KGS Home Geology Home

Kansas Geological Survey, Bulletin 47, pt. 2, originally published in 1943


Kansas Oil Field Brines and their Magnesium Content

by Walter H. Schoewe

with chemical analyses by R. Q. Brewster and Calvin Vander Werf

Cover of the book; tan paper with black text.

Originally published in 1943 as Kansas Geological Survey Bulletin 47, pt. 2. This is, in general, the original text as published. The information has not been updated. An Acrobat PDF version (6.3 MB) is also available.

Abstract

This report is a brief study of the Kansas oil field brines, especially as related to their magnesium content: It has been known in a general way that some of the Kansas oil field brines have magnesium content greater than that of sea water from which, in recent years, metallic magnesium is being extracted successfully on a commercial scale. Similarly, metallic magnesium is also being extracted from oil field brines in Michigan. The chief purpose of the investigation was to ascertain the chemical nature of the waste brines, which are now very expensive to dispose of, and to determine whether metallic magnesium, an essential strategic material for war purposes, might not be extracted from these brines. During the summer of 1942 brine samples and other pertinent data were collected from 79 of the major and more important oil fields in the state. The brines were analyzed in the chemical laboratories at the University of Kansas.

On the basis of the analyses, at least six oil-producing formations (Layton, Stalnaker, Kansas City-Lansing, Hoover, Topeka, and Peru pay zones) have an average magnesium content greater than that of ordinary sea water. Certain other formations, such as "chat," Bartlesville, "conglomerate," and Simpson ("Wilcox") formations, yield brines essentially the same in their magnesium content as sea water. The "Mississippi lime," Gorham, Viola, "Hunton," and Arbuckle formations are deficient in this ingredient. The report includes tables giving the complete analyses of the brines studied.

The report includes a brief description of metallic magnesium and its compounds including their occurrences, uses, and derivation from oil field brines. Sources of required processing materials, costs, and prices of magnesium and its compounds are briefly outlined.

After discussing the factors controlling the commercial practicability of recovering magnesium from oil field brines, the report concludes with an analysis of Kansas oil fields worthy of consideration for magnesium recovery and recommended for further detailed study. The Kansas oil fields most worthy of consideration on the basis of data on hand are: Burrton field, Reno county; Bornholdt field, McPherson county; Zenith field, Stafford and Reno counties; Welch field, Rice county; Hall-Gurney field, Russell county; and Oxford field, Sumner county.

The present studies indicate that metallic magnesium extraction from oil field brines as a new and specialized industry in Kansas is not feasible. The information at hand does, however, suggest strongly that more detailed study may show the practicability of extracting magnesium from the brines as an auxiliary phase of the oil industry, to the extent of offsetting the high cost of brine disposal. This applies especially to the Burrton oil field in Reno county.

Introduction

The presence of magnesium in oil field brines and the increasing usefulness of metallic magnesium as an essential strategic material for war purposes have prompted the State Geological Survey of Kansas to investigate the possibility of using the oil field brines of the state as a source of metallic magnesium. It has been known in a general way that some of the Kansas oil field brines have a magnesium content greater than that of sea water from which, in recent years, metallic magnesium has been commercially extracted at Freeport, Texas. Magnesium is also being extracted from oil field brines in Michigan and western Texas (Pawell, 1942, p. 331). Vast amounts of salt water or brine are produced annually along with the oil. At present, the brines are considered only a bothersome and expensive waste, the disposal of which constitutes one of the major problems of the oil operators. Oil field brine disposal is subject to regulations defined by statute. Brines must be disposed of without polluting surface streams, contaminating or mineralizing domestic underground water supplies, damaging soil, or killing vegetation.

Oil field brines in Kansas are disposed of legally in two general ways: (1) impounding it on the lease and (2) injecting the brine into subsurface formations at designated disposal wells. Occasionally, some brine is released directly on the surface, where it either penetrates into the soil, evaporates, or drains off into surface streams.

In any case, the disposal of the brine is bothersome. Furthermore, no mineral matter has as yet been salvaged from it; therefore, its disposal has been an expensive item in the cost of operating an oil lease or oil field. Because Kansas oil field brines contain mineral matter of economic wartime importance, the present investigation was inaugurated as part of the program of the State Geological Survey in the war effort.

The investigation for ascertaining the magnesium content of Kansas oil field brines and the possibility of extracting the mineral for wartime purposes was under the direction of R. C. Moore, State Geologist, and John C. Frye, Assistant State Geologist. The geological part of the project was assigned to Walter H. Schoewe, staff geologist. The chemical analyses were made by R. Q. Brewster, chemical consultant to the Geological Survey and professor of Chemistry at the University of Kansas, who was assisted by Calvin Vander Werf, assistant professor of Chemistry at the University of Kansas.

Scope of the Survey

Oil pools investigated

The present investigation covers the entire oil-producing sections of Kansas (fig. 1). It was impossible, however, because of limited time, to collect brine samples and other pertinent data from every oil pool in the state. Samples of brine were collected from practically all of the major and more important oil pools in western Kansas. Less time and effort were devoted to the eastern oil fields because of their declining production and also because of the greater difficulty in obtaining good and reliable brine samples. In all, 79 oil fields were visited. The names of the oil pools from which samples were obtained are indicated in table 1.

Figure 1—Map of Kansas showing location of oil and gas fields. After Raymond P. Kercher.

Map of Kansas showing location of oil and gas fields.

