Relevant bibliographies by topics / Phytovolatilization

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  2. Dissertations / Theses
  3. Book chapters

Academic literature on the topic 'Phytovolatilization'

Author: Grafiati
Published: 4 June 2021
Last updated: 25 April 2022

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Journal articles on the topic "Phytovolatilization"

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Limmer, Matt, and Joel Burken. "Phytovolatilization of Organic Contaminants." Environmental Science & Technology 50, no. 13 (June 16, 2016): 6632–43. http://dx.doi.org/10.1021/acs.est.5b04113.

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Zhou, Li Ming, Jun Xiang Chen, Jian Mei Zhou, Hui Guo, and Bo Liu. "Research Progresses in Soil Phytoremediation Polluted by Cadmium." Advanced Materials Research 1073-1076 (December 2014): 659–65. http://dx.doi.org/10.4028/www.scientific.net/amr.1073-1076.659.

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Phytoremediation is the use of plants for the removal of pollutants from contaminated soil. Phytoremediation is an environmentally friendly and cost effective alternative to current remediation technologies. This review outlines general aspects of phytoremediation. It further reviews various phytoremediation processes in detail: phytoextraction, rhizofiltration, phytostabilization, rhizosphere degradation, and phytovolatilization. The hyperaccumulators of cadium and advances in the phytoextraction, phytostabilization, transgenic plants, agricultural technologies for soil phytoremediation by cadium were reviewed.
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Edwards, Maureen R. A., Marie-France Hetu, Melanie Columbus, Anthony Silva, and Daniel D. Lefebvre. "THE EFFECT OF ETHYLENE GLYCOL ON THE PHYTOVOLATILIZATION OF 1,4-DIOXANE." International Journal of Phytoremediation 13, no. 7 (August 2011): 702–16. http://dx.doi.org/10.1080/15226514.2010.525553.

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Zhang, Qing, Wenqian Kong, Linfeng Wei, Yingjun Wang, Yadan Luo, Pu Wang, Jiyan Liu, Jerald L. Schnoor, and Guibin Jiang. "Uptake, phytovolatilization, and interconversion of 2,4-dibromophenol and 2,4-dibromoanisole in rice plants." Environment International 142 (September 2020): 105888. http://dx.doi.org/10.1016/j.envint.2020.105888.

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Arnold, C. W., D. G. Parfitt, and M. Kaltreider. "Phytovolatilization of Oxygenated Gasoline-Impacted Groundwater at an Underground Storage Tank Site Via Conifers." International Journal of Phytoremediation 9, no. 1 (March 2007): 53–69. http://dx.doi.org/10.1080/15226510601139409.

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Guarino, Francesco, Antonio Miranda, Stefano Castiglione, and Angela Cicatelli. "Arsenic phytovolatilization and epigenetic modifications in Arundo donax L. assisted by a PGPR consortium." Chemosphere 251 (July 2020): 126310. http://dx.doi.org/10.1016/j.chemosphere.2020.126310.

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OSENI, Ojo M., Omotola E. DADA, Gideon O. OKUNLOLA, Ezekiel D. OLOWOLAJU, Michael S. AKINROPO, Akinjide M. AFOLABI, and Adebisi A. AKINLABI. "Phytoremediation technology, plant response to environmental contaminants and the need for soil augmentation." Notulae Scientia Biologicae 12, no. 3 (September 29, 2020): 486–99. http://dx.doi.org/10.15835/nsb12310737.

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Contaminants in the environment occur naturally and/or through anthropogenic activities. These contaminants become a threat to all living organisms because of their increased in the environment and non-biodegradable nature. In order to protect the environment from these contamination, various techniques have been developed, and among them is phytoremediation. Phytoremediation is a technology that employed plant species for reclaiming contaminated soil, air, and water. This technology has been widely accepted in recent times, because of its low cost and environmentally friendly. In addition, augmentation of the contaminated soil, either chemo augmentation or bioaugmentation, have been used for the effective absorption of some of these contaminants. When the plants are grown in the contaminated sites, the contaminant in the soil maybe removed, immobilized, degraded or volatized. These phytoremediation technologies are: phytoextraction, phytovolatilization, rhizofiltration, phyto-stimulation, phyto-stabilization and phytodegradation. Based on the phytoremediation potentials of plants, pollutants are being removed from the environment thereby keeping the environment safe.
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Peco, Jesús D., Pablo Higueras, Juan A. Campos, José M. Esbrí, Marta M. Moreno, Fabienne Battaglia-Brunet, and Luisa M. Sandalio. "Abandoned Mine Lands Reclamation by Plant Remediation Technologies." Sustainability 13, no. 12 (June 8, 2021): 6555. http://dx.doi.org/10.3390/su13126555.

