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#Cplot so42 ucsd
terrimake · 2 years
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Cplot so42 ucsd
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However there haveīeen no systematic geochemical studies of potassium accumulation in this lake. Yuan (1981) on how potassium accumulates in theĭabuxun Lake provided important clues to our There have been several articles discussing theįormation of potash in the Qarhan Saline Lake Is far more complicated than simple equilibrium Therefore, the formation mechanism of potash, marine or non-marine, Salt crystals when the brine becomes saturated Seawater, potash must form in the playa stage.Īt this stage brines can exist in only voids between Salt sediments along the evaporative path of QSL is now in a stage called “playa lake” asĭefined by Valyashko (1972a). Low, it is still possible for potassium to accumulate Sodium is less than 0.01, much less than seawater.Īlthough the potassium concentration is relatively Solid and liquid) are 53.4 billion tons and 0.44 billion tons, respectively. Qinhai Province, China, the total NaCl and KClĬontents in the Qarhan Saline Lake (including Of the First Geological Team (Yang et al., 1968) of Potash evaporites may be found in this lake Lake: disseminated, stratoid and layered, each having its counterparts in ancient potash deposits.īecause hydrological and geochemical processesĪre very active in this lake, many phenomena canīe observed today. Occurrences of potash salts in the Qarhan Saline Saline Lake (QSL) in the Qaidam Basin, WestĬhina, demonstrate that some anomalous marinetype evaporites are formingfrom non-marine Modern potash-salt deposits in the Qarhan Key-words: inland basin, potash deposit, brine geochemistry, saline lake, carnallite, China. This is a very important process for the accumulation of potash deposits as discovered in the The sediments, including disseminated potash salts, are redistributed after the dissolution. During the playa-lake stage, the shift of inflow river channels may result in the dissolution ofĭry salt plains and the formation of a brine lake. Of potassium in brine lakes (e.g., the Dabuxun Lake) seated in the dry salt plain and the formation of stratoid potashĪlong the lake shore. Hydrological cycles are responsible for the accumulation Cooling is an additionalįactor in the precipitation of the disseminated potash salts. It was found thatĭisseminated potash salts precipitate through the slow evaporation of intercrystalline brine. Model, the formation mechanisms of potash salts have been studied and described in this article. Geochemical processes and geomorphology in and around the lake, and using the specific interaction solubility Through the investigation of the sediments, hydrological cycles, Of potash salts: disseminated, stratoid and layered. In this lake, there are three different occurrences The National Laboratory of Mineral Deposit Research, Department of Earth Sciences,Ībstract: The Qarhan Saline Lake is now in the stage ìplaya lakeî, where brine lakes and a dry salt plain coexist.Īlthough an inland lake, it has large amount of marine-type salts. Department of Chemistry, University of California, San Diego, La Jolla, CA 92093-0340, USAĢ. The accumulation of potash in a continental basin:ġ.
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greysgifts · 2 years
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Cplot so42 ucsd
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In addition, plants hold the potential for the development of a cost-effective approach for the removal and remediation of heavy metalladen soils and water through the use of metal-hyperaccumulating plants (phytoremediation) ( Raskin et al., 1994 Dushenkov et al., 1995 Salt et al., 1995, 1998 Clemens, 2006). Food crops are a major source of heavy metal intake in humans, which has prompted interest in understanding how plants take up, detoxify and retain heavy metals. Many human disorders have been attributed to the ingestion of heavy metals, including learning disabilities in children, dementia, impairment of bone metabolism and increased cancer rates ( Tong et al., 2000 Allen et al., 2002 Aschner and Walker, 2002 Ohta et al., 2002 Yu et al., 2002 Waisberg et al., 2003 Heck et al., 2009 Satarug et al., 2010). Toxic metals such as lead, cadmium (Cd), mercury and the metalloid arsenic can accumulate in soils and water to levels that are detrimental to human and environmental health. Our results modify the glutathione-depletion driven model for sulfate assimilation gene induction during cadmium stress, and suggest that an enhanced oxidative state and depletion of upstream thiols, in addition to glutathione depletion, are necessary to induce the transcription of sulfate assimilation genes during early cadmium stress. Moreover, genetic, HPLC mass spectrometry, and gene expression analysis of the nrc1 and nrc2 mutants, revealed that intracellular glutathione depletion alone would be insufficient to induce gene expression of sulfate uptake and assimilation mechanisms. The nrc1 mutation was mapped to the γ-glutamylcysteine synthetase gene and the nrc2 mutation was identified as the first viable recessive mutant allele in the glutathione synthetase gene. Two nrc mutants, nrc1 and nrc2, were mapped, cloned and further characterized. The screen identified non-allelic mutant lines that fell into one of three categories: (i) super response to cadmium ( SRC) mutants (ii) constitutive response to cadmium ( CRC) mutants or (iii) non-response and reduced response to cadmium ( NRC) mutants. Stably transformed luciferase reporter lines were ethyl methanesulfonate (EMS) mutagenized, and stable M 2 seedlings were screened for an abnormal luciferase response during exposure to cadmium. The SULTR1 2 promoter (2.2 kb) was fused with the firefly luciferase reporter gene to quantitatively report the transcriptional response of plants exposed to cadmium. Microarray studies identified a high-affinity sulfate transporter ( SULTR1 2) among the most robust and rapid cadmium-inducible transcripts. To genetically elucidate cadmium-specific transcriptional responses in Arabidopsis, we designed a genetic screen based on the activation of a cadmium-inducible reporter gene. However, the mechanisms mediating toxic heavy metal-induced gene expression remain largely unknown. Plants exposed to heavy metals rapidly induce changes in gene expression that activate and enhance detoxification mechanisms, including toxic-metal chelation and the scavenging of reactive oxygen species.
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