Table 1—Oil pools from which brine samples were collected

Pool County Samples Pool County Samples
Agard Greenwood 1 Hittle Cowley 2
Ainsworth Barton 2 Johnson McPherson 1
Atherton Russell 1 Keesling Rice 2
Augusta Butler 2 Kraemer Butler 1
Augusta, North Butler 2 Kraft-Prusa Barton 4
Beaumont Greenwood 2 Lorraine Ellsworth 2
Bemis Ellis 2 Madison Greenwood 2
Bloomer Ellsworth, Barton 4 Miami Miami 5
New Albany Elk 1 Oxford Sumner 5
Bornholdt McPherson 3 Padgett Sumner 1
Browning Greenwood 1 Peabody Marion 1
Burnett Ellis 1 Peace Creek Reno 1
Burrton Reno 4 Potwin Butler 2
Chase Rice 4 Rainbow-Bend Sumner 1
Cunningham Pratt 4 Ritz-Canton McPherson 8
Demalorie-Sowder Greenwood 1 Russell Russell 2
Eastman Cowley 1 Sallyards Greenwood 1
Edwards Ellsworth 2 Sedan Chautauqua 1
Elbing Butler 4 Seeley Greenwood 2
Eldorado Butler 6 Sellens Russell 1
Eureka Greenwood 1 Severy Greenwood 1
Fairport Russell 2 Shutts Ellis 1
Fairport-Austin Russell 1 Silica Rice, Barton 5
Fairport-North Russell 1 Sperling Harvey 1
Florence Marion 1 St. John Stafford 1
Foxbush Butler 1 Stafford Stafford 1
Frog-Hollow Cowley 1 State Cowley 1
Garden-Schaffer Butler 2 Stoltenberg-Stratman Ellsworth 3
Geneseo Rice 3 Trapp Barton, Russell 4
Goodrich Sedgwick 4 Trapp, North Russell 1
Gorham-East Russell 5 Valley Center Sedgwick 3
Gorham-West Russell 2 Virgil-North Coffey, Greenwood 2
Graber McPherson 2 Virgil-West Greenwood 1
Graham Cowley 5 Voshell McPherson 2
Greenvale Russell 1 Welch Rice 2
Greenwich Sedgwick 3 Wellington Sumner 1
Hall-Gurney Russell 6 Wherry Rice 2
Halstead Harvey 2 Wherry-East Rice 2
Hinchman Greenwood 1 Winterscheid Woodson 2
      Zenith Reno, Stafford 4

Geologic formations from which samples were obtained

Brine samples were collected from all of the important oil-bearing formations. Table 2 gives, in chronological sequence, the names of the oil-bearing formations or "pay zones" sampled, together with the number of samples obtained from each.

Table 2—Producing formations and number of samples collected

Formation Samples
Tarkio 2
Topeka 4
Hoover 1
Stalnaker 1
Kansas City-Lansing 28
Peru 2
Cherokee, top 1
Bartlesville (New Albany) 14
Gorham 4
"Basal conglomerate" 4
"Chat" 18
"Mississippi lime" 8
"Hunton" 3
Viola 12
Simpson ("Wilcox") 16
Arbuckle ("Siliceous lime, dolomite") 51

Method of collecting samples

Effort was made to collect brine samples representative of the entire oil field. The number of samples collected in any given field depended upon the size of the oil pool and the type of method used in disposing of the salt water. In the smaller fields, one or two samples were normally considered sufficient. In the larger fields, however, effort was made to obtain samples from various parts of the oil pool—from the center and both ends. Where the pool was sufficiently wide, samples were also collected at both sides of the field. Where the field was unusually long, samples were collected approximately every 2 miles along the trend of the field. In cases, however, where the salt water was disposed of in deep disposal wells, one sample Was collected at each disposal well, regardless of the length or breadth of the field.

Quantitatively, one quart of brine constituted the normal sample. The brine was collected in glass Mason jars provided with glass covers or tops. Samples were obtained at the wells, usually under the supervision of a farm boss, pumper, or other official. Because of the different methods employed in disposing of the brine waters, the samples were collected from various sources. Some came from the bleeder at the well. Others were obtained at the gun barrel at the siphon, gun barrel gauge, or at the place where the brine coming from the gun barrel siphon emptied into the settling tank, or where the brine, after leaving the siphon, emptied into a pond. In a few cases the valve of the gun barrel had to be opened in order to secure the sample. In oil pools where the salt water was disposed of by means of deep disposal wells, the samples were either collected at the bleeder of the well or at the place where the brine emptied into the settling tank or pit just previous to its entry into the well. In one or two cases, the sample was drawn off from the bottom of the oil storage tank.

The following oil companies and operators cooperated in the project: Aladdin Petroleum Corporation, Amerada Petroleum Corporation, Nate Appleman, Atlantic Refining Company, Aylward Production Company, Barnsdall Oil Company, Bay Petroleum Company, Beardmore Drilling Company, Inc., Beaumont Petroleum Company, H. C. Bennett, Bennett-Wolf, F. Berger, Big Brothers Oil Company, B. B. Blair, Bridgeport Machine Company, British-American Oil Producing Company, Carter Oil Company, Central Supply Company, Cities Service Oil Company, Colorado Petroleum, Inc., Conley and Cooper, Continental Oil Company, Darby Petroleum Company, Deep Rock Oil Corporation, Derby Oil Company, Dickey Oil Company, Drillers Gas Company, El Dorado Refining Company, Goldstein Company, Gulf Oil Corporation, J. J. Hall, Herndon Drilling Company, Carl Hipple, T. C. Johnson (Estate), Jones-Shelburne, A. Landon, Leader Oil Company, Leader Oil Company-Zephyr Drilling Company, Magnolia Petroleum Company, M. & L. Oil Company, Maxwell Petroleum Company, W. C. McBride, Inc., Ward McGinnis, McPherson Drilling Company, L. R. Mendenhall, Mid-Continent Petroleum Corporation, Mohawk Oil Company, National Refining Company, Ohio Oil Company, OKO Oil and Gas Company, Olson Drilling Company, Oskaloosa Oil and Gas Company, Palmer Oil Company, Phillips Petroleum Company, S. J. Polhamus (Estate), Prunty Production Company, Pryor and Lockhart, Inc., Santa Clara Drilling Company, Shaffer-Howell, E. B. Shawver, Shell Oil Company, Sinclair-Prairie Oil Company, Skelly Oil Company, Snowden and McSweeney, Solar Oil Corporation, L. Spencer, Stanolind Oil and Gas Company, State Training School, Sunray Oil Company, The Texas Company, Tidewater Oil Company, Transwestern Oil Company, White Star Oil, and York State Oil Company.

Acknowledgments

The present investigation for determining the magnesium content of the State's natural salt water or brines associated with the production of oil would have been impossible without the wholehearted and gracious cooperation of the various oil companies and operators. Although space does not permit the listing of the names of the many farm bosses, pumpers, and other employees of the various oil companies and operators, I wish to express my sincere thanks to them for their courteous and willing aid in helping me to obtain the brine samples and other pertinent data requested. The names of the oil companies and operators cooperating in this project are listed elsewhere in this bulletin. Special gratitude is due to the Cities Service Oil Company for providing me with office space at Oil Hill in the Eldorado district and also for permitting me to study certain data in the files.

