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Pizarro, Roberto, Carolina Morales, Pablo Garcia-Chevesich, Peter F. Ffolliott, Oscar Vallejosa, Leonardo Vega, Rodrigo Valdes, Claudio Olivares i Francisco Balocchi. "Soil Erosion in Arid and Semi-Arid Climates of Northern Chile". Arizona-Nevada Academy of Science, 2011. http://hdl.handle.net/10150/296986.
Pełny tekst źródłaPopp, Alexander. "An integrated modelling approach for sustainable management of semi-arid and arid rangelands". Phd thesis, kostenfrei, 2007. http://opus.kobv.de/ubp/volltexte/2007/1510/.
Pełny tekst źródłaBaker, Malchus B. Jr, Barbara Hutchinson, Eric Pfirman, Michael Haseltine i Jeffrey Schalau. "Management of Arid and Semi-Arid Watersheds: Decision-Making Tools and Technology Transfer". Arizona-Nevada Academy of Science, 2001. http://hdl.handle.net/10150/296558.
Pełny tekst źródłaZanchetta, Anna <1982>. "Remote Sensing Techniques for Change Detection Analysis in Arid and Semi-arid areas". Doctoral thesis, Alma Mater Studiorum - Università di Bologna, 2017. http://amsdottorato.unibo.it/8134/1/ZANCHETTAAnna_PhDThesis.pdf.
Pełny tekst źródła夏江瀛 i Kong-ying Ha. "Microbial ecology of arid environments". Thesis, The University of Hong Kong (Pokfulam, Hong Kong), 2013. http://hdl.handle.net/10722/193421.
Pełny tekst źródłapublished_or_final_version
Biological Sciences
Doctoral
Doctor of Philosophy
Cluff, C. Brent. "Water Harvesting in Arid Lands". Water Resources Research Center. The University of Arizona, 1987. http://hdl.handle.net/10150/306468.
Pełny tekst źródłaThe use of water harvesting systems in arid lands offers the potential of making lands productive that are now largely unusable due to lack of water for domestic livestock or agricultural use. As long as there is rainfall a water harvesting system can be designed to collect that rainfall and store it until it can be used for beneficial use. The water harvesting system consists of a catchment and a storage facility. If the water is to be used for agriculture it would also include an agricultural area. The agricultural area could be located within the catchment area or in a separate nearby area. Many different treatments have been tested for use in catchment construction. These treatments increase the runoff by decreasing the permeability of the surface and or reducing the time the water stays on the surface or amount of water trapped on the surface. A list of the more promising treatments in order of their increasing cost, are: (1) Shaped compacted-earth; (2) sodium-treated shaped compacted-earth; (3) wax-treated shaped compacted-earth; (4) gravel-covered plastic; (5) fiberglass-asphalt chipcoated; (6) asphalt-plastic-asphalt chipcoated; (7) rubberized-asphalt chipcoated; and (8) reinforced-mortar-covered plastic. The use of compartmented reservoirs make storage of water more efficient. Evaporation and in some cases seepage losses are reduced using the compartmented reservoir by keeping the water concentrated into a volume with as small a surface area as possible. This method of storage when combined with the collection of runoff from a natural surface or with one that is inexpensively treated makes it practical to provide water for supplemental irrigation. This combination is called a water harvesting agrisystem. Concentration of water in a compartmented reservoir can be accomplished in flat terrain using a pump. If the water is being used at a fast enough rate concentration can also be accomplished by selective removal. Alternatively with topography of a sufficient grade, concentration can be accomplished by gravity. Evaporation control on the compartmented reservoir can be improved by placing an evaporation control barrier on the "last" compartment, the one in which water is concentrated and has water in it the longest time. This enhances the value of the evaporation control barrier and increases the dependable water supply. A computer model has been developed to help in the design of the water harvesting systems including agrisystems with compartmented reservoirs. This program fits on portable personal computers and can thus be taken by the designer to a field location to develop an optimum design at a minimum cost. The model can be improved through calibration in a given area as systems are installed and data collected.