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Abandoned mine lands (AMLs), which are considered some of the most dangerous anthropogenic activities in the world, are a source of hazards relating to potentially toxic elements (PTEs). Traditional reclamation techniques, which are expensive, time-consuming and not well accepted by the general public, cannot be used on a large scale. However, plant-based techniques have gained acceptance as an environmentally friendly alternative over the last 20 years. Plants can be used in AMLs for PTE phytoextraction, phytostabilization, and phytovolatilization. We reviewed these phytoremediation techniques, paying particular attention to the selection of appropriate plants in each case. In order to assess the suitability of plants for phytoremediation purposes, the accumulation capacity and tolerance mechanisms of PTEs was described. We also compiled a collection of interesting actual examples of AML phytoremediation. On-site studies have shown positive results in terms of soil quality improvement, reduced PTE bioavailability, and increased biodiversity. However, phytoremediation strategies need to better characterize potential plant candidates in order to improve PTE extraction and to reduce the negative impact on AMLs.
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Tiodar, Emanuela D., Cristina L. Văcar, and Dorina Podar. "Phytoremediation and Microorganisms-Assisted Phytoremediation of Mercury-Contaminated Soils: Challenges and Perspectives." International Journal of Environmental Research and Public Health 18, no. 5 (March 2, 2021): 2435. http://dx.doi.org/10.3390/ijerph18052435.

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Mercury (Hg) pollution is a global threat to human and environmental health because of its toxicity, mobility and long-term persistence. Although costly engineering-based technologies can be used to treat heavily Hg-contaminated areas, they are not suitable for decontaminating agricultural or extensively-polluted soils. Emerging phyto- and bioremediation strategies for decontaminating Hg-polluted soils generally involve low investment, simple operation, and in situ application, and they are less destructive for the ecosystem. Current understanding of the uptake, translocation and sequestration of Hg in plants is reviewed to highlight new avenues for exploration in phytoremediation research, and different phytoremediation strategies (phytostabilization, phytoextraction and phytovolatilization) are discussed. Research aimed at identifying suitable plant species and associated-microorganisms for use in phytoremediation of Hg-contaminated soils is also surveyed. Investigation into the potential use of transgenic plants in Hg-phytoremediation is described. Recent research on exploiting the beneficial interactions between plants and microorganisms (bacteria and fungi) that are Hg-resistant and secrete plant growth promoting compounds is reviewed. We highlight areas where more research is required into the effective use of phytoremediation on Hg-contaminated sites, and conclude that the approaches it offers provide considerable potential for the future.
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Ogo, O., S. Agbara, B. Inalegwu, and IW Nyinoh. "Assessment of Heavy Metal Bioaccumulation Capacity of Calopogonium muconoides and Senna obtusifolia as Potential Bioremediation Agents." NIGERIAN ANNALS OF PURE AND APPLIED SCIENCES 4, no. 1 (August 21, 2021): 191–200. http://dx.doi.org/10.46912/napas.230.

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A wide range of inorganic and organic compounds such as combustibles, and putrescible substances, hazardous waste, explosives, petroleum products and heavy metals (HM) can cause contamination. In addition, the non-biodegradability of heavy metals further exacerbates environmental pollution with its attendant health consequences on the biotic components of the ecosystem including humans. The use of living organisms such as plants and microbes is increasingly becoming acceptable practice of sustainable environmental sanitation. However, identification of potential bioremediation agents is still challenging. This study was carried out to bridge this gap by assessing heavy metal bioaccumulation properties of Calopogoniun Muconoides and Senna obtusifolia plants at contaminated site of mechanic workshop (site 1) in comparative to a physically non-contaminated site (site 2) within Makurdi metropolis of Benue State Nigeria. The selected plants were obtained from both sites and evaluated for their bioaccumulation capacities using standard procedures. The results revealed the sample plants accumulated high levels of heavy metals particularly in the leaves and roots, suggesting the utilization of phytoextraction, phytostabilization and phytovolatilization mechanisms of remediation. The plants and HM generally presented an order of concentration and bioaccumulation as: Senna obtusifolia > Calopogonium Muconoides; Zn > Fe > Pb > Cu > Cd > Cr > Ni. These findings suggest that these novel plants, especially Senna obtusifolia are good agents of bioremediation of heavy metals. Studies involving isotopic labeling to determine the exact mechanism of remediation as well molecular techniques such as transcriptomics and proteomics to identify genes/molecules that confer phytoremediation potential on the plants would be the next focus of our research in this emerging field of environmental biochemistry.
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Dissertations / Theses on the topic "Phytovolatilization"

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Diamond, J. Oliver. "Quantifying the Removal of Trichloroethylene via Phytoremediation a Hill Air Force Base, Utah Operational Unit 2 Using Recent and Historical Data." DigitalCommons@USU, 2016. https://digitalcommons.usu.edu/etd/4743.

