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Geosciences 2018, 8, 56 17 of 18 44. Schowanek, D.; Feijtel, T.C.; Perkins, C.M.; Hartman, F.A.; Federle, T.W.; Larson, R.J. Biodegradation of [S, S], [R, R] and mixed stereoisomers of ethylenediaminedisuccinic acid (EDDS), a transition metal chelator. Chemosphere 1997, 34, 2375–2391. [CrossRef] 45. Hyvönen, H. Studies on Metal Complex Formation of Environmentally Friendly Aminopolycarboxylate Chelating Agents. Ph.D. Thesis, University of Helsinki, Helsinki, Finland, 2008. 46. Takahashi, R.; Fujimoto, N.; Suzuki, M.; Endo, T. Biodegradabilities of ethylenediamine-N, N′-disuccinic acid (EDDS) and other chelating agents. Biosci. Biotechnol. Biochem. 1997, 61, 1957–1959. [CrossRef] [PubMed] 47. Meers, E.; Tack, F.M.G.; Verloo, M.G. Degradability of ethylenediaminedisuccinic acid (EDDS) in metal contaminated soils: Implications for its use soil remediation. Chemosphere 2008, 70, 358–363. [CrossRef] [PubMed] 48. Metsärinne, S.; Tuhkanen, T.; Aksela, R. Photodegradation of ethylenediaminetetraacetic acid (EDTA) and ethylenediamine disuccinic acid (EDDS) within natural UV radiation range. Chemosphere 2001, 45, 949–955. [CrossRef] 49. Turan, M.; Esringu, A. Phytoremediation based on canola (Brassica napus L.) and Indian mustard (Brassica juncea L.) planted on spiked soil by aliquot amount of Cd, Cu, Pb, and Zn. Plant Soil Environ. 2007, 53, 7. 50. Kos, B.; Greman, H.; Lestan, D. Phytoextraction of lead, zinc and cadmium from soil by selected plants. Plant Soil Environ. 2003, 49, 548–553. 51. Pereira, B.F.F.; Abreu, C.A.D.; Herpin, U.; Abreu, M.F.D.; Berton, R.S. Phytoremediation of lead by jack beans on a Rhodic Hapludox amended with EDTA. Sci. Agricola 2010, 67, 308–318. [CrossRef] 52. Seth, C.S.; Misra, V.; Singh, R.R.; Zolla, L. EDTA-enhanced lead phytoremediation in sunflower (Helianthus annuus L.) hydroponic culture. Plant Soil 2011, 347, 231. [CrossRef] 53. Pinto, I.S.; Neto, I.F.; Soares, H.M. Biodegradable chelating agents for industrial, domestic, and agricultural applications, a review. Environ. Sci. Pollut. Res. 2014, 21, 11893–11906. [CrossRef] [PubMed] 54. Luo, C.; Shen, Z.; Li, X. Enhanced phytoextraction of Cu, Pb, Zn and Cd with EDTA and EDDS. Chemosphere 2005, 59, 1–11. [CrossRef] [PubMed] 55. Tandy, S.; Schulin, R.; Nowack, B. Uptake of metals during chelant-assisted phytoextraction with EDDS related to the solubilized metal concentration. Environ. Sci. Technol. 2006, 40, 2753–2758. [CrossRef] [PubMed] 56. Hauser, L.; Tandy, S.; Schulin, R.; Nowack, B. Column extraction of heavy metals from soils using the biodegradable chelating agent EDDS. Environ. Sci. Technol. 2005, 39, 6819–6824. [CrossRef] [PubMed] 57. Grcˇman, H.; Vodnik, D.; Velikonja-Bolta, Š.; Leštan, D. Ethylenediaminedissuccinate as a new chelate for environmentally safe enhanced lead phytoextraction. J. Environ. Qual. 2003, 32, 500–506. [CrossRef] [PubMed] 58. Fine, P.; Paresh, R.; Beriozkin, A.; Hass, A. Chelant-enhanced heavy metal uptake by Eucalyptus trees under controlled deficit irrigation. Sci. Total Environ. 2014, 493, 995–1005. [CrossRef] [PubMed] 59. Shilev, S.; Naydenov, M.; Tahsin, N.; Sancho, E.D.; Benlloch, M.; Vancheva, V.; Sapundjieva, K.; Kuzmanova, J. Effect of easily biodegradable amendments on heavy metal solubilization and accumulation in technical crops—A field trial. J. Environ. Eng. Landsc. Manag. 2007, 15, 237–242. 60. Cao, A.; Carucci, A.; Lai, T.; La Colla, P.; Tamburini, E. Effect of biodegradable chelating agents on heavy metals phytoextraction with Mirabilis jalapa and on its associated bacteria. Eur. J. Soil Biol. 2007, 43, 200–206. [CrossRef] 61. Lenntech. Lithium (Li) and Water: Reaction Mechanisms, Environmental Impact and Health Effects. 2017. Available online: https://www.lenntech.com/periodic/elements/li.htm (accessed on 2 November 2017). 62. Schrauzer, G.N. Lithium: Occurrence, dietary intakes, nutritional essentiality. J. Am. Coll. Nutr. 2002, 21, 14–21. [CrossRef] [PubMed] 63. Wallace, A.; Romney, E.M.; Cha, J.W.; Chaudhry, F.M. Lithium toxicity in plants. Commun. Soil Sci. Plant Anal. 1977, 8, 773–780. [CrossRef] 64. Kabata-Pendias, A.; Pendias, H. Source Trace Elements in Soil and Plants, 3rd ed.; CRC Press: Boca Raton, FL, USA, 1984; p. 116. 65. Shahzad, B.; Tanveer, M.; Hassan, W.; Shah, A.N.; Anjum, S.A.; Cheema, S.A.; Ali, I. Lithium toxicity in plants: Reasons, mechanisms and remediation possibilities—A review. Plant Physiol. Biochem. 2016, 107, 104–115. [CrossRef] [PubMed]PDF Image | Induced Plant Accumulation of Lithium
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Product and Development Focus for Infinity Turbine
ORC Waste Heat Turbine and ORC System Build Plans: All turbine plans are $10,000 each. This allows you to build a system and then consider licensing for production after you have completed and tested a unit.Redox Flow Battery Technology: With the advent of the new USA tax credits for producing and selling batteries ($35/kW) we are focussing on a simple flow battery using shipping containers as the modular electrolyte storage units with tax credits up to $140,000 per system. Our main focus is on the salt battery. This battery can be used for both thermal and electrical storage applications. We call it the Cogeneration Battery or Cogen Battery. One project is converting salt (brine) based water conditioners to simultaneously produce power. In addition, there are many opportunities to extract Lithium from brine (salt lakes, groundwater, and producer water).Salt water or brine are huge sources for lithium. Most of the worlds lithium is acquired from a brine source. It's even in seawater in a low concentration. Brine is also a byproduct of huge powerplants, which can now use that as an electrolyte and a huge flow battery (which allows storage at the source).We welcome any business and equipment inquiries, as well as licensing our turbines for manufacturing.CONTACT TEL: 608-238-6001 Email: greg@infinityturbine.com (Standard Web Page)