I also wish to express my appreciation to Ogden S. Jones, geologist of the Oil Field Section, Division of Sanitation, Kansas State Board of Health, for making it possible for James Nelson, field geologist of the southern district of the same Oil Field Section, to accompany and assist me for several days in the field in collecting the first suite of samples and in obtaining the necessary information relative to them. Thanks are also due Paul Hollands, field geologist for the Great Bend district of the Conservation Division of the Kansas State Corporation Commission, for certain data relative to the project. I wish to express my thanks to John M. Jewett, geologist of the State Geological Survey, who collected five samples from Miami county. Lastly, I thank John C. Frye, Assistant State Geologist, under whose direct supervision the project was carried out, for his interest in the work and for his timely suggestions relative to the writing of this report; R. Q. Brewster for checking chemical data and for his suggestions relative to table 5 through 14; and Dorothea Weingartner for editorial assistance.

Magnesium and Kansas Oil Field Brines

Chemistry of Kansas Oil Field Brines

Chemical analyses of Kansas oil field brines show that the brines, irrespective of the oil fields and "pay zones" or horizons from which they come, are essentially alike in the dissolved chemical constituents that they contain, but that they differ materially as to their concentration. The analyses show that of all the dissolved chemical constituents contained in the brines, chloride, sodium, and calcium greatly predominate (table 3). Magnesium is next in importance quantitatively. Other elements present but occurring in much lesser amounts are bromine, iodine, aluminum, iron, and potassium. Magnesium, of all the chemical constituents contained in the brines, is of the greatest importance at the present time. It is the only one which occurs in sufficient amounts to offer possibilities of commercial extraction under present conditions. Other ingredients, such as sodium and calcium, occur in far greater amounts than does magnesium; but, since these substances may be obtained much more readily from other sources, their extraction from brines in Kansas is unwarranted and unprofitable. Studies show that certain formations are invariably higher in magnesium content than brines coming from other "pay zones" or oil-producing formations (table 4).

Table 3—Dissolved chemical constituents of Kansas oil field brines with range in milligrams per liter

Chemical
constituents
Range
Total solids 17,880-228,320
Chloride 10,729-142,547
Sodium 9,200-68,700
Calcium 246-7,900
Magnesium 153-3,960
Bicarbonate 12-869
Bromide 0-425
Iodide 0-8
Sulphate 0-2,800
Aluminum 0-781
Iron 0-15

Table 4—Magnesium content of Kansas oil field brines

Formation Magnesium in milligrams per liter Samples
represented
Range Average
Layton   3,960 1
Stalnaker   2,620 1
Kansas City-Lansing 972-3,910 2,525 31
Hoover   2,515 1
Topeka   2,400 1
Peru 1,840-2,610 2,225 2
"Chat" 704-2,460 1,461 19
Bartlesville 461-2,490 1,223 16
"Conglomerate" 750-1,455 1,184 4
Simpson ("Wilcox") 235-2,035 1,033 8
"Mississippi lime" 432-1,857 772 8
Gorham 450-1,030 701 3
Viola 185-1,547 584 14
"Hunton" 153-1,138 523 5
Arbuckle 152-3,110 523 52
Sea Water 1,045 (Jones, 1943, p. 18); 1,279 (Burnett, 1942, Table II); 1,400 (Frye, 1942, p. 105).

According to the analyses, practically every oil-producing formation in Kansas yields, in some well or wells, brines containing magnesium in amounts greater than is contained in ordinary sea water. However, in most cases the magnesium content is much lower than that of sea water. The highest magnesium bearing brine is found in the Kansas City-Lansing zone. Not only does this zone produce the highest magnesium salt water, but it does so persistently in all wells and in all oil fields. The Arbuckle limestone, on the other hand, is prevailingly low in magnesium, with an average content less than 500 milligrams per liter. Even this formation, however, occasionally yields a brine high in magnesium. An Arbuckle brine obtained from a well in sec. 24, T. 11 S., R. 18 W., in the Burnett oil field, Ellis county, contained 3,110 milligrams of magnesium per liter.

Not only is there a difference in the magnesium content of the brines of the various oil-producing formations, but there is also a quantitative variation of this ingredient in anyone given formation. The magnesium concentration varies from one part of a field to another and also among the various oil fields. Variations among fields, as well as complete chemical analyses of the brines; are given in tables 5 through 14.

[Note: All chemical analyses in milligrams per liter. To convert to parts per million, divide by specific gravity of the brine. * denotes a concentration of less than 1 milligram per liter; ‡ denotes a concentration of less than 25 milligrams per liter; † denotes analyses supplied by private companies; all other analyses were made by R. Q. Brewster and Calvin Vander Werf at the University of Kansas.]

