8
Combustion with oxygen in a sealed Parr bomb has been accepted for many years as a standard procedure for converting solid and liquid combustible samples into soluble forms ready for chemical analysis. It is a reliable whose effectiveness stems from its ability to treat samples quickly and conveniently within a closed system, thus ensuring complete retention and potential recovery of all combustion products. The bomb combustion method is an essential step is standard ANSI/ASTM methods for determining sulfur and chlorine in coal, and it has been applied successfully to the determination of arsenic, phosphorus and other elements as well. The methods given here for sulfur and chlorine correspond to the basic ASTM reference methods for these elements, each of which calls for a gravimetric finish. Although these are reliable procedures, other less time consuming volumetric, nephelometric or ion chromatographic methods can be used for estimating these elements after recovering the bomb washings. Such alternatives are suggested in the references which follow. Sulfur in Combustible Solids. Burn a 1.0 gram sample and collect the washings as described in the basic procedure for using the 1108 oxygen bomb. Let the bomb stand for at least 5 minutes after firing; then remove it from the water and release the residual gases slowly and at an even rate so that the pressure is reduced to atmospheric in not less than one minute. Open the bomb and wash all parts of its interior, including the combustion capsule, valve passages and electrodes, with a fine jet of distilled water containing 1 ml of a saturated solution of methyl orange indicator per liter. Wash until no acid reaction is observed, collecting the washings in a beaker. If necessary, use a rubber policeman to transfer any precipitate from the bomb or capsule to the beaker. After neutralizing the solution, add 1 ml of ammonium hydroxide, heat the solution to boiling, and filter through a rapid qualitative paper. Wash the residue and filter paper with hot distilled water and add sufficient water to bring the total volume of solution to approximately 250 ml. Neutralize with concentrated hydrochloric acid and add 2 ml in excess. Add 10 ml of saturated bromine water and evaporate to approximately 200 ml on a hot plate or other source of heat. Adjust to a slow boil and stir constantly while adding 10 ml of a 10% barium chloride solution from a pipette. Continue stirring for two minutes, cover with a fluted watch glass and keep just below boiling on a steam bath or hot plate until the volume is reduced to 75 ml, then allow the precipitate to settle for another hour while cooling. Filter through an ashless filter paper and wash with warm water until free from chlorides. Transfer the paper and precipitate to a weighed crucible, dry at low heat, char the paper without flaming, then raise the temperature to a good red heat (approximately 925 °C) and heat to a constant weight. If the crucible is placed in a cold electric muffle furnace and the current turned on, drying, charring and ignition will usually occur at the desired rate. After ignition is complete, allow the crucible to cool to room temperature and weigh. Determine the exact weight of the barium sulfate precipitate and calculate the percentage of sulfur in the sample as follows: Sulfur, % = Wt. BaSO 4 X 13.734 Wt. Sample Sulfur in Combustible Liquids. For oils or other liquids containing 5% sulfur or less, use a sample weighing from 0.6 to 0.8 gram. If the sample contains over 5% sulfur, use a sample weighing from 0.3 to 0.4 gram and add an equal amount of sulfur- free U.S.P. white oil. If the sample is not readily miscible with white oil, some other low sulfur combustible diluent may be used. However, the combined weight of sample and white oil or other combustion aid must not exceed 1.0 gram. If the sample is volatile it must be weighed in a sealed holder. The procedure for filling the bomb, firing, recovering the washings and determining sulfates is the same for liquid samples as described in the preceding method for solids. Other less time consuming procedures have been suggested as an alternative to the gravimetric methods described here for estimating sulfur in the bomb washings. Among the titrimetric methods: Hicks 21 , et al titrates with lead perchlorate and determines the equivalence point using a lead ion specific electrode. Callan 11 suggests converting to benzadine sulfate and titrating with standard hydroxide solution. Siegfriedt 41 titrates with barium chloride solution using tetra-hydroxyquinone as an indicator. Randall 37 adds barium chloride in excess and back titrates with disodium hydrogen phosphate Analytical Methods for Oxygen Bombs No. 207M

207M, Analytical Methods for Oxygen Bombs

Embed Size (px)