Saragadam, Bhaskararao. "design guidelines and maintenance manual for green roofs in the semi-arid and arid regions". Master's thesis, Alma Mater Studiorum - Università di Bologna, 2018.
Znajdź pełny tekst źródłaMitchell, John Talmadge. "A Framework for Development in Rural Arid and Semi-Arid Environments in Africa: The Somalia Case". Diss., Virginia Tech, 2020. http://hdl.handle.net/10919/98224.
Pełny tekst źródłaDoctor of Philosophy
The wars and conflicts of various types in Africa have made the continent poorer and prevented development in many countries. One of the major, and seemingly intractable conflict locations, is Somalia located in the East Horn of Africa (EHA). This research provides an understanding of salient facts in Somalia's 27 years of war by examining culture and key conflict factors. The objective of this assessment is to identify potential culturally acceptable pathways that will lead to business opportunities and development as a means of conflict mitigation. The improvement of job opportunities for youth is viewed as a means to offset the current participation in the ongoing conflict. Somali and non-Somali sources were consulted to identify and verify avenues for economic growth, sustainability, and educational opportunities. Visits to Somalia and Somaliland confirmed that livestock, and related products, are key components for development and job creation. Technologies with potential to improve productive capacity and disrupt existing value chains were also evaluated. Findings from informal discussions and a pilot test of a proposed framework are presented. The framework identifies elements for development of an innovative, disruptive, and scalable business model that facilitates the implementation of renewable energy production. In addition, it targets education for the livestock and agroforestry industries, improving job and business opportunities.
Hussey, Michael Charles. "Surface detection of alkaline ultramafic rocks in semi-arid and arid terrains using spectral geological techniques". Thesis, Open University, 1998. http://oro.open.ac.uk/54178/.
Pełny tekst źródłaBrearley, Darren. "Developing completion criteria for rehabilitation areas on arid and semi-arid mine sites in Western Australia". Thesis, Curtin University, 2003. http://hdl.handle.net/20.500.11937/745.
Pełny tekst źródłaBrearley, Darren. "Developing completion criteria for rehabilitation areas on arid and semi-arid mine sites in Western Australia". Curtin University of Technology, Department of Environmental Biology, 2003. http://espace.library.curtin.edu.au:80/R/?func=dbin-jump-full&object_id=13937.
Pełny tekst źródła5. To provide a better understanding of ecosystem function by investigating the relationship between state factors, interactive controls, and ecosystem processes at rehabilitation and analogue sites; and 6. To develop a methodology for establishing realistic environmental completion criteria at mine sites situated in arid and semi-arid Western Australia. Field trials were established at four mine sites located within three subtly different bioclimatic zones that extend through the arid / semi-arid shrubland belt of Western Australia; Northeastern Goldfields (Granny Smith Gold Mine, Sunrise Dam Gold Mine), Eastern Goldfields (Black Swan Nickel Mine), and Northeastern Wheatbelt (Westonia Gold Mine). 1 The re-establishment of a self-sustaining vegetation cover integrated with the surrounding ecosystem, was the common end land use objective at the four mine sites selected for this study. For three sites located in the Northeastern Goldfields and Eastern Goldfields of Western Australia, sheep were grazed on surrounding rangeland; the fourth site located in the Northeastern Wheatbelt of Western Australia, and was surrounded by Crown Land. 2 To better understand ecosystem function, the dynamic behaviour and interaction of plant biodiversity parameters was monitored regularly at 19 post-mining rehabilitation sites up to 11 years after direct seeding. For functional ecosystems, plant biodiversity parameters changed rapidly during the initial five years after seeding following predictable trends, after which time they remained within a relatively stable range.