Table 5—Kansas City-Lansing brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Severy Greenwood 17 28 11E 60 1225 Pond 1.098 164 2208 47600 6550 93905 102 60 15 * 150400
Madison Greenwood 5 23 11E - 1060 - - 1351 33812 3443 63333 76 109 - - - 12 103700
Madison Greenwood 15 22 11E - 1310 - - 1585 34366 3838 65333 67 113 - - - 12 106500
Teeter Greenwood 16 23 9E - 1515 - - 1785 40773 4739 78330 68 109 - - - 94 128200
Teeter Greenwood 16 23 9E - 1915 - - 1593 41852 5382 80330 70 106 - - - 84 131400
Eldorado Butler 21 25 5E - 1743 - - 2540 55690 8203 107783 41 48 - - - 42 174400
Eldorado Butler 29 25 5E - 1970 - - 3550 51483 14927 116032 50 130 - - - - 186800
Augusta Butler 35 27 4E little 2300 Pond 1.121 131 3410 53500 9050 131328 72 105 5 210 * 197700
Augusta Butler 17 28 4E - 2060 - - 2974 58491 9533 115764 36 38 - - - 67 186900
Augusta Butler 29 28 4E - 2140 - - 2774 63020 8585 122500 128 38 - - - 17 199700
North Augusta Butler 11 27 4E 80 2200 Pond 1.106 130 2670 55200 8040 101534 150 108 50 8 320 * 177100
Elbing Butler 17 23 4E 20 2160 Pond 1.110 122 2262 55100 7200 107479 50 84 60 5 * 172200
Graham Cowley 10 33 3E 40 2500 Pond 1.150 139 2940 77000 12480 145105 12 100 3 * 237600
Hillsboro Marion 20 20 2E - 1980 - - 2569 53564 6050 103000 71 - - - 53 168000
Goodrich Sedgwick 15 25 1E 20 2626 Pond 1.150 30 3910 71380 10900 145860 33 375 2 895 2 233400
Silica Rice 27 19 10W 30 3200 Pond 1.108 57 3492 52420 8085 109806 82 130 * 864 * 174900
Bloomer Ellsworth 31 17 10W 30-40 3070 Pond 1.100 66 2705 49290 8965 98040 113 155 * 461 * 161300
Kraft-Prusa Barton 17 16 11W 50 - Pond 1.097 73 2690 42860 9610 92540 50 90 200 15 464 3 148200
Cunningham Pratt 35 27 11W 20 3450 Pond 1.158 174 3351 75600 14000 156749 48 110 15 166 1 250000
Cunningham Pratt 25 27 11W little 3450 Pond 1.150 176 2441 67400 16000 145855 175 * 115 10 84 80 232200
Cunningham Pratt 24 27 11W little 3450 Pond 1.159 175 2810 75000 14730 156203 75 6 105 15 360 16 249300
Greenvale Russell 4 15 12W - 3100 Pond 1.088 105 2685 41500 8440 89300 110 30 * 93 2 142200
Hall-Gurney Russell 31 14 13W 5 2950 pond 1.114 92 3075 55300 11100 117825 200 48 70 10 51 1 187700
Hall-Gurney Russell 26 14 13W 8-30% 2800 Pond 1.072 94 2420 38400 7000 80970 100 120 110 * * 129100
Hall-Gurney Russell 22 14 14W 32 2950 Pond 1.112 97 3240 53300 11200 117733 50 36 145 5 50 1 185800
Gorham, East Russell 2 14 15W - 3050 Deep well 1.040 78 1015 16940 2540 34130 275 96 30 3 64 20 55000
Gorham, West Russell 4 14 15W 150 3050 Pond 1.040 81 972 17590 2560 34590 400 448 25 * * 56600
Fairport-Austin Russell 31 12 15W 75 3000 Pond 1.075 83 2200 34620 6420 73030 250 48 40 10 138 64 115200
Fairport Russell 30 12 15W little 3000 Pond 1.095 84 2580 44675 9300 96660 75 48 95 5 402 2 152600
Fairport Russell 8 12 15W 5-10 3025 Pond 1.100 85 2240 50760 5670 94940 600 84 125 3 68 * 154200
Fairport North Russell 32 11 15W 30 3000 Pond 1.095 86 2760 43870 8620 92980 100 66 60 2 255 3 148700

Table 6—Bartlesville brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Shambaugh Greenwood 15 23 13E 700 1565 Deep well 1.040 155 712 19900 1980 32059 50 232 25 2 * 55000
Seeley Greenwood 32 22 11E 1000 2000 Pond 1.045 160 703 21675 2660 41172 168 20 2 * 66400
Madison Greenwood 14 22 11E 2 1900 Pond 1.052 156 900 25150 3065 49223 180 40 2 * 78600
Madison Greenwood 14 22 11E - 1900 - - 632 28629 3694 52830 491 88 - - - 13 87200
Madison Greenwood 12 22 11E 50 1800 Pond 1.060 157 1078 28800 3660 56876 84 20 2 * 90500
Demalorie-Sowder Greenwood 12 22 10E 2 2000 Pond 1.063 158 1093 29750 4400 61051 6 75 2 81 62 96500
Browning Greenwood 30 22 10E 30 2300 Pond 1.068 159 1122 33150 4415 63875 100 54 60 5 129 10 102900
Teeter Greenwood 16 23 9E - 2540 - - 863 26715 3316 50000 14 61 - - - 99 81700
Sallyards Greenwood 1 26 8E little 2400 Deep well 1.079 167 1187 34400 6160 77890 50 72 20 8 48 5 119800
Eastman Butler 6 31 6E 85 2850 Pond 1.100 133 1330 52000 5600 98098 54 40 5 190 3 157300
Garden-Schaffer do. 6 27 6E 100 2750 Pond 1.102 126 1564 51100 7460 100184 75 96 150 3 87 1 160700
Frog-Hollow Cowley 20 32 5E 50 3000 Pond 1.140 134 2060 46000 14680 165494 50 18 60 * 230 8 228600
Fox-Bush Butler 26 28 5E 100 2800 Pond 1.095 132 1910 47400 6820 92396 400 36 20 2 293 3 149300
Haverhill Butler 27 27 5E - 2774 - - 1464 47095 7100 90000 33 84 - - - 36 146500
Augusta Butler 16 28 4E 400 2550 Pond 1.030 117 461 11900 1830 23659 750 210 110 * * 38900
Rainbow-Bend Sumner 21 33 3E 100 3200 Pond 1.141 141 2490 69600 12120 141167 50 12 130 2 302 7 225900

Table 7—"Conglomerate" brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Wherry Rice 6 21 7W little 3400 Pond 1.070 24 1190 34830 5100 66951 74 175 * 33 4 108400
Wherry Rice 12 21 7W 40 3469 Pond 1.090 15 1455 46600 6050 89412 27 425 * 440 10 144700
Wherry Rice 16 21 7W 20 3400 Pond 1.066 23 750 34520 5330 65570 84 270 * 57 6 106700
Wherry Rice 21 21 7W - - Pond 1.080 16 1340 40170 5700 67630 120 385 * 294 * 125600