Citation preview

Page 1: 207M, Analytical Methods for Oxygen Bombs

Combustion with oxygen in a sealed Parr bomb has been accepted for many years as a standard procedure for converting solid and liquid combustible samples into soluble forms ready for chemical analysis. It is a reliable whose effectiveness stems from its ability to treat samples quickly and conveniently within a closed system, thus ensuring complete retention and potential recovery of all combustion products. The bomb combustion method is an essential step is standard ANSI/ASTM methods for determining sulfur and chlorine in coal, and it has been applied successfully to the determination of arsenic, phosphorus and other elements as well. The methods given here for sulfur and chlorine correspond to the basic ASTM reference methods for these elements, each of which calls for a gravimetric finish. Although these are reliable procedures, other less time consuming volumetric, nephelometric or ion chromatographic methods can be used for estimating these elements after recovering the bomb washings. Such alternatives are suggested in the references which follow. Sulfur in Combustible Solids. Burn a 1.0 gram sample and collect the washings as described in the basic procedure for using the 1108 oxygen bomb. Let the bomb stand for at least 5 minutes after firing; then remove it from the water and release the residual gases slowly and at an even rate so that the pressure is reduced to atmospheric in not less than one minute. Open the bomb and wash all parts of its interior, including the combustion capsule, valve passages and electrodes, with a fine jet of distilled water containing 1 ml of a saturated solution of methyl orange indicator per liter. Wash until no acid reaction is observed, collecting the washings in a beaker. If necessary, use a rubber policeman to transfer any precipitate from the bomb or capsule to the beaker. After neutralizing the solution, add 1 ml of ammonium hydroxide, heat the solution to boiling, and filter through a rapid qualitative paper. Wash the residue and filter paper with hot distilled water and add sufficient water to bring the total volume of solution to approximately 250 ml. Neutralize with concentrated hydrochloric acid and add 2 ml in excess. Add 10 ml of saturated bromine water and evaporate to approximately 200 ml on a hot plate or other source of heat. Adjust to a slow boil and stir constantly while adding 10 ml of a 10% barium chloride solution from a pipette. Continue stirring for two minutes, cover

with a fluted watch glass and keep just below boiling on a steam bath or hot plate until the volume is reduced to 75 ml, then allow the precipitate to settle for another hour while cooling. Filter through an ashless filter paper and wash with warm water until free from chlorides. Transfer the paper and precipitate to a weighed crucible, dry at low heat, char the paper without flaming, then raise the temperature to a good red heat (approximately 925 °C) and heat to a constant weight. If the crucible is placed in a cold electric muffle furnace and the current turned on, drying, charring and ignition will usually occur at the desired rate. After ignition is complete, allow the crucible to cool to room temperature and weigh. Determine the exact weight of the barium sulfate precipitate and calculate the percentage of sulfur in the sample as follows: Sulfur, % = Wt. BaSO4 X 13.734 Wt. Sample Sulfur in Combustible Liquids. For oils or other liquids containing 5% sulfur or less, use a sample weighing from 0.6 to 0.8 gram. If the sample contains over 5% sulfur, use a sample weighing from 0.3 to 0.4 gram and add an equal amount of sulfur-free U.S.P. white oil. If the sample is not readily miscible with white oil, some other low sulfur combustible diluent may be used. However, the combined weight of sample and white oil or other combustion aid must not exceed 1.0 gram. If the sample is volatile it must be weighed in a sealed holder. The procedure for filling the bomb, firing, recovering the washings and determining sulfates is the same for liquid samples as described in the preceding method for solids. Other less time consuming procedures have been suggested as an alternative to the gravimetric methods described here for estimating sulfur in the bomb washings. Among the titrimetric methods: Hicks21, et al titrates with lead perchlorate and determines the equivalence point using a lead ion specific electrode. Callan11 suggests converting to benzadine sulfate and titrating with standard hydroxide solution. Siegfriedt41 titrates with barium chloride solution using tetra-hydroxyquinone as an indicator. Randall37 adds barium chloride in excess and back titrates with disodium hydrogen phosphate