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Trichloroethylene (TCE) is a carcinogenic, chlorinated volatile organic compound that was commonly used as a degreasing solvent for aircraft maintenance at many US Air Force bases. Past improper disposal of TCE has resulted in contaminated groundwater at many of these facilities. Phytoremediation, defined as the use of plants and their associated microorganisms to stabilize or remove contamination, has been implemented as part of a TCE groundwater cleanup at Travis Air Force base near Sacramento, CA and is being considered as a remediation option at other bases. Volatilization of TCE from leaves and the surface of the soil near the trees were shown to be the most important removal mechanisms at the Travis site. Past studies conducted on indigenous trees growing above TCE contaminated groundwater at several Hill Air Force Base (HAFB) locations have also shown that TCE is taken up and volatilized by the trees. However, phytoremediation has not been implemented, in part because of the difficulty in predicting the potential effectiveness of TCE removal over time. Flow through or recirculating chambers were used to quantify the amount of TCE removed by volatilization through leaf, trunk, and soil surfaces. Tenax™ sorbent tubes, used to collect TCE from the chambers, were analyzed by thermal desorption gas chromatography/mass spectrometry. Tree cores were collected using an incremental borer and analyzed by headspace GC/MS to quantify the TCE mass contained in the trees. Field measured transpiration stream concentrations (TSC) and groundwater data were used to calculate transpiration stream concentration factors (TSCF) for TCE. Comparing current and historical data, it was found that trees reach a steady state TSCF value of 0.26 after about 15 years. Using this information, it was predicted that a phytoremediation plot containing 40 poplar trees located in a seep area within HAFB OU2 would remove 4.82 kg of TCE annually. A larger plot covering the entire hillside above this seep (160 trees) could remove up to 19.28 kg of TCE annually, once trees reach a steady state TSCF.
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Book chapters on the topic "Phytovolatilization"

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Arya, S. S., S. Devi, R. Angrish, I. Singal, and Kanta Rani. "Soil Reclamation Through Phytoextraction and Phytovolatilization." In Volatiles and Food Security, 25–43. Singapore: Springer Singapore, 2017. http://dx.doi.org/10.1007/978-981-10-5553-9_3.

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Zayed, Adel, Elizabeth Pilon-Smits, Mark deSouza, Zhi-Qing Lin, and Norman Terry. "Remediation of Selenium-Polluted Soils and Waters by Phytovolatilization." In Phytoremediation of Contaminated Soil and Water. CRC Press, 1999. http://dx.doi.org/10.1201/9781439822654.ch4.

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Zayed, Adel, Elizabeth Pilon-Smits, Mark deSouza, Zhi-Qing Lin, and Norman Terry. "Remediation of Selenium-Polluted Soils and Waters by Phytovolatilization." In Phytoremediation of Contaminated Soil and Water, 61–83. CRC Press, 2020. http://dx.doi.org/10.1201/9780367803148-4.

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Jagdale, Swati, and Aniruddha Chabukswar. "Phyto-Remediation: Using Plants to Clean Up Soils." In Advances in Environmental Engineering and Green Technologies, 215–35. IGI Global, 2016. http://dx.doi.org/10.4018/978-1-4666-9734-8.ch011.

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In this chapter authors have discussed the role of plants to develop contaminant free environment. This concept is also known as Phytoremediation. Phytoremediation is a word formed from the Greek prefix “phyto” meaning plant, and the Latin suffix “remedium” meaning to clean or restore. This technology has been receiving attention lately as an innovative, cost-effective alternative to the more established treatment methods used at hazardous waste sites. Phytoremediation can be classified into different applications, such as phytofiltration or rhizofiltration, phytostabilization, phytovolatilization, phytodegradation and phyto-extraction etc. The chapter will deal with phytoremediation, its advantages, limitations and in detail techniques of classification and application.
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Bhandari, Geeta. "Phytoremediation." In Advances in Environmental Engineering and Green Technologies, 286–304. IGI Global, 2018. http://dx.doi.org/10.4018/978-1-5225-3126-5.ch018.

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Environmental pollution with xenobiotics is a global problem and development of inventive remediation technologies for the decontamination of impacted sites are therefore of paramount importance. Phytoremediation capitalizes on plant systems for removal of pollutants from the environment. Phytoremediation is a low maintenance remediation strategy and less destructive than physical or chemical remediation. Phytoremediation may occur directly through uptake, translocation into plant shoots and metabolism (phytodegradation) or volatilization (phytovolatilization) or indirectly through plant-microbe-contaminant interactions within plant root zones (rhizospheres). In recent years, researchers have engineered plants with genes that can bestow superior degradation abilities. Thus, phytoremediation can be more explored, demonstrated, and/or implemented for the cleanup of metal contaminants, inorganic pollutants, and organic contaminants.
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Farraji, Hossein, Nastaein Qamaruz Zaman, Mohammad Ali Zahed, and Hamed Faraji. "Role of Rhizoremediation in Decontaminating Some Hazardous Pollutants." In Handbook of Research on Inventive Bioremediation Techniques, 213–46. IGI Global, 2017. http://dx.doi.org/10.4018/978-1-5225-2325-3.ch009.