The stabilising of parameters over time was identified as a key indicator of rehabilitation success, however the point at which the parameters stabilised was influenced by numerous variables and was difficult to accurately predict. Prolific seed germination resulted in high seedling density during the initial growing season. Plant density then progressively decreased in response to competition, before stabilising within a range approximately five years after seeding. Revegetation cover was typically low during the first growing season, increasing rapidly there after before also stabilising in line with plant density. Maximum species richness was generally achieved during the first and second year when annual Atriplex species were prominent. Perennial Atriplex species established more slowly during the early stages of revegetation development, but eventually replaced the annual component as the dominant taxa. Perennial Maireana species required up to three years before germinating in the field and establishing themselves in the revegetation; in many cases they replaced perennial Atriplex as the prominent taxa. The presence or absence of cyclonic rainfall during the first growing season was a major determinant of the ecosystem trajectory, controlling revegetation structure and composition. The germination and successful establishment of hard seeded species, including Acacia and Senna, was reliant on heavy summer rainfall during the early stages of ecosystem development to break seed dormancy and extend the length of the first growing season. This provided an important competitive advantage against faster growing Atriplex species, which possessed greater drought tolerance.
The intensity of summer rainfall was also beneficial in leaching surface salts from the upper profile and hence, reducing salinity within the rooting zone. In the absence of heavy summer rainfall during the first growing season, the establishment of a low chenopod dominated vegetation cover was favoured, total species richness for the rehabilitation tended to be lower, and the variety of plant life forms was restricted to low and mid stratum shrubs. Increasing water stress resulted in progressively higher rates of local species extinction, with fewer taxa possessing the drought tolerance adaptations required to survive. For established revegetation, cyclonic rainfall increased productivity (as measured by % foliage ground cover) and stimulated the establishment of new taxa, which in many cases were brought in from adjacent unmined vegetation complexes (analogue sites). While the benefits of summer cyclonic rainfall were undoubtedly important to ari and semi-arid ecosystems, the occurrence of drought was also important in buffering the ecosystem against large-scale change by acting as a negative feedback to constrain cumulative productivity. Parent waste rock material varied considerably between rehabilitation sites, affecting the soil resource supply and associated functional components. Extreme salinity was a typical limitation of the rehabilitation medium, reducing the variety of salt tolerant species and favouring annual Atriplex during the early stages of ecosystem development. The cover of annual species present during early stages of ecosystem development contributed to decreasing salinity in the plant rooting zone, by reducing surface temperature and hence capillary rise of salts during summer months.
Annual Atriplex species were replaced by perennial Atriplex in line with decreasing surface salinity. Fundamental to successful revegetation of the post-mining rehabilitation site was the requirement that reconstruction and contouring focus on maximising water retention and reducing salinity within the upper soil profile. Once the initial vegetation community established and plant parameters became relatively stable, change continued to occur, albeit slowly. One factor contributing to this change was the immigration rate of biota from adjacent revegetation or more commonly from surrounding analogue complexes. Linking rehabilitation areas to surrounding functional ecosystems ensured the movement of plants and animals, and ultimately increased the rate of recovery. The sustainability of post-mining rehabilitation was enhanced where these links were established early, allowing for the provision of additional seed and the migration of displaced species. The life cycle pattern of keystone species in the revegetation was found to be an important determinant in long-term sustainability of the plant cover, particularly for chenopod shrublands where one species was typically dominant. The senescence and death of large numbers of a dominant revegetation species together, had the ability to significantly alter the revegetation structure and composition. The impact for rehabilitation where a number of dominant taxa co-exist was less pronounced. Thus it follows that a minimum level of species richness was important to long-term rehabilitation sustainability, as was the development of an age-class structure in the rehabilitation.
The most common disturbances encountered at the rehabilitation trial sites were drought, overgrazing and weed infestation. All three disturbances decreased the plant biodiversity parameters measured. Ecosystem recovery following disturbance was dependent on effective rainfall, but occurred rapidly with plant parameters returning to pre-disturbance levels within one to two growing seasons. The recovery of plant biodiversity parameters followed the same trends identified at functional rehabilitation sites during the initial five years following direct seeding. 3 Assessment of plant biodiversity parameters occurred at 15 analogue sites supporting native vegetation undisturbed by mining. It was anticipated that data from analogue sites could be used as a 'reference' against which to compare developing rehabilitation. However, analogue vegetation complexes were less dynamic in comparison to rehabilitation sites. Minor seasonal changes were recorded for plant biodiversity parameters, but overall annual change was minimal. Significant and sudden changes within analogue communities only occurred following disturbance, such as severe overgrazing, and recovery to pre-disturbance levels was rapid following the removal of the disturbance and return of effective rainfall. A major difference between rehabilitation and analogue sites related to their age. Rehabilitation sites were 'juvenile systems' assessed against a time frame much shorter than had been required for natural processes to achieve the developmental state represented at analogue sites.
