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Assessing sodium

The only subsequent regulatory development thus far under TOSCA, directed specifically at soluble silicates, was a proposed rule (54) under Section 8(a) which would require manufacturers to keep certain records and report production and exposure related data on approximately 2300 chemicals to EPA. This information was held to be necessary to rank chemicals for investigation and to make preliminary risk assessments. Sodium silicate, potassium silicate, sodium metasilicate and sodium orthosilicate were included on the candidate list, presumably because reports to the initial inventory showed them to be manufactured in high tonnage volume. [Pg.44]

Activation Atrial preparation Biophysics Calcium channel Cardiac action potential Channel kinetics Comprehensive in vitro proarrhythmia assay Delayed rectifier Early afterdepolarisation ECG Hodgkin-Huxley ICHS7A ICHS7B In silico modelling Inactivation Inward rectifier Langendorff heart Purkinje fibre Safety assessment Sodium channel Stem cells... [Pg.150]

Assessing sodium concentration is of clinical relevance as low urine sodium concentration may indicate dehydration, while a relatively high urine sodium concentration suggests acute renal failure. Lvova and coworkers (2009) proposed an E-tongue composed of chemical sensors to detect urinary system dysfunctions and creatinine levels. The electrochemical system was composed of miniaturized metallic sensors and ISEs with PVC solvent polymeric membranes. The device enabled the correct classification of urine samples from healthy volunteers, according to creatinine levels and to predict the creatinine content of urine. [Pg.381]

In this section the influence of micelles of cetyltrimethylammonium bromide (CTAB), sodium dodecylsulfate (SDS) and dodecyl heptaoxyethylene ether (C12E7) on the Diels-Alder reaction of 5.1a-g with 5.2 in the absence of Lewis-add catalysts is described (see Scheme 5.1). Note that the dienophiles can be divided into nonionic (5.1a-e), anionic (5.If) and cationic (5.1g) species. A comparison of the effect of nonionic (C12E7), anionic (SDS) and cationic (CTAB) micelles on the rates of their reaction with 5.2 will assess of the importance of electrostatic interactions in micellar catalysis or inhibition. [Pg.133]

The correct viscose age or ripeness for spinning varies according to the type of fiber being made. Ripeness can be assessed by estabHshing the salt concentration necessary to just coagulate the viscose dope. The preferred test uses sodium chloride (salt figure) although ammonium chloride is the basis of the alternative method (Hottenroth number). [Pg.347]

Assessment of Sodium Conductor Distribution Cable, DOE/ET-504-1, Westinghouse Research and Development Center, Pittsburgh, Pa., June 1979. [Pg.172]

A simple, quahtative method is the skin stripping technique (322) which strips off a sampling from the skin with ceUophane tape. Methods have been developed (330,331) in which organisms on the hands ate transferred to gloves and sampled. These methods assess both immediate and persistent effects of antiseptics. In aH tests with antiseptics, suitable neutralizing chemicals for the antiseptics employed are necessary so that surviving bacteria may be recovered and counted. Some of these are lecithin, Lubrol W, Polysorbate, and sodium thiosulfate (322). [Pg.140]

Water Tests. In colorfastness to water, ISO 10S-E01, the test specimen is placed in contact with the chosen adjacent fabrics, immersed in water, and placed wet between glass plates and left for 4 h at 37°C. After drying, the effect on the test specimen and stain on adjacents are assessed. The test, colorfastness to seawater, ISO 10S-E02, is the same as EOl but uses 30 g/L anhydrous sodium chloride solution instead of water. To test for colorfastness to chlorinated seawater/swimming baths water, ISO 10S-E03, the specimen is immersed in sodium hypochlorite solution containing either 100, 50, or 20 mg of active chlorine per Hter at pH 7.5 for 1 h at 27°C, rinsed, dried, and assessed. [Pg.376]

Eor colorfastness to perspiration, ISO 10S-E04, the specimen is immersed in a solution of 0.5 g/L of 1-histidine monohydrochloride monohydrate and 5 g/L sodium chloride buffered to either pH 8.0 (alkaH perspiration test) or pH 5.5 (acid perspiration test) in a dish at 50 1 Hquor-to-goods ratio, at room temperature for 30 min. The specimen is removed and, as in the water test EOl, left for 4 h between plates at 37°C before drying and assessing both test piece and adjacents. [Pg.376]

