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Spectrophotometric investigation of the deep blue colored, water-soluble complex of
Method | ΔF (Kcal/mole) | ||||
Mukherji and Dey (4) | 4.11 | ?5.70 | |||
Subhrana and Raghavrao (6) | 4.80 | ?6.66 |
Taken (μg) | Found (μg)a | Standard deviation (μg) |
751 | 748 | 12 |
1501 | 1485 | 15 |
2252 | 2192 | 7 |
- a
- The values are the average of seven determinations, from which the standard deviation value was calculated.
12.
A simple, rapid, and accurate method for determination of total sulfur and inorganic sulfate in biological materials by barium chloranilate colorimetry is presented. Criteria required
Sample | Determinations | Mean (μg) | SD (μg) | ||
Whole blood | 10 | 1004 | 21 | ||
Blood plasma | 10 | 543 | 4 | ||
TCA extracts | 10 | 24 | 2 | ||
Urine (totals) | 10 | 598 | 31 | ||
Urine (inorganic S) | 10 | 374.4 | 19 |
Hydrochloric acid | 4 — 8M | ||||
Lead | 0 — 0.03M | ||||
Antimony | 0 — 0.002M |
Time (min) | 0 | 5 | 10 | 30 | 60 |
Consumption of Mn(III) (mol/mol) | 2.00 | 1.99 | 2.00 | 2.01 | 2.00 |
Transition metal | Concentration (M) | Percentage inhibition | Mg(II) found (×l05M) |
Fe(II) | 3.6.10?5 | 54.1 | 4.62 |
Fe(III) | 3.6.10?5 | 47.8 | 4.48 |
Co(II) | 3.4.10?5 | 50.0 | 4.53 |
Ni(II) | 3.4.10?5 | 50.0 | 4.53 |
Cu(II) | 3.1.10?5 | 52.0 | 4.56 |
Zn(II) | 3.0.10?5 | 54.1 | 4.62 |
Cd(II) | 1.7.10?5 | 52.0 | 4.56 |
Hg(II) | 9.9.10?6 | 45.8 | 4.44 |
Sn(II) | 2.1.10?6 | 50.0 | 4.52 |
Pb(II) | 1.2.10?6 | 54.1 | 4.62 |
- a
- Conditions: 4.53.10?5M Mg(II), 35 ng Mn ml?1, 0.429 M ammonia, 1.6.10?4M OH-PDT.
Mg(II) found (M)b | |||
Natural water | Ca(II) presenta | Atomic absorption | |
sample | M | Kinetic absorption | method |
Commercial | 3.45 · 10?4 | 1.65 · 10?3 | 1.74 · 10?3 |
Commercial | 5.46 · 10?4 | 1.57 · 10?4 | 1.81 · 10?4 |
Untreated | 6.13 · 10?4 | 2.16 · 10?4 | 2.40 · 10?4 |
Treated | 4.95 · 10?4 | 1.93 · 10?4 | 2.17 · 10?4 |
- a
- EDTA titration less the magnesium.
- b
- Average of three separate determinations. traces of magnesium(II). The reaction is followed spectrophotometrically by measuring the rate of change in absorbance at 594 nm. The calibration graph (percentage inhibition vs magnesium concentration) is linear in the range 329–535 · 10?5M with an accuracy and precision of 1.2%. The method has been applied to the determination of magnesium in natural waters at low concentrations.
17.