Hence, it was important not to model one specific analogue site too closely, but instead model the desired revegetation structure and species composition on a variety of local analogue complexes occurring in parent materials 'matched' closely to those of the rehabilitation site. Data from analogue sites should be utilised extensively during rehabilitation planning, but cautiously when interpreting the rehabilitation outcome. For mine sites in arid and semi-arid Western Australia, the application of specific numeric targets for plant biodiversity parameters as a measure of rehabilitation success was not recommended. A number of factors and controls in the developing ecosystem together determined the rehabilitation outcome. These factors were site and time specific; minor changes in any number of variables led to significantly different rehabilitation outcomes, making them difficult to accurately predict. 4 Quality and germination testing confirmed progeny seed from a number of rehabilitation trials was of similar or higher viability than the maternal seed originally sown. This was further confirmed by field responses at trials in the Northeastern Goldfields one year after the 1994 drought, when elevated plant density was recorded following the return of above average rainfall. The ability of rehabilitation to show an immediate response to rainfall following a seven-month drought, and for vegetation parameters to subsequently recover to pre-disturbance levels within one to two years, provided an indication that the revegetation cover was resilient. The relationship between plant production and rainfall was dependent on a 'carryover' effect between seasons or following drought years, and 'pulses' mediated, for instance, by the amount of seed in the soil store.
The 'reserve' component in and ecosystems was responsible for both the memory of the system between pulses and for its long-term resilience. 6 The analysis of time series data collected from 19 rehabilitation trials emphasized the importance of planning and implementation of best practice techniques to subsequent rehabilitation success, and reinforced the difficulty associated with accurately predicting the final rehabilitation outcome. The large spatial heterogeneity of undisturbed vegetation complexes across the landscape of arid and semi-arid Western Australia, provided the foundation on which site-specific rehabilitation scenarios could be modelled, albeit with caution. The translation of data into useful completion criteria was dependent on the realisation that successful rehabilitation requires the implementation of best practice rehabilitation techniques, as determined by technically prescriptive (design) based standards, as much as the identification of a successful rehabilitation outcome, as determined by performance (outcome) based standards. With this in mind, completion criteria were developed as part of a robust theoretical framework incorporating the larger mine plan, and were not simply based on numbers generated as stand-alone performance standards. The broad methodology generated could be adopted by any mine site across the mining industry, however the criteria and, more specifically, the standards for each criterion should always remain site specific.
The methodology designed for developing completion criteria has been addressed in three stages: 1. Planning, 2. Operational and Monitoring, and 3. Post-Mining Hand-Over. Within each stage three parameters are addressed: 1. Criteria, 2. Process, and 3. Standard. 'Planning' is the most important stage in the development of completion criteria. It is the stage when an appropriate end land use is determined, analogue sites are assessed, a rehabilitation plan developed along with specified design standards ensuring implementation of best practice techniques, and a process of risk assessment implemented. The 'Operational Monitoring Stage' focuses on rehabilitation success during the period of ecosystem development. This stage is concerned largely with rehabilitation monitoring, from which performance standards can be developed to gauge rehabilitation success for specific periods during revegetation development. The initial task in Stage 2 is to ensure all aspects of the rehabilitation plan have been implemented as specified in Stage 1, and meet agreed design standards. The final stage of the completion criteria process, 'Post Mining Hand Over', is to ensure the rehabilitated site is safe, and able to successfully revert to the end land use.