In colorfastness to acid spotting, ISO 10S-E0S, drops of a solution of either acetic acid (300 g of glacial acetic acid per Hter of water), sulfuric acid (50 g of concentrated acid per Hter), or tartaric acid (100 g of crystalline acid per Hter) are spotted onto the test material, which is then dried and assessed. Colorfastness to alkaH spotting, ISO 10S-E06, is like E05 except that a solution of 100 g of anhydrous sodium carbonate per Hter of water is used. Colorfastness to water spotting, ISO 10S-E07, is like E05 but uses drops of water and assessment is made after 2 min wet and after drying. In colorfastness to hot water, ISO 10S-E08, the textile specimen and adjacents are wound around a glass rod and placed in water adjusted to pH 6 with acetic acid at 70°C... [Pg.376]

Golorfastness to Bleaching. In fastness to hypochlorite bleachiag, ISO 10S-N01, the specimen is agitated ia a solution of sodium, calcium, or lithium hypochlorite containing 2 g/L available chlorine buffered to pH 11.0 with sodium carbonate for 1 h at 20°C and 50 1 Hquor-to-goods ratio. The specimen is tinsed ia water, hydrogen peroxide, or sodium bisulfite solution to remove free chlorine, dried, and assessed. [Pg.377]

In fastness to peroxide bleaching, ISO 10S-N02, the specimen is immersed ia a standard bleaching solution containing hydrogen peroxide (or sodium peroxide for viscose) where the composition of the bleaching Hquor is dependent on the fibers used ia the test specimen as are the pH and time of exposure (1—2 h). The objective of the test is to assess the colorfastness usiag typical bulk bleaching conditions for the fiber under test. [Pg.377]

In this reaction, iodine is liberated from a solution of potassium iodide. This reaction can be used to assess the amount of ozone in either air or water. For determination in air or oxygen, a measured volume of gas is drawn through a wash bottle containing potassium iodide solution. Upon lowering the pH with acid, titration is effected with sodium thiosulfate, using a starch solution as an indicator. There is a similar procedure for determining ozone in water. [Pg.485]

A fairly detailed risk analysis of fires was in the Clinch River Breeder Reactor (CRBR) Risk Assessment Study, 1977. In this study, FMEA was used to identify important fire locations for a wide variety of combustibles, including cables, oil, and sodium. The resulting estimate of the frequency of fire-induced core melt, 5E-7 per reactor-year, is substantially below the estimates discussed above. [Pg.196]

This test uses a cloud of sodium chloride particles. The size distribution is from below 0.1 pm to approximately 2.0 pm and a figure for percentage penetration is obtained. Since the test does not materially load the filter, it can be used to assess the quality of each unit before dispatch. This test forms the basis of Eurovent 4/4, which differs a little in procedure. [Pg.451]

Thermogravimetry is a valuable technique for the assessment of the purity of materials. Analytical reagents, especially those used in titrimetric analysis as primary standards, e.g. sodium carbonate, sodium tetraborate, and potassium hydrogenphthalate, have been examined. Many primary standards absorb appreciable amounts of water when exposed to moist atmospheres. TG data can show the extent of this absorption and hence the most suitable drying temperature for a given reagent may be determined. [Pg.432]

As the DI plant becomes exhausted, silica leakage occurs in the treated MU water and the pH falls abruptly. Furthermore, where sodium ion leakage occurs from the cation bed, it produces a regenerative effect on the anion bed, which may also lead to silica leakage. To differentiate between the two phenomena, sodium ion leakage from the cation bed should be assessed directly using selective sodium-ion electrodes, flame photometric analysis, or other appropriate test methods. [Pg.199]