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Rhizoremediation is a natural biological base, multifactorial operation treatment method which highly depends to environmental factors especially in terrestrial environment as operation of remediation process. Interaction and relationship between microbial community and plant roots is specific attraction and advantages of this advanced treatment method. Decontamination efficiency and time could be highly manageable by operation and rhizoaugmentation. Rhizoremediation is advanced compact combination of phytoextraction, phytovolatilization, phytotransformation and phytostabilization. High efficiency of pollutants removal, adaptive and wide range of operation and augmentation factors cause of emerging application of this for biodegradable organic compounds and heavy metals. Selection of suitable plant and joining them with comfortable microbial couples is a function which can plane simultaneously removal system. This chapter will present an overview on PAH, TPH, PCB and heavy metal removal and mechanism of decontamination, plant selection and augmentation process.
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Krishnasamy, Selvanayaki, Ramkumar Lakshmanan, and Mythili Ravichandran. "Phytoremediatiation of Metal and Metalloid Pollutants from Farmland: An In-Situ Soil Conservation." In Biodegradation Technology of Organic and Inorganic Pollutants. IntechOpen, 2022. http://dx.doi.org/10.5772/intechopen.98659.

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Phytoremediation is an effective technology for in-situ remediation of high level polluted soils. Phytoremediation is a plant-mediated approach, which involves the use of plants to absorb and remove elemental pollutants or lower their concentration or bioavailability to soil. Plants have efficacy to absorb compounds in the soil even at low concentration through their root system. Plant root system has geotropism which helps them to extend into the soil matrix and hyper accumulate heavy metals to increase their bioavailability considerably and thereby the polluted soil is domesticated and the soil fertility is enhanced. The heavy-metal-resistant endophytes give the promising effect on plant growth, by decreasing metal phytotoxicity and affecting metal translocation and accumulation in plants. It is an eye opening for researches to implement the phytoremediation of organic contaminants through endophytes that produce various enzymes to metabolize organic contaminants and reduce both the phytotoxicity and evapotranspiration of volatile contaminants. Here, we focus on the most widely used phytoremediation strategies, phytostabilization, phytoextraction, phytovolatilization, and phytofiltration in the remediation of heavy metal-polluted soil.
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Roy, Dibakar, Dasari Sreekanth, Deepak Pawar, Himanshu Mahawar, and Kamal K. Barman. "Phytoremediation of Arsenic Contaminated Water Using Aquatic, Semi-Aquatic and Submerged Weeds." In Biodegradation [Working Title]. IntechOpen, 2021. http://dx.doi.org/10.5772/intechopen.98961.

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Arsenic (As) is the one the most toxic element present in earth which poses a serious threat to the environment and human health. Arsenic contamination of drinking water in South and Southeast Asia reported one of the most threatening problems that causes serious health hazard of millions of people of India and Bangladesh. Further, use of arsenic contaminated ground water for irrigation purpose causes entry of arsenic in food crops, especially in Rice and other vegetable crops. Currently various chemical technologies utilized for As removal from contaminated water like adsorption and co-precipitation using salts, activated charcoal, ion exchange, membrane filtration etc. are very costly and cannot be used for large scale for drinking and agriculture use. In contrast, phytoremediation utilizes green plats to remove pollutants from contaminated water using various mechanisms such as rhizofiltration, phytoextraction, phytostabilization, phytodegrartion and phytovolatilization. A large numbers of terrestrial and aquatic weed flora have been identified so far having hyper metal, metalloid and organic pollutant removal capacity. Among the terrestrial weed flora Arundo donax, Typha latifolia, Typha angustifolia, Vetivaria zizinoids etc. are the hyper As accumulator. Similarly Eicchornea crassipes (Water hyacinth), Pistia stratiotes (water lettuce), Lemna minor (duck weed), Hyrdilla verticillata, Ceratophyllum demersum, Spirodella polyrhiza, Azola, Wolfia spp., etc. are also capable to extract higher amount of arsenic from contaminated water. These weed flora having As tolerance mechanism in their system and thus remediate As contaminated water vis-à-vis continue their life cycle. In this chapter we will discuss about As extraction potential of various aquatic and semi aquatic weeds from contaminated water, their tolerance mechanism, future scope and their application in future world mitigating As contamination in water resources.
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