Analytical Methods for Oxygen Bombs

No. 207M

Page 2: 207M, Analytical Methods for Oxygen Bombs

2

with the addition of alcohol. Herrig20 back titrates with Tritiplex III using phthalein purple as an indicator. A conductometric method has been suggested by Barthel6. Nephelometric methods for trace amounts of sulfate have been suggested by Toennies43 and Bailey5. Chlorine in Combustible Solids and Liquids. Platinum combustion capsules and platinum ignition wire are recommended for these tests because of the extremely corrosive nature of chlorine and its compounds. After repeated use with such samples, the inner surfaces of the bomb will become etched to the point where appreciable amounts of metal salts will be introduced during each combustion. The ability of the bomb to withstand such corrosion can be improved by keeping the inner surfaces highly polished. Any bomb which is being used for chlorine determinations should be repolished at regular intervals to prevent the development of deep pits. The alternative to this procedure is to use an 1108CL bomb which offers much better resistance to chlorine than the standard 1108 bomb. Or for ultimate protection, use an 1105C or 1106C bomb with a platinum liner. Samples containing more than 2% chlorine by weight should be diluted with U.S.P. white oil or some other non-volatile, chlorine-free diluent. The suggested amounts of sample and diluent are shown in the following table, but the user is cautioned that the combined weight of the charge must not exceed 1.0 gram. % Chlorine Grams of Grams of in Sample Sample White Oil Below 2 0.8 0.0 2 to 5 0.4 0.4 5 to 10 0.2 0.6 10 to 20 0.1 0.7 20 to 50 0.05 0.7 Place about 5 ml of a 5% sodium carbonate solution (135g Na2CO310H2O per liter) in the bomb, assemble and fill with oxygen to a pressure of 35 atmospheres. Immerse the bomb in a bath through which cold water is circulating. Attach the ignition wire to the bomb terminal, then stand at least six feet from the bath when firing the charge. Keep the bomb in the bath at least five minutes before removal. Release the residual gas slowly and at an even rate so that the pressure is reduced to atmospheric in not less than one minute. Open the bomb and examine for traces of unburned sample or sooty deposits. If found, discard the determination and clean the bomb thoroughly before using it again. If the combustion was satisfactory, wash the sample cup and all interior surfaces of the bomb with a fine stream of distilled water, collecting the washings in a

600 ml beaker. Scrub the interior of the cylinder and the underside of the head with a rubber policeman. Continue washing until no acid reaction is observed on any bomb parts or passages, which will normally require at least 300 ml of wash water. Acidify the solution by adding 1:1 nitric acid dropwise until the methyl red endpoint is observed; then add 2 ml excess acid. Filter through a qualitative paper and collect the filtrate in a 600 ml beaker. Heat to about 60 °C; protect from strong light and slowly add 5 ml of silver nitrate solution (50 g per liter) while stirring. Heat almost to boiling and hold at this temperature until the supernatant liquid becomes clear. Add a few drop of silver nitrate solution to test for complete precipitation. If cloudiness appears, repeat the above operation. Allow the beaker to stand in a dark place for at least one hour. Filter the precipitate by suction onto a weighed fritted glass filter. Wash with distilled water containing 2 ml of 1:1 nitric acid per liter. Dry the precipitate and crucible at 110 °C for one hour. Cool in a desiccator and weigh. Make a blank determination with 0.7 to 0.8 gram of white oil, omitting the sample; then calculate the chlorine content of the sample by substituting in the following equation: Chlorine, % by wt. = (P-B) 24.74 m where, P = grams AgCl obtained from sample B = grams AgCl obtained from blank m = mass of sample in grams ASTM Methods for Sulfur and Chlorine. Oxygen bomb procedures for determining sulfur and chlorine in a broad range of combustible materials are given in the following standard methods published by the American Society for Testing and Materials, copies can be obtained from ASTM at 1916 Race Street, Philadelphia, PA. 19103. ASTM Method D129-91, “Standard Test Method for Sulfur in Petroleum Products (General Bomb Method)”. ASTM Method D3177-89, “Standard Test Method for Total Sulfur in the Analysis Sample of Coal and Coke”. ASTM Method D2361-91, “Standard Test Method for Chlorine in Coal”. ASTM Method D1619-88, “Standard Test Method for Sulfur in Carbon Black”.