A sensitive spectrofluorimetric procedure with rhodamine B in the presence of aluminum chloride is given for determining submicrogram and microgram quantities of thallium in silicate rocks. Samples are decomposed with a mixture of hydrofluoric and nitric acids and then treated with hydrochloric acid. Thallium is extracted as its dithizonate with chloroform from an alkaline medium containing ascorbate, citrate, and cyanide and then back-extracted with dilute nitric acid. After destruction of the organic matter and treatment with bromine, hydrochloric acid, aluminum chloride, and rhodamine B, the
相似文献
Thallium (p.p.m.) | Method | Ref. | |
G-1 | W-1 | ||
1.06 | 0.102 | Neutron activation analysis | 1 |
1.08 | 0.121, 0.116 | Neutron activation analysis | 2 |
1.3 | 0.17 | Neutron activation analysis | 3 |
1.3 | 0.11 | Spectrographic | 4 |
0.105–0.110 | Flameless atomic absorption spectroscopy | 5 | |
1.3a | 0.13a | 19 | |
1.24b | 0.110b | 20 | |
1.09 ± 0.01 | 0.110 ± 0.005 | Spectrofluorimetric | Present method |
- a
- Values given by Fleischer.
- b
- Average value given by Flanagan. fluorescence intensity of the benzene-extracted rhodamine B chlorothallate is measured. The limit of determination is approximately 0.01 p.p.m. for a 1.0-g sample. The thallium contents of U.S. Geological Survey standard rocks G-1 and W-1 were found to be 1.09 ± 0.01 and 0.110 ± 0.005 p.p.m., respectively.
18.
Sulfite ion reacts with mercury(II) ion in acid solution to form the mercury(I) ion. The reaction is rapid and quantitative. The mercury(I) ion absorbs at 237 nm with a molar
相似文献
SO2 (ppm) | ?HgCl2a | ?HgBr2 | ?Hg(Ac)2b | ?Hg(SCN)2 |
2.0 | 12,500 | 10,000 | 10,000 | 9,200 |
4.0 | 12,500 | 11,500 | 10,000 | 9,000 |
6.0 | 12,500 | 11,500 | 10,000 | 9,200 |
8.0 | 12,000 | 11,000 | 10,500 | 9,800 |
- a
- Molar absorptivity based on sulfite ion at 230 nm. Solution was 6.86 buffer.
- b
- Mercuric acetate solutions seemed to be somewhat unstable. absorptivity of about 25,000. The absorbance is linear over a range of approximately 0.5–5.0 ppm as SO2. Covalent mercury(II) compounds form a complex with sulfite, Hg(SO3)22?, which absorbs at 230 nm and shows a linear response over a range of 1–8 ppm as SO2.
19.
A potentiometric method is described for the determination of thiosemicarbazones involving the formation of a complex with Ag(I). This method is proposed for thiosemicarbazones of the following carbonyl compounds: salicylaldehyde, p-hydroxybenzaldehyde, benzaldehyde, picolinaldehyde, 6-methylpicolinaldehyde and p-dimethylaminebenzaldehyde. Stability constants of the complexes are determined by Ringbom and Harju's method. FIG. 2. Variation of pAg + logαPAT (H) + log ([Ag?PAT)]/[PAT])
Thiosemicarbazone | Log |
-Benzaldehyde | 15.5 ± 0.1 |
-Picolinaldehyde | 14.0 ± 0. |
-6-Methylpicolinaldehyde | 14.5 ± 0. |
-Salicylaldehyde | 15.7 ± 0.1 |
-p-Hydroxybenzaldehyde | 15.6 ± 0. |
-p-Dimethylaminebenzaldehyde | 17.2 ± 0.1 |
Cell type | Applications |
Human polymorphonuclear leukocytes | (1) Detection of bactericidal defects, particularly chronic granulomatous disease |
(2) Detection of host opsonic defects (both immunoglobulin and complement ?C3b opsonic defects). | |
(3) Analysis of drug effects on host cellular and opsonic defenses (9,11). | |
(4) Characterization of bacteria or other particulate matter in terms of ability to generate opsonic activity and/or be ingested by phagocytic cells (3,7). | |
Alveolar macrophages | (1) Detection of environmental pollutant effects on respiratory defense mechanisms (against both particulate and soluble matter). |
(2) Analysis of drug effects on respiratory defense mechanisms, particularly drugs administered in the treatment of respiratory diseases. |
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