The complexation of Pu(IV) with carbonate ions is investigated by solubility measurements of 238Pu02 in neutral to alkaline solutions containing sodium carbonate and bicarbonate. The total concentration of carbonate ions and pH are varied at the constant ionic strength (I = 1.0), in which the initial pH values are adjusted by altering the ratio of carbonate to bicarbonate ions. The oxidation state of dissolved species in equilibrium solutions are determined by absorption spectrophotometry and differential pulse polarography. The most stable oxidation state of Pu in carbonate solutions is found to be Pu(IV), which is present as hydroxocarbonate or carbonate species. The formation constants of these complexes are calculated on the basis of solubility data which are determined to be a function of two variable parameters the carbonate concentration and pH. The hydrolysis reactions of Pu(IV) in the present experimental system assessed by using the literature data are taken into account for calculation of the carbonate complexation. [Pg.315]

Sodium dodecyl sulfate has been used to induce a dry, scaly skin condition in human subjects by daily treatment with a 4% aqueous solution on one leg over a period of 2 weeks. Measurements were made of stratum comeum hydration, scaliness, and lipid composition which were used to assess in vivo surfactant perturbations on desquamation [381]. [Pg.292]

The most recent comprehensive assessment of the quality of rivers in the USA is that of Smith et al. 12), This followed an earlier assessment by Wolman et al. in 1971 (iS). The former 1987 assessment was based on 24 water quality measures from 161-383 stations around the country covering the period 1974-1981. Trends observed included major increases in nitrate, phosphorous, sodium, suspended sediment, fecal bacteria, dissolved oxygen deficit, arsenic and selenium. Major decreases were observed with nitrate, suspended sediment, fecal bacteria, dissolved oxygen deficit and lead. [Pg.244]

Use chemical behavior and electronegativities to assess the reasonableness of the assignments. Phosphoric acid can be viewed as the phosphate anion (-3 charge) associated with three H ions. Sodium, an alkali metal, readily forms cations with +1 charge, hi KH, the assignments are consistent with the electronegativities (jjf) of the two elements — 0.8, = 2.1. [Pg.1357]

Tjandra et al. (1998) have proposed an interfacial reaction model for the kinetics of the reaction between 1-bromo octane and sodium phenoxide to give 1-phenoxyoctane in a nonionic microemulsion. In this model the microemulsion is assumed to consist of the aqueous phase and the interface is covered by a monolayer of surfactant molecules. It is thus possible to assess the interfacial area from the concentration of the surfactant in the microemulsion medium. [Pg.151]

Solid-phase microextraction (SPME) consists of dipping a fiber into an aqueous sample to adsorb the analytes followed by thermal desorption into the carrier stream for GC, or, if the analytes are thermally labile, they can be desorbed into the mobile phase for LC. Examples of commercially available fibers include 100-qm PDMS, 65-qm Carbowax-divinylbenzene (CW-DVB), 75-qm Carboxen-polydimethylsiloxane (CX-PDMS), and 85-qm polyacrylate, the last being more suitable for the determination of triazines. The LCDs can be as low as 0.1 qgL Since the quantity of analyte adsorbed on the fiber is based on equilibrium rather than extraction, procedural recovery cannot be assessed on the basis of percentage extraction. The robustness and sensitivity of the technique were demonstrated in an inter-laboratory validation study for several parent triazines and DEA and DIA. A 65-qm CW-DVB fiber was employed for analyte adsorption followed by desorption into the injection port (split/splitless) of a gas chromatograph. The sample was adjusted to neutral pH, and sodium chloride was added to obtain a concentration of 0.3 g During continuous... [Pg.427]


See other pages where Assessing sodium is mentioned: [Pg.33]    [Pg.33]    [Pg.406]    [Pg.225]    [Pg.376]    [Pg.2209]    [Pg.222]    [Pg.235]    [Pg.217]    [Pg.1035]    [Pg.1049]    [Pg.403]    [Pg.552]    [Pg.482]    [Pg.185]    [Pg.186]    [Pg.257]    [Pg.32]    [Pg.245]    [Pg.157]    [Pg.280]    [Pg.282]    [Pg.105]    [Pg.231]    [Pg.273]    [Pg.465]    [Pg.99]    [Pg.144]    [Pg.235]   
See also in sourсe #XX -- [ Pg.118 ]




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