Page 3: 207M, Analytical Methods for Oxygen Bombs

3

ASTM Method D808-91, “Standard Test Method for Chlorine in New and Used Petroleum Products (Bomb Method)”. ASTM Method D1847-87, “Standard Test Method for Total Chlorine Content of Epoxy Resins”. ASTM Method D3684-78, (1988) “Standard Test Method for Total Mercury in Coal by the Oxygen Bomb Combustion/Atomic Absorption Method”. ASTM Method D3761-91, “Standard Test Method for Total Fluorine in Coal by the Oxygen Combustion/Ion Selective Electrode Method”. ASTM Method D4208-88, “Standard Test Method for Total Chlorine in Coal by the Oxygen Combustion/Ion Selective Electrode Method”. ASTM Method E144-64, (1992), “Standard Recommended Practice for Safe Use of Oxygen Combustion Bombs”. ASTM Method E775-87, “Standard Test Methods for Total Sulfur in the Analysis Sample of Refuse-Derived Fuel”. ASTM Method E776-87, “Standard Test Method for forms of Chlorine in Refuse-Derived Fuel”. ASTM Method E926-88, “Standard Test Method of Preparing Refuse-Derived Fuel (RDF) Samples for Analysis of Metals”. Halogen Determinations. Other halogens in addition to chlorine can be determined by the oxygen bomb method. Agruss3 used the oxygen bomb to determine chlorine, bromine and iodine mineral oils. Longo30 applied this method to many different organic compounds, with particular emphasis on the determination of iodine. Intonti25 used an oxygen bomb for analyzing insecticides and antifermentatives. Bradford8 describes a bomb method for determining fluorine in coal. Bailey5 and Selig38,39 describe the use of platinum lined bomb for determining fluorine. The Monsanto Co. 32 uses the oxygen bomb combustion method for determining small amounts of pentachlorophenol and similar chlorophenols in wall board, wood, paperboard, fish net, rubber etc. Recently, Nadkarni34 has used halogen selective electrodes to determine fluorine, chlorine, bromine and iodine in coal samples and polymers after combustion in an oxygen bomb. Arsenic Determinations. It has been shown by Carey12 that combustion in an oxygen bomb is a reliable way of preparing samples for the determination of arsenic by the Gutzeit method, or by the Marsh-Berzelius method. In this application the

oxygen bomb replaces the acid digestion generally used in the standard methods for arsenic. Mercury Determinations. Borchardt7 used an oxygen bomb to determine mercury in paper. Fujita17 determined mercury in rice, rice hulls and hair, while Ukita44 used the bomb method for mercury determinations using atomic absorption spectrometry for the final measurement. Phosphorus Determinations. Oxygen bomb methods for determining phosphorus have been given by Piercy35, Conrad13, Wreath47, and Buss10. One problem associated with this determination is the formation of a phosphoric acid mist in the bomb which does not settle out after combustion. To dissipate the mist, apply 20 v.d.c. to the electrodes. To minimize the formation of phosphoric acid mist, add one gram of sodium carbonate to the sample, mix some sodium naphthenate or zinc oxide with the sample. Boron Determinations. An oxygen bomb technique suggested by Hill22 has been found excellent for the destruction of animal and vegetable tissue preparatory to chemical analysis. A similar technique for the analysis of blood samples has also been recommended23. This procedure has been used successfully for determining small amounts of boron in animal and vegetable matter, and it seems reasonable to assume that it would work equally well for determining other elements. Burke9, Conrad13,14 and Kuck27 also describe methods for determining boron after combustion in an oxygen bomb. Other Elements. Selenium, Zinc, Lead, Titanium, Iron, Sodium, Potassium, Calcium, Magnesium, Copper, Carbon, Hydrogen, Oxygen, Tritium, Beryllium, Chromium, Manganese, Nickel, Vanadium and Carbon-14, all can be determined by oxygen bomb methods. Selenium has been determined in solid wastes by Johnson26 and in plant and animal tissue by Dye15. Zinc in rubber and copper in mushrooms has been reported by Przybylski36. Edwards16 has sodium, potassium, calcium and magnesium in fuels. Fujiwara18 describes methods for determining iron, aluminum and titanium in polyethylene, and Anduze4 on titanium in polyethylene. Lead in piston deposits has been determined by Conrad13. Lead in coal has been determined by Lindahl29. Carbon determinations by the oxygen bomb method have been reported by Adam1,2, Lambris28, Thomas42, Mehta31 and Nishioka33. Hydrogen has been determined by Mehta31 and Nishioka33 and Zhokovskay48. The use of two bombs for determining oxygen is described by Witaker46.