While plant biodiversity parameters formed the focus of the current study, a variety of other functional ecosystem components may also make sound assessment criteria for determining rehabilitation success. Increasing the knowledge base for other functional components in arid and semi-arid ecosystems would further increase the ability to accurately determine rehabilitation success.
Studies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 25 (Fall/Winter 1987)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1987. http://hdl.handle.net/10150/303424.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter No. 23 (December 1985)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1985. http://hdl.handle.net/10150/303444.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter No. 24 (June 1986)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1986. http://hdl.handle.net/10150/217873.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter No. 22 (September 1985)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1985. http://hdl.handle.net/10150/227913.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter No. 37 (Spring/Summer 1995)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1995. http://hdl.handle.net/10150/228111.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter No. 38 (Fall/Winter 1995)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1995. http://hdl.handle.net/10150/228112.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 26 (Spring/Summer 1988)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1988. http://hdl.handle.net/10150/228183.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 27 (Fall/Winter 1988)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1988. http://hdl.handle.net/10150/228184.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 28 (Spring/Summer 1989)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1989. http://hdl.handle.net/10150/228211.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 29 (Fall/Winter 1989)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1989. http://hdl.handle.net/10150/228182.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 30 (Fall/Winter 1990)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1990. http://hdl.handle.net/10150/228185.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 31 (Fall/Winter 1991)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1991. http://hdl.handle.net/10150/228186.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 32 (Spring/Summer 1992)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1992. http://hdl.handle.net/10150/228187.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 33 (Spring/Summer 1993)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1993. http://hdl.handle.net/10150/228188.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 34 (Fall/Winter 1993)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1993. http://hdl.handle.net/10150/228189.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 35 (Spring/Summer 1994)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1994. http://hdl.handle.net/10150/228190.
Pełny tekst źródłaStudies, University of Arizona Office of Arid Lands. "Arid Lands Newsletter Vol. 36 (Fall/Winter 1994)". Office of Arid Lands Studies, College of Agriculture, University of Arizona (Tucson, AZ), 1994. http://hdl.handle.net/10150/228231.
Pełny tekst źródłaAbushandi, Eyad. "Rainfall-runoff modeling in arid areas". Doctoral thesis, Technische Universitaet Bergakademie Freiberg Universitaetsbibliothek "Georgius Agricola", 2011. http://nbn-resolving.de/urn:nbn:de:bsz:105-qucosa-68530.
Pełny tekst źródłaPatrick, Cecil. "Reservoir tillage for semi-arid environments". Thesis, Cranfield University, 2005. https://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.426071.
Pełny tekst źródłaHempson, Gareth Peter. "Herbivore dynamics in an arid environment". Thesis, University of Edinburgh, 2011. http://hdl.handle.net/1842/5665.
Pełny tekst źródłaAl-Qurashi, Aisha Mufti Al-Sayyid Hassan. "Rainfall-runoff modelling in arid areas". Thesis, Imperial College London, 2008. http://hdl.handle.net/10044/1/8860.
Pełny tekst źródłaBraun, Jeffery Kenneth. "Cold Arid Climate, Efficient Building Design". The University of Arizona, 2015. http://hdl.handle.net/10150/552683.
Pełny tekst źródłaThis paper will look at the current information concerning sustainable strategies. It will look at the ones that have been used in the past as well as the strategies that are currently being used. After studying the existing material on sustainable practices and strategies the next step will be looking at three primary sources and determining strategies that will be most useful. The first source that will be used is a professional working in the field. Secondly buildings that are located in a cold arid climate will be studied and finally a program called climate consultant. The recommendations from all three sources will be compiled in a list, organized by how many sources recommended each strategy. The strategies that have the most recommendations will be implemented into a residential single family building design for cold arid climates.
Giacomelli, Gene, i Kathryn Hahne. "Evaporative Cooling in Semi-Arid Climates". College of Agriculture and Life Sciences, University of Arizona (Tucson, AZ), 2008. http://hdl.handle.net/10150/146294.
