados para os estádios superiores. Dessa forma, o presente trabalho foi realizado objetivando avaliar as estratégias de estabelecimentos das espécies vegetais por meio da regeneração natural, numa área em reflorestamento, no município de Laranjeiras-SE. Foram instaladas 30 parcelas, e no centro dessas parcelas foram instalados coletores (1m x 1m) para estimar a chuva de sementes. Para a caracterização do banco de sementes, foi coletada, no mês de agosto de 2014 (correspondente a estação chuvosa na região) e fevereiro de 2015 (estação seca), uma amostra de solo no centro de cada subparcela (1m x 1m), através de um gabarito metálico que foi introduzido no solo para remover uma camada de 5 cm. Na avaliação do banco de plântulas, foram realizadas análises de altura e diâmetro das plântulas, entre agosto de 2014 (estação chuvosa) a fevereiro de 2015 (estação seca), em subparcelas (1m x 1m). Na chuva de sementes foram encontradas 7.788 sementes, dentre as quais a espécie Schinus terebinthifollius Raddi (aroeira) apresentou maior número de sementes coletadas, com 6.799 amostras possuindo frequência de 87,84% em relação as outras espécies. A síndrome de dispersão autocórica foi observada para as espécies Centrosema brasilianum (L.) Benth., Fabaceae 2 e Anadenanthera colubrina (Vell.) Brenan, para Asteraceae 1 e Bignoniaceae 1 a síndrome de dispersão observada foi anemocorórica e para as espécies Schinus terebinthifollius e Passiflora mansoi (Mart.) Mast, a síndrome de dispersão presente foi a zoocórica. No estudo do banco de sementes, foi encontrado um total de 171 sementes. Nas análises por estação chuvosa e seca do banco de sementes, a espécie Schinus terebinthifollius prevaleceu com maior número de indivíduos na estação chuvosa. Contudo, prevaleceu a espécie Fabaceae 1 na estação seca. A distribuição das espécies por parcela foi heterogênea em ambas as estações, porém apresentou uma melhor distribuição no período chuvoso. No estudo do banco de plântulas, foram encontradas amostras pertencentes a sete famílias e treze espécies. A espécie Schinus terebinthifollius representou 28% dos espécimes amostrados, seguida por Genipa americana L. com 20%. Na estação chuvosa houve uma melhor distribuição de plântulas ao longo das parcelas. O processo de regeneração natural da área de estudo apresentou uma diversidade de espécies nas três formas de regeneração avaliadas com diferentes épocas de frutificação, estabelecendo assim, uma constante oferta de sementes, viabilizando o desenvolvimento de novos indivíduos para processos futuros.