Page 4: 207M, Analytical Methods for Oxygen Bombs

4

Nadkarni34 has determined nitrogen in coal samples using a chemiluminescent method following combustion in an oxygen bomb. This method is much faster than the traditional Kjeldahl method, requiring only a minute to determine nitrogen concentration. A method for determining H3 and C14 in biological materials is described by Sheppard40. Fujiwara19 gives an excellent review of methods for determining trace elements in organic compounds by the oxygen bomb method.

Lindahl29 describes a particularly useful method for the determination of beryllium, chromium, manganese, nickel, vanadium, copper, lead and zinc in coal. A procedures manual issued by the U.S. Environmental Protection Agency recommends combustion in a Parr Oxygen Bomb for preparing all combustible materials for inorganic analysis. Specific procedures are given for mercury, antimony and arsenic.

PROCEDURES FOR DETERMINING TRACE

ELEMENTS USING A QUARTZ LINER IN THE 1108 OXYGEN BOMB

Trace amounts of heavy metals in coal and other combustible samples can be determined by the bomb method but usually these procedures have required the use of an expensive platinum liner in the bomb to avoid problems introduced by the leaching of trace amounts of heavy metals from the bomb walls and electrodes during combustion. This problem has now been resolved with the introduction of a cup and cover which can be used in any 1108 Parr oxygen bomb to hold the combustion products. Although a quartz liner does not offer the complete protection obtainable with a platinum liner, it is nevertheless an effective means for preventing heavy metal contamination in certain combustion procedures. THE 513A QUARTZ LINER The quartz liner now offered for use in the 1108 oxygen bomb consists of a quartz cup, 61 mm dia. x 86 mm deep, with a flat quartz cover which rests on top of the cup. Holes are provided in the cover for inserting platinum electrodes which extend into the cup to support a short length of platinum fuse wire and a fused silica sample holder. All of the parts needed to add this liner to an 1108 oxygen bomb are provided in the 1912 Conversion Set listed below. KRAFT (TRW) PROCEDURES Some of the earlier combustion procedures using a quartz-lined oxygen bomb were developed by M.L. Kraft of TRW, Inc., Defense and Space Systems Group, who used this method to prepare spark source mass spectrometry samples of coal, oil and other organic matter. In the Kraft methods the sample is burned in a fused silica capsule using 10 ml of 1:1 nitric acid in the bottom of the quartz liner to absorb the combustion products. Kraft found that background quantities of Cr, Fe, Ni and Mn were completely eliminated by this arrangement.

LINDAHL PROCEDURES FOR TRACE

ELEMENTS IN COAL Extensive studies by Peter C. Lindahl29 of the Exxon Production Research Company have shown that a quartz-lined Parr 1108 oxygen bomb provides a rapid and accurate method for treating coal samples to determine trace amounts of Be, Cd, Cr, Cu, Pb, Mn, Ni, V and Zn by atomic absorption spectrometry. The basic Lindahl combustion is described below. Further details covering final assays for each element are provided in the complete Lindahl Paper, a reprint of which can be obtained from Parr Instrument Company on request. Weigh a pelletized coal sample (1.0-1.2g) in a silica capsule. Transfer 10 ml of 1:10 HNO3 to either the combustion bomb or to the quartz liner. Assemble the bomb and charge it with oxygen to 15 atm. Place the bomb in a cooling water bath and ignite the sample. Allow the bomb to remain in the bath for 5 minutes, then remove the bomb and release the pressure slowly. Open the bomb carefully and rinse all parts thoroughly into a Teflon beaker; then evaporate the washings to dryness on a hot plate or in a microwave oven. Treat the residue in the Teflon beaker with 5 ml of aqua regia and 5 ml of HF and heat to dryness. Treat the residue with the appropriate volume of HNO3 along with water to make the final solution 1% in HNO3 after dilution to volume. For ash contents up to 5%, dilute to 25 ml. For ash up to 10% dilute to 100 ml. In Lindahl’s work, final assays were performed by atomic absorption spectrophotometric methods. Flame absorption analyses were run on a Perkin-Elmer Model 5000 AA Spectrophotometer. Flameless analyses were performed using a Perkin-Elmer Model 703 AA Spectrophotometer equipped with a Model 400 HGA. Hollow cathode lamps were used in all analyses except for cadmium and lead analysis in which electrodeless discharge lamps were used.