Table 8—"Chat" brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Greenwich Sedgwick 14 26 2E 4000 2850 Deep well 1.072 37 1192 36420 4260 69000 86 10 8 223 * 111200
Goodrich Sedgwick 21 25 1E 600 3000 Pond 1.075 29 1110 36020 4050 62588 90 200 2 220 * 109200
Wellington Sumner 4 32 1W 20 3690 Pond 1.143 147 1950 66500 13480 137652 2200 30 190 2 781 15 222800
Ritz-Canton McPherson 19 19 1W 300 2900 Pond 1.079 44 704 40560 4070 72578 50 73 45 2 * 117960
Ritz-Canton McPherson 29 19 1W 80 2960 Pond 1.071 41 1182 37270 3940 69010 59 170 * 130 * 111760
Ritz-Canton McPherson 25 19 2W 360 2970 Deep well 1.075 42 1101 37470 3980 69560 89 70 3 113 10 112160
Ritz-Canton McPherson 36 19 2W 120 3000 Pond 1.068 43 859 35380 3624 64610 64 58 * 121 * 104720
Halstead Harvey 2 23 2W 3000 3000 Deep well 1.070 2 794 34770 3350 61700 130 150 * 142 2 101250
Halstead Harvey 12 23 2W - 2980 Pond 1.070 1 980 33110 3480 63310 122 110 2 * 101400
Johnson McPherson 30 19 3W 60-70 3100 Pond 1.087 48 1491 43980 5720 83450 40 50 * 38 * 134720
Burrton Reno 15 24 4W 4000 3400 Deep well 1.115 8 2180 66652 9200 129015 60 247 * 525 1 207880
Burrton Reno 10 24 4W - - Pond 1.128 9 2460 75264 10600 143862 84 110 * * 232380
Burrton Reno 23 23 4W - - Deep well 1.110 10 2140 58720 8620 113200 48 395 * * 183220
Burrton Reno 1 23 4W - 3500 Pond 1.119 11 2270 67370 9510 128240 50 94 130 * * 207620
Bornholdt McPherson 31 20 5W - 3333 Deep well 1.098 12 1510 57942 7370 109290 40 46 310 * 335 3 176850
Bornholdt McPherson 29 20 5W 550 3350 Deep well 1.090 13 1630 46400 7040 89316 33 420 * * 146840
Bornholdt McPherson 18 20 5W 300 - Pond 1.085 14 1410 38900 6100 91140 40 90 * 208 4 137880
Welch Rice 3 21 6W 1700 3410 Deep well 1.105 6 1230 53568 7800 103324 40 150 * 540 8 166660
Welch Rice 2 21 6W 1000 2350 Deep well 1.100 7 1560 51197 7450 101420 46 100 * 900 7 162680

Table 9—Mississippi lime brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Stephenson Woodson 7 24 14E 25 1700 Pond 1.037 152 514 16500 2340 32107 125 264 20 * 49 1 51900
Winterschied Woodson 29 23 14E 12 1700 Pond 1.050 153 458 24200 1890 43105 104 10 2 20 11 69800
Hinchman Greenwood 20 24 13E 200 1600 Pond 1.036 150 641 16700 1765 29415 450 342 * 2 58 1 50000
Blackwell Greenwood 10 24 13E 100 1659 Pond 1.033 151 600 15050 1630 28484 550 396 10 * * 46700
Virgil-North Coffey 14 23 13E 25 1700 Pond 1.025 154 432 11050 1117 20677 150 444 10 * * 33900
Virgil Greenwood 11 24 12E 200 1750 Deep well 1.037 168 700 16700 2180 32441 254 5 * * 52300
Eureka Greenwood 36 25 10E 20 2000 Pond 1.050 163 971 22500 2830 43673 246 20 * * 70200
Beaumont Greenwood 25 27 8E 30 2510 Pond 1.091 165 1857 44550 6780 89009 175 96 10 3 * 142500

Table 10—Hunton brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Peabody Marion 15 22 4E 6097 2510 Pond 1.015 124 153 5760 710 10982 225 330 * * * 18200
Elbing Butler 20 23 4E 3748 2370 Pond 1.020 120 320 8500 990 16195 725 300 10 * * 27000
Graber McPherson 20 21 1W 1200 3300 Deep well 1.044 38 751 21090 2327 40090 96 * * 133 3 64300
Graber McPherson 32 21 1W - 3300 Deep well 1.075 39 1138 36590 4149 68430 67 * 2 182 * 110600
Sperling Harvey 13 22 2W 60 3305 Deep well 1.031 3 253 14150 1260 25000 100 120 65 * * 41300

Table 11—Viola brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Garden-Schaffer Butler 4 27 6E 400 3100 Pond 1.031 127 516 13200 1800 25720 700 264 * * * 42200
Eldorado Butler 4 26 5E 15 2650 Pond 1.048 108 1170 22500 3140 44656 375 24 15 * * 71900
Eldorado Butler 17 26 5E Much 2600 Pond 1.040 112 864 18600 2640 36715 500 396 5 * * 59700
Florence Marion 18 21 5E - 2300 Pond 1.017 125 228 5670 616 10729 325 312 * * * 17900
Elbing Butler 17 23 4E - 2350 - - 371 5399 909 10000 1178 301 - - - 24 18100
Elbing Butler 17 23 4E 150 2400 Pond 1.018 123 248 6600 870 12766 300 246 10 * * 21000
Greenwich Sedgwick 14 26 2E 4000 3100 Deep well 1.020 36 204 7800 755 14320 501 * * * 23600
Hillsboro Marion 28 20 2E - 3037 - - 271 5284 597 10000 15 79 - - - - 16400
Ritz-Canton McPherson 20 19 1W ** 3000 Deep well 1.030 40 404 11980 1803 22990 75 233 15 * * 37400
Ritz-Canton McPherson 17 19 1W 800 3387 Pond 1.030 46 353 11980 1619 22520 65 175 10 * * 36700
Ritz-Canton McPherson 11 19 2W 35 3300 Pond 1.020 45 185 9280 1191 17111 55 322 15 * * 28200
Peace Creek Reno 22 23 10W - - Pond 1.035 22 640 16720 1670 30918 650 15 * 65 * 50700
Cunningham Pratt 12 28 11W 20 4250 Pond 1.095 177 1547 46500 7900 83852 175 12 90 8 110 6 140200
Stafford Stafford 15 24 12W - 3800 - 1.065 20 1140 30100 5540 60500 210 65 * 91 * 97600
** Several hundred.

Table 12—Simpson (Wilcox) brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Padgett Sumner 26 34 2E 30 3500 Pond 1.140 140 2035 68500 14400 142547 300 18 105 3 407 5 228300
Greenwich Sedgwick 15 26 2E 300 3000 Deep well 1.020 35 288 8360 789 15990 90 530 * * * 26000
Valley Center Sedgwick 1 26 1E 140 3390 Deep well 1.040 32 628 17830 1900 32965 90 250 80 * * 53600
Ritz-Canton McPherson 21 19 1W 75 3440 Pond 1.015 47 235 5560 892 10874 80 184 * * * 17700
Zenith Reno 7 24 10W - 3607 Pond 1.055 17 1150 26170 4150 51533 230 45 * * 83300
Zenith Stafford 14 24 11W - - Deep well 1.065 21 1450 31290 5260 63860 204 75 * 350 1 102700
Zenith Stafford 15 24 11W 200 3600 Pond 1.075 18 1515 36080 5900 71000 72 345 * * 114900
Zenith Stafford 23 24 11W - 3600 Pond 1.050 19 985 20745 3220 29410 335 70 * 47 1 76400