Pełny tekst źródłaIn the semi-arid climate of southern AZ, evaporative cooling systems are commonly used and very effective for cooling homes (swamp coolers), outdoor areas (misters), and for greenhouses used for commercial and horticultural plant production (pad-and-fan, high-pressure-fog). The purpose of this brochure is to educate users about strategies they can employ to save water and improve the performance of evaporative cooling systems. Principles of operation, a list of advantages and disadvantages, and a comparison of common systems is also included, to help users decide the best system for them.
Cermak, Otto Wayne 1935. "Aesthetic design using arid climate plants". Thesis, The University of Arizona, 1988. http://hdl.handle.net/10150/191984.
Pełny tekst źródłaElgallal, Manal Mukhtar. "Development of an approach for the evaluation of wastewater reuse options for arid and semi-arid area". Thesis, University of Leeds, 2017. http://etheses.whiterose.ac.uk/17581/.
Pełny tekst źródłaAbubeker, Hassen. "Characterization and evaluation of Indigofera species as potential forage and cover crops for semi-arid and arid ecosystems". Pretoria : [s.n.], 2006. http://upetd.up.ac.za/thesis/available/etd-03292006-171339.
Pełny tekst źródłaMimi, Ziad A. "Water resources and water demand management for arid and semi-arid areas : West Bank as a case study". Thesis, Loughborough University, 1999. https://dspace.lboro.ac.uk/2134/7169.
Pełny tekst źródłaRamali, Aman Mohamed. "Optimisation of water use for food production in arid and semi-arid regions : a case study of Libya". Thesis, University of Reading, 2011. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.558727.
Pełny tekst źródłaYaraghi, N. (Navid). "Assessing the impacts of artificial groundwater recharge structures on river flow regime in arid and semi-arid regions". Master's thesis, University of Oulu, 2017. http://urn.fi/URN:NBN:fi:oulu-201709062799.
Pełny tekst źródłaWhittington-Jones, Gareth Morgan. "The role of aardvarks (Orycteropus afer) as ecosystem engineers in arid and semi-arid landscapes of South Africa". Thesis, Rhodes University, 2007. http://hdl.handle.net/10962/d1005445.
Pełny tekst źródłaHelu, Ali Tuama. "Integrated water losses assessment and water balance study over arid and semi-arid basins located in developing countries". Thesis, Cardiff University, 2015. http://orca.cf.ac.uk/89385/.
Pełny tekst źródłaHamilton, Jeffrey Muir. "Arugula Crop Production in Arid and Semi-Arid Regions: Nutritional Value, Postharvest Quality, and Sustainability in Controlled Environments". Diss., The University of Arizona, 2009. http://hdl.handle.net/10150/195968.
Pełny tekst źródłaLadbrook, Megan. "Spatial and temporal patterns (1973-2012) of bushfire in an arid to semi-arid region of Western Australia". Thesis, Edith Cowan University, Research Online, Perth, Western Australia, 2015. https://ro.ecu.edu.au/theses/1660.
Pełny tekst źródłaHutton, Christopher Joseph. "Modelling watershed processes in semi-arid environments". Thesis, University of Exeter, 2010. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.529295.
Pełny tekst źródłaBakir, N. M. W. "Environmental house planning in hot arid countries". Thesis, Cardiff University, 1987. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.376562.
Pełny tekst źródłaTorofder, Golam. "Manipulating wheat yield in semi-arid environments". Thesis, University of Aberdeen, 2002. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.394451.
Pełny tekst źródłaGibson, Michelle Rene. "Movement ecology of Australian arid-zone birds". Thesis, Durham University, 2018. http://etheses.dur.ac.uk/12778/.
Pełny tekst źródłaYoung, Deborah J., i Malchus B. Jr Baker. "Management of Semi-Arid Watersheds: Technology Transfer". Arizona-Nevada Academy of Science, 1998. http://hdl.handle.net/10150/296506.
Pełny tekst źródłaGunawardene, Nihara. "Arid zone ant communities of Western Australia". Thesis, Curtin University, 2003. http://hdl.handle.net/20.500.11937/1178.
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