Page 5: 207M, Analytical Methods for Oxygen Bombs

5

QUARTZ LINER CONVERSION SET All of the parts needed to install a quartz liner in an 1108 oxygen bomb are provided in a conversion set (No. 1912) obtainable from Parr. The set consists of: 1 513A Quartz liner 1 4AFB Platinum electrode, straight 1 5AFB Platinum electrode, loop 2 68AC Lock nuts, T303SS 1 45C3 Platinum fuse wire, 300 cm 4 43A3 Combustion capsules, fused silica Any of the above items can also be purchased separately. PROCEDURE FOR INSTALLING THE LINER 1. Unscrew the two alloy electrodes from the bomb

head. Insert 4AFB platinum electrode through the hole nearest the center of the quartz cover; attach a 68AC lock nut to the straight electrode and screw the electrode into the insulated terminal in the bomb head.

2. Insert the 5AFB loop electrode into the opening nearest the edge of the quartz cover; attach a 68AC lock nut to the electrode and screw it into the bomb head.

3. Position the straight electrode with the hook pointed outward and tighten the lock nut gently; then turn the loop electrode to its center position and tighten the lock nut. Bring the loop electrode to its final position by gentle pressure in the loop itself, but remember that platinum is soft and the threads on the electrodes can be damaged by tightening lock nuts more than necessary. Also, it may be necessary to bend the loop electrode slightly to allow the cover to slide freely on the electrodes and still remain concentric with the bomb cylinder.

4. Use either fused silica or platinum combustion capsules with this assembly, and always use platinum fuse wire, either 36 ga. or 26 ga. wire in the same manner as the regular 45C10 alloy wire. If the heavier 26 ga. wire is used, wrap two or three turns around each electrode and shape

the wire into a running loop around the periphery of the capsule. This will allow the capsule to be inserted and removed without disturbing the fuse. It will also keep the wire out of the direct flame and reduce the possibility of a melt. Always add an auxiliary fuse to the heavy 26 ga. wire, using either cotton or nylon thread or a thin strip of filter paper for this purpose.

5. When firing the 26 ga. fuse do not hold the firing button down more than one or two seconds. A longer ignition period will melt the wire. If the wire melts, use the 7 cm terminals on the ignition unit to obtain a lower firing voltage; or add a heavy, one-ohm resistor to the 10-cm firing circuit to lower the voltage.

6. To assemble the bomb, slide the quartz cup into the cylinder and lower the head and quartz cover into the bomb gently so as not to break the cover.

7. For zinc and cadmium determinations, the 230A synthetic rubber sealing ring on the bomb head should be replaced with a similar ring made of Viton, Part No. 230AJV.

8. Handle the quartz cup and cover carefully as these parts are easily broken. And, although quartz is noted for its good resistance to thermal shock, these parts can be broken by a non-uniform burn or other unusual conditions in the bomb. Breakage can be minimized by always leaving as much moisture in the sample as possible (up to 40% in some cases) to avoid the sometimes explosive reaction which may result from burning a bone dry sample.

513A Quartz Liner with 514A Cover for 1108 Oxygen Bomb

1108 Oxygen

Bomb with 513A

Quartz Liner

Page 6: 207M, Analytical Methods for Oxygen Bombs

6

1. Adam. J., J. Chem. Met. Mining Soc. S. Africa, 39, 1

(1938). 2. Adam, J., “The Use of the Calorimetric Bomb for the

Determination of Carbon in Coal”, J. Chem. Met. Mining Soc. S. Africa 39, 69-70 (1938).

3. Agruss, M.S., Ayers, Jr., G.W. and Schindler, H.,

“Organic Halogen Compounds in Mineral Oils, Detection, Determination & Identification”, Ind. Eng. Chem., Anal. Ed. 13, 69-70 (1941).

4. Anduze. T. A., “Calorimetric Determination of Titanium

in Polyethylene”, Anal. Chem. 29, 90 (1957). 5. Bailey, J.J. and Gehring, D.G., “Determination of

Traces of S, F and B in Organic Materials by Oxygen Bomb Combustion”, Anal. Chem. 33, 1760 (1961).