Table 13—Arbuckle brine data with chemical analyses

Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Beaumont Greenwood 25 27 8E 100 2750 Pond 1.045 166 674 19000 3050 38034 325 312 5 * * 61400
Eldorado Butler 5 26 5E 400 2450 Deep well 1.028 109 408 10000 1635 20153 650 264 10 * * 33100
Eldorado Butler 15 25 5E - 2500 - - 313 11054 1398 19330 1357 322 - - - 25 33700
Hittle Cowley 28 31 4E - 3300 Pond 1.043 115 519 15440 2070 30000 450 606 35 * * 49100
State Cowley 15 32 4E 300 - Pond 1.055 114 835 24650 3720 48706 700 294 15 * * 78900
Graham Cowley 9 33 3E 375 3500 Pond 1.067 136 1050 30900 4130 59558 400 252 30 * * 96300
Graham Cowley 10 33 3E 400 3500 Pond 1.064 137 1263 29200 4130 57142 400 270 15 * * 92400
Graham Cowley 10 33 3E 800 3500 Pond 1.073 138 1263 34450 5170 67655 750 252 20 * * 109600
Voshell McPherson 9 21 3W 350 3395 Pond 1.028 5 380 12378 1550 22963 50 404 55 * * 37800
Lorraine Ellsworth 23 17 3W 500-1000 3260 Deep well 1.024 62 366 10320 1430 19350 275 522 15 * * 32300
Geneseo Rice 19 18 7W - - Deep well 1.018 26 320 7150 1260 14220 - 245 10 * * 23200
Geneseo Rice 6 19 7W - - Pond 1.014 25 237 6990 835 12832 - 576 10 * * 21500
Geneseo Rice 12 18 8W - - Pond 1.025 27 340 10430 1760 20280 - 505 5 * * 33300
Edwards Ellsworth 27 17 8W 240 3200 Pond 1.033 60 505 13440 2205 25970 350 427 10 * * 43000
Edwards Ellsworth 33 17 8W 150-200 3250 Deep well 1.024 59 246 8460 1562 16413 400 512 5 * * 27200
Lorraine Ellsworth 11 17 9W - 3216 - - 152 6260 400 10660 35 476 - - - 1 18000
Lorraine Ellsworth 23 17 9W Much 3200 Pond 1.024 61 188 6120 657 11070 - 632 20 * * 18700
Chase Rice - 19 9W 800-1000 3250 Deep well 1.020 54 209 7360 647 14370 - 579 5 * * 21800
Chase Rice 21 19 9W 385 3250 Deep well 1.017 53 288 7520 994 14090 - 507 5 * * 23400
Chase Rice 5 20 9W 1500 3250 Deep well 1.020 52 299 7540 1304 14650 75 411 5 * * 24300
Chase Rice 18 20 9W 360 3380 Pond 1.020 51 227 6660 860 12310 70 510 5 * * 20600
Chase Rice 19 20 9W - 3384 - - 167 6484 917 11000 1340 351 - - - - 20200
Keesling Rice 10 20 9W 100 3230 Pond 1.020 49 273 8910 788 15830 55 577 5 * * 26400
Keesling Rice 16 20 9W 900 3260 Pond 1.018 50 229 7000 761 12700 - 507 - * * 21200
Silica Rice 33 19 10W 1224 3300 Deep-well 1.022 56 317 8690 1258 16550 80 344 - * * 27200
Silica Rice 34 19 10W - 3297 Pond 1.022 58 301 8180 1078 15280 500 519 5 * * 25400
Stoltenberg Ellsworth 1 17 10W 3000 3270 Pond 1.026 63 526 8750 2062 18820 625 394 25 * * 31200
Bloomer Ellsworth 31 17 10W 100 3240 Pond 1.020 65 281 7710 1190 14494 475 489 - * ~ * 24600
Bloomer Ellsworth 33 17 10W 6 3800 Pond 1.024 71 445 7780 1370 15380 675 264 10 * * 26000
Bloomer Ellsworth 36 17 11W 50 3280 Pond 1.031 67 649 14100 2360 27500 550 581 30 * * 44800
Silica Barton 1 20 11W 900 3200 Deep well 1.020 55 287 7900 1041 14916 - 181 - * * 24300
Silica Barton 12 20 11W 900 3300 Deep well 1.020 64 338 7980 1203 15030 525 497 25 * * 25600
Kraft-Prusa Barton 17 16 11W 240 - Pond 1.020 72 310 6330 1180 12515 - 696 10 " * 21300
Kraft-Prusa Barton 33 16 11W 115 3350 Pond 1.020 70 296 6950 1270 13365 525 605 10 * * 23000
Hall-Gurney Russell 24 14 13W 120 3200 Pond 1.027 95 600 10900 2095 23031 650 269 15 * * 37600
St. Johns Stafford 28 24 13W 15 4200 Pond 1.035 178 500 10230 2335 32207 2200 378 * * * 47900
Ainsworth Barton 33 16 13W 200 3400 Deep well 1.022 103 399 7790 1580 16537 450 444 * * * 27200
Ainsworth Barton 26 18 13W - 3380 Pond 1.022 102 340 8550 1595 17616 625 474 * * * 29200
Trapp Barton 8 16 13W 30% 3300 Pond 1.028 101 460 10850 1550 20360 250 690 * * * 34200
Trapp Barton 29 15 13W 300 3300 Pond 1.032 99 618 13050 2370 27042 180 660 * * * 43900
Sellens Russell 26 15 13W 350 3300 Deep well 1.029 100 618 11840 2260 26270 300 312 * * * 41600
Russell Russell 27 13 14W 100 3290 Deep well 1.024 75 316 8750 715 15550 250 498 5 * * 26100
Russell Russell 33 13 14W 70 3290 Pond 1.022 106 479 8800 1910 19060 300 532 - * - * 31100
Ochs Russell 24 15 14W - 3350 - - 425 12106 2142 22000 2227 501 - - - 31 39500
Trapp Russell 25 15 14W 100 3325 Pond 1.033 98 585 15050 2575 25763 160 588 * * * 44700
Trapp Russell 36 15 14W - 3400 Pond 1.028 104 545 12100 1690 23870 275 720 * * * 39200
Atherton Russell 30 13 14W 100 3200 Deep well 1.023 107 420 7400 1780 16449 325 786 * * * 27200
North Trapp Russell 8 13 15W 300 3000 Pond 1.032 96 708 12380 2470 26383 150 692 17 * * 42800
Beemis Ellis 12 11 17W 130 3350 Deep well 1.045 87 804 18400 3120 37430 125 294 35 * 107 5 60500
Beemis Ellis 14 11 17W 80 3396 Pond 1.044 88 766 17720 2660 35410 135 402 20 * * 57100
Shutts Ellis 5 12 17W 150 3600 Pond 1.037 90 615 15550 2500 31110 700 324 * * * 50800
Burnett Ellis 24 11 18W little 3150 Pond 1.115 89 3110 52000 10990 112670 75 144 77 * 248 6 179300