6. Barthel, J., Herglotz, H. and Lissner, A., “Rapid Method

for the Determination of Total Sulfur in Solid Fuels”, Chem. Tech. (Ger.) 2, 179-81 (1950).

7. Borchardt, L.G. and Browning, B.L., “An Oxygen Bomb

Method for Determining Mercury in Paper”, Tappi 41, 669 (1958).

8. Bradford, H. R., “Fluorine in Western Coals”, Mining

Eng. 9, 78-9 (1957). 9. Burke, W.M., “Boron Determination in Volatile Organic

Compounds Using the Parr Oxygen Bomb”, Ind. Eng. Chem., Anal. Ed. 13, 50-1 (1941).

10. Buss, H., Kohlschutter, H.W. and Preiss, M.,

“Determination of Phosphorus in Organic Materials After Decomposition with Sodium Peroxide or Compressed Oxygen”, Z. Anal. Chem. 214 (2), 106-9 (1965).

11. Callan, T.P. and Toennies, G., “Determination of Sulfur

in Organic Compounds”, Ind. Eng. Chem., Anal. Ed. 13, 450-5 (1941).

12. Carey, F.P., Blodgett, G. and Satterlee, H.S.,

“Preparation of Samples for Determination of Arsenic – Oxygen Bomb Combustion Method”, Ind. Eng. Chem., Anal. Ed. 6, 327-30 (1934).

13. Conrad, Anne L., “Modification of the Parr Bomb

Method for the Combustion of Petroleum Products”, Mikrochemie ver. Mikrochim. Acta. 38, 514-20 (1951).

14. Conrad, Anne L. and Vigler, M.S., “Determination of

Boron in Borine Compounds”, Anal. Chem. 21, 585 (1949).

15. Dye, W.B., Bretthauer, E., Seim, H.J. and Blincoe, C.,

“Fluorometric Determination of Selenium in Plants and Animals with 3,3’-Diamino-benzadine”, Anal. Chem. 35, 1687 (1963).

16. Edwards, A.H. and Pearce, A.O., “Determination of

Sodium and Potassium in fuels”, Nature 154, 463 (1944).

17. Fujita, M., Terao, M., Takeda, Y., Hoshino, O. and

Ukita, C., Abstract Papers at the 24th Annual Meeting of the Pharmaceutical Society of Japan, p. 552 (1967).

18. Fujiwara, S. and Narasaki, H., Bunseki Kagaku 10,

1268 (1961). 19. Fujiwara, S. and Narasaki, “Determination of Trace

Elements in Organic Material by the Oxygen Bomb Method”, Anal. Chem. 40, 2031-3 (1968).

20. Herrig, H.J., Brennstoff-Chem. 42, 355 (1961). 21. Hicks, J.F., Fleenor, J. F. and Smith H., Anal. Chim.

Acta. 68, 480-3 (1974). 22. Hill, W. H., Seals, J. and Montiegel, Ethel, “Destruction

of Animal and Vegetable Tissue by Combustion in a Parr Oxygen Bomb”, Am. Ind. Hyg. Assoc. J. 19, 378-81 (1958).

23. Hill, W.H. and Smith, R.C., “Analysis of Blood for

Boron”, Am. Ind. Hyg. Assoc. J. 20, 131-3 (1959). 24. Huggler, N., “Sohio Modification of ASTM D-129,

Sulfur in Petroleum Products and Lubricants by the Bomb Method”. Standard Oil Co. (Ohio), March, 1956.

25. Intoni, R. and Gargiulo, M., “Determination of

Halogens in Organic Substances by Means of the Bomb Calorimeter”, Rend. Ist. Super. Sanita (Rome) 11, 731-42 (1948).

26. Johnson, H., “Determination of Selenium in Solid

Waste”, Environmental Science & Technology 4, 850-2 (1970).

27. Kuck, J.A. and Grim, E.C., Microchem, J. 3, 35 (1959). 28. Lambris, G. and Boll, H., “A New Method for the Rapid

and Exact Determination of Carbon Content of Solid and Liquid Fuels”, Brennstoff-Chem. 18, 61-6 (1937).

29. Lindahl, Peter C., “An Oxygen Bomb

Combustion/Atomic Absorption Spectrophotometric Method for the Determination of Trace Elements in Coal”, Exxon Production Research Company, Houston, Tx 77001. Reprints available from Parr Instrument Company, Moline, IL 61265

30. Longo, B., “Determination of Halogens, Especially

Iodine, in Organic Compounds Using the Calorimetric Bomb”, Atti. X° congr. Intern. Chim. 3, 427-8 (1939).

31. Mehta, R.K.S., “Determination of Carbon and

Hydrogen by Calorimeter Bomb”, J. Sci. Ind. Research (India) 13B, 195-203 (1954).

SELECTED BIBLIOGRAPHY OF OXYGEN BOMB METHODS

Page 7: 207M, Analytical Methods for Oxygen Bombs

7

32. Monsanto Co., Organic Chemicals Div., St. Louis, Mo., “Determination of Chlorphenols and Their Salts in Impregnated Materials”, Technical Bulletin 0-24 (March 15, 1945).

33. Nishioka, S. and Miwa, M., “Determination of Carbon

and Hydrogen with a Bomb Calorimeter”, J. Chem. Soc. Japan, Ind. Chem. Sect. 55, 377-9 (1952).

34. Nadkarni, R.A., “Determination of Volatile Elements in

Coal and other Organic Materials”, Am. Lab., August, 1981.

35. Piercy, G.T., Plant, E.K. and Rogers, M.C., “Rapid

Determination of Phosphorus in Linseed Oil by Oxygen Bomb”, Ind. Eng. Chem., Anal. Ed. 12, 165 (1940).

36. Przybylski, E., “A New Application of the Calorimetric

Bomb for Quantitative Analysis”, Roczniki Pantswowego Zakladu Hig. 5, 170 (1954).

37. Randall, M. and Stevenson, H.O., “Rapid Volumetric

Method for the Determination of Sulfate Ion”, Ind. Eng. Chem., Anal. Ed. 14, 620-1 (1942).

38. Selig, W., “Fluorine Analysis of Viton and Viton

Containing Explosives”, Univ. Calif. Radia. Lab. Bul. 14875 (1966).

39. Selig, W., “Fluorine Analysis of Plastic-Bonded

Explosives and Plastics”, Univ. Calif. Radia. Lab. Bul. 70156 (1966).

40. Sheppard, H. and Rodegker, W., “Determination of H3

and C14 in Biological Materials Using Oxygen Bomb Combustion”, Anal. Biochemistry 4, 246-51 (1962).

41. Siegfriedt, R.K., Wiberley, J.S. and Moore, R.W., “Determination of Sulfur after Combustion in a Small Oxygen Bomb”, Anal. Chem. 23, 1008-11 (1951).

42. Thomas, M., “Rapid Method for Determination of

Carbon in Explosive Materials”, Mem. poudres 34, 402-11 (1952).

43. Toennies, G. and Bakay, B., “ Photonephelometric

Microdetermination of Sulfate in Organic Compounds”, Anal. Chem. 25, 160-5 (1953).

44. Ukita, T., Osawa, T., Imura, N., Tonomura, M., Sayato,

Y., Nakamuro, K., Kanno, S., Fukui, S., Kaneko, K., Ishikura, S., Yonaha, M., and Nakamura, T., “A Novel Quick Determination of Mercury”, The Jour. Of Hygienic Chem. 16, 258-66 (1970).

45. U.S. Environmental Protection Agency, “IERL-RTP

Procedures Manual: Level 1, 2nd Ed., Interagency Energy/Environment R&D Program Report”, EPA-600/7-78-201, Industrial Environmental Research Laboratory, Research Triangle Park, NC 27711.

46. Whitaker, J.W., Chakravorty, R.N. and Ghosh, A.K.,

“Oxygen Determination by combustion in a Bomb”, J. Sci. Ind. Research (India) 15B, 72-7 (1956).

47. Wreath, A.R., J. Assoc. Official Agr. Chemists, 31, 800

(1948). 48. Zhokovskaya, M.D., “A New Method for the

Determination of Hydrogen in Solid Fuel by Combustion in a Bomb Calorimeter”, Chem. Zentr. II. 952-3 (1947).

Page 8: 207M, Analytical Methods for Oxygen Bombs

PARR INSTRUMENT COMPANY 211 Fifty Third Street Moline, Illinois 61265 Phone 800 872 7720 Fax 309 762 9453

www.parrinst.com email [email protected]

Rev. 07/04