Table 14—Topeka, Hoover, Stalnaker, Layton, Peru, Gorham, and New Albany brine data with chemical analyses

Zone Pool County Location Brine
(bbls.
day)
Depth to
horizon
Disposal
method
Sp. Gr.
(60° F.)
Sample
number
Magnesium
(Mg)
Sodium
(Na)
Calcium
(Ca)
Chloride
(Cl)
Sulphate
(SO4)
Bicarbonate
(HCO3)
Bromide
(Br)
Iodide
(I)
Aluminum
(Al)
Iron
(Fe)
Total
solids
Sec. T. R.
Topeka Oxford Sumner 14 32 2E 75 1300 Deep well 1.140 145 2400 65000 9410 127530 2100 72 180 4 220 4 206900
Hoover Oxford Sumner 14 32 2E 75 1700 Deep well 1.140 146 2515 67500 9415 131874 1400 36 280 2 290 8 213300
Stalnaker Oxford Sumner 14 32 2E 870 2100 Deep well 1.155 142 2620 71100 11100 141072 24 120 2 710 12 226800
Layton Oxford Sumner 14 32 2E 100 2400 Deep well 1.158 144 3960 75000 11820 152162 72 180 2 321 3 243500
Peru Sedan Chautauqua 12 33 10E 50 1400 Pond 1.090 148 1840 40500 6910 82962 54 90 4 115 5 132500
Peru Hittle Cowley 24 31 4E little 2400 Pond 1.135 116 2610 68700 11300 138884 50 24 * * 371 5 221900
Gorham Hall-Gurney Russell 31 14 13W 30-40% 3300 Pond 1.024 93 450 10950 1150 19452 275 513 10 * * 32800
Gorham Gorham, East Russell 2 14 15W - 3250 Deep well 1.045 77 1030 17060 3960 35950 625 750 10 * * 59300
Gorham Gorham, East Russell 11 14 15W Much 3257 Pond 1.028 82 624 8300 1370 17075 50 841 5 * * 28400
New Albany New Albany Elk 3 29 13E 25 550 Creek 1.055 149 1750 26800 2880 51164 50 186 30 8 170 2 83000

Description, Occurrence, and Derivation of Metallic Magnesium

Description

Metallic magnesium is a silvery white metal of high tensile strength. It is the lightest of all the known metals that are comparatively little altered under ordinary atmospheric conditions. Its specific gravity is 1.74; its melting point is 633° C.; and its boiling point is 1120° C.

Occurrence

Magnesium occurs in nature only in the combined state and is one of the most common metals associated with rocks. It constitutes approximately 2.1 percent of the earth's crust; which makes it the eighth most abundant element or sixth most abundant metal.

Common magnesium-bearing minerals include magnesite, MgCO3; dolomite, CaMg(CO3)2; olivine, 2(MgFe)OSiO2; serpentine, H4Mg3Si2O9; epsomite (epsom salt), MgSO4 · 7H2O; brucite, and the Stassfurth salts of commercial importance—carnallite KMgCl3 · 6H2O; kainite, MgSO4 · KCl · 3H2O; kieserite, MgSO4 · H2O; and schoenite, K2SO4 · MgSO4 · 6H2O. In addition, other magnesium minerals are asbestos, meerschaum, spinel, tourmaline, chrondrodite, pyrope, biotite, phlogopite, chlorite, talc, sepiolite, garnierite, bradleyite, and some of the pyroxenes and amphiboles. Magnesium is also found in mineral waters, sea bitterns, sea water, and oil field brines.

Derivation, general

At the present time metallic magnesium is derived from the following minerals: magnesite, dolomite, epsomite, olivine, and serpentine. It is also obtained from chemically produced magnesia, or magnesium oxide in its various forms, magnesium chloride, magnesium sulphate, magnesium hydroxide, and magnesium silicofluoride. Today it is also extracted from ordinary sea water, bitterns, saline deposits, and oil field brines.

Derivation of metallic magnesium from oil field brines

Natural brines contain sodium chloride, calcium chloride, magnesium chloride, bromine, and other chemical constituents. The first step in obtaining metal magnesium, Mg; is to treat the brine with calcium hydroxide (calcined limestone or quicklime, CaO, or with calcined dolomite, CaO and MgO). As a result, magnesium hydroxide, Mg(OH)2, and calcium chloride, CaCl2, are formed. The magnesium hydroxide is then dissolved in hydrochloric acid, HCl, to form magnesium chloride, MgCl2, from which metallic magnesium and gaseous chlorine are derived by electrolysis. According to Gann (1930, p. 694), at the Dow Chemical Company's plant at Midland, Michigan, the bromine is first removed from the brine after which the brine is treated with a magnesium hydrate slurry to precipitate iron and any other impurities contained therein. After the sodium chloride has been removed by crystallization, the magnesium and calcium chlorides in the rotary-filter mother liquor are separated from each other by fractional crystallization, with addition of chlorine during the process. The purified magnesium chloride solution is concentrated further by crystallization. The crystals are melted in their water of crystallization, the fused mass flaked, and then air-dried until an almost anhydrous magnesium chloride, MgCl2, is produced. The magnesium chloride is then electrolyzed in a sodium chloride bath. The process is continuous, and the metal, which is of high purity, is periodically 'dipped from the rectangular cast-steel pots in which electrolysis occurs and cast into ingots of various sizes.

Although metallic magnesium is the end product sought, it may not be desirable, feasible, or practicable to extract the metal from the oil field brines at each recovery plant established. It may prove to be more advantageous merely to produce magnesium hydroxide, Mg(OH)2, dry it, and ship it elsewhere to be further processed. On the other hand, it may be desirable to further process the magnesium hydroxide to some specific magnesium product, such as "caustic," "calcined," or "dead-burned" magnesia, and then dispose of the product. Or the process may be carried on to completion until metallic magnesium is obtained. In the following pages a brief description is given concerning the processing of the more important magnesium compounds.

Magnesium hydroxide, Mg(OH)2

Regardless of what magnesium substance is desired at any oil field brine recovery plant, the first step consists in converting the contained magnesium chloride into magnesium hydroxide. This may be done by treating the magnesium chloride of the brine either with calcined limestone (quicklime, CaO), or with calcined dolomite, or with both. The chemical reactions represented by the first two processes are shown in the following equations:

1. MgCl2 + CaO + H2O = Mg(OH)2 + CaCl2.
magnesium chloride + lime + water = magnesium hydroxide + calcium chloride.

2. MgCl2 + CaO + MgO + 2H2O = 2Mg(OH)2 + CaCl2
magnesium chloride + lime + magnesia + water = magnesium hydroxide + calcium chloride

The magnesium hydroxide, Mg(OH)2, is an amorphous substance that is more than twice as heavy as metallic magnesium. It may be shipped to other plants for further processing or it may be further treated at the recovery plant, as outlined in the following pages.

Magnesium oxide or magnesia, MgO

The basic magnesium hydroxide when calcined or dehydrated is converted into magnesium oxide, MgO, which is a white powder, very soft and light. Commercially it is known as magnesia. This chemical substance may be had on the market in various forms which depend upon the temperatures at which the magnesium hydroxide was calcined (table 15).

Table 15—Forms of magnesium oxide or magnesia and the temperatures at which they are formed

Product Temperature
(degrees C.)
"Caustic" magnesia 700-1,200
"Dead-burned" or sintered magnesia 1,400-1,560 (in presence of iron)
1,400-1,600 (absence of impurities)
Artificial periclase 1,700 and above
Magnesia brick 1,700 and above

The products in table 15 are also called "caustic" and "calcined magnesite." The chemical reaction involved in the formation of magnesium oxide from magnesium hydroxide is represented by the following chemical equation:

Mg(OH)2 + heat = MgO + H2O.
magnesium hydroxide + heat = magnesia + water

Magnesium chloride, MgCl2

Although magnesium is present in the brine chiefly in the form of the chloride; nevertheless, in order to obtain it, it is necessary first to convert the magnesium chloride into either the hydroxide or oxide as mentioned above and then precipitate magnesium chloride by dissolving the hydroxide or oxide in hydrocloric acid. The chemical reactions are as follows:

Mg(OH)2 + 2HCl = MgCl2 + 2H2O
magnesium hydroxide + hydrochloric acid = magnesium chloride + water

Magnesium chloride is the substance from which metallic magnesium is derived by electrolysis.

Magnesium chloride may be had commercially in the form of a hydrous crystalline salt, MgCl2 · 6H2O, as a partially dehydrated flaky material, and also in the anhydrous state.

Magnesium sulphate, MgSO4

Magnesium hydroxide or magnesium oxide treated with sulphuric acid results in the formation of magnesium sulphate, according to the following chemical reactions:

Mg(OH)2 + H2SO4 = MgSO4 + 2H2O
magnesium hydroxide + sulphuric acid = magnesium sulphate + water

MgO + H2SO4 = MgSO4 + H2O
magnesium oxide + sulphuric acid = magnesium sulphate + water

Magnesium sulphate is found in salt beds and in a number of hydrous varieties, chief of which is Epsom salt, MgSO4 · 7H2O. Epsom salt is a soft, highly soluble, colorless to white mineral having a bitter salty taste. It occurs commonly as granular, fibrous, or earthy masses. Kieserite, MgSO · H2O, kainite, MgSO4 · KCl · 3H2O, and schoenite, K2SO4 · MgSO4 · 6H2O, are other hydrous magnesium sulphate salts of commercial importance. These are associated with the world-famous Stassfurt salt deposits in Germany.

Magnesium carbonate, MgCO3

Magnesium carbonate, MgCO3, which occurs in nature in the form of the mineral magnesite, is produced chemically by treating magnesium chloride or magnesium sulphate with sodium bicarbonate.

MgCl2 + 2NaHCO3 = MgCO3 + 2NaCl + H2O + CO2
magnesium chloride + sodium bicarbonate = magnesium carbonate + sodium chloride + water + carbon dioxide

MgSO4 + 2NaHCO3 = MgCO3 + Na2SO4 + H2O + CO2
magnesium sulphate + sodium bicarbonate = magnesium carbonate + sodium sulphate + water + carbon dioxide

Magnesium carbonate is an infusible, glassy to earthy substance, colorless to white, yellow, brown, or blackish. It is brittle and breaks with a conchoidal fracture. In the form of the mineral, it usually occurs as a granular, compact, or unglazed porcelain-like earthy mass.

Magnesium silicate, 2H2Mg3Si4O12

Magnesium chloride or magnesium sulphate when treated with sodium silicate yields magnesium silicate, a substance in composition similar to that of the mineral talc, H2Mg3Si4O12. This substance is useful in various ways as indicated elsewhere in this report.

6MgCl2 + 8Na2SiO3 + 4H2O = 2H2Mg3Si4O12 + 12NaCl + 4NaOH
magnesium chloride + sodium silicate + water = magnesium silicate + sodium chloride + sodium hydroxide

6MgSO4 + 8Na2SiO3 + 4H2O = 2H2Mg3Si4O12 + 6Na2SO4 + 4NaOH
magnesium sulphate + sodium silicate + water = magnesium silicate + sodium sulphate + sodium hydroxide

Magnesium silicofluoride, MgSiF6

Magnesium hydroxide or magnesium oxide treated with hydrosilicofluoric acid yields a water soluble, white, crystalline powder known as magnesium silicofluoride.

Mg(OH)2 + H2SiF6 = MgSiF6 + 2H2O
magnesium hydroxide + hydrosilicofluoride = magnesium silicofluoride + water

MgO + H2SiF6 = MgSiF6 + H2O
magnesium oxide + hydrosilicofluoride = magnesium silicofluoride + water

Uses of Metallic Magnesium and its Compounds

Metallic magnesium, Mg

Metallic magnesium has been used largely as a deoxidizing and desulphurizing agent in the manufacture of alloys, especially aluminum. It is used in making castings for aircraft parts, such as crankcases, pistons, oil-pans, bearings, and control levers. It is used in the manufacture of motion picture machines, field glasses, microscopes, and surveying and other scientific instruments. Magnesium is an important ingredient in incendiary bombs, military flares, flashlight powders, pyrotechnics, tracer bullets, and shells. It is used in the making of optical mirrors, electric batteries, and numerous other articles.

Magnesium oxide or magnesia, MgO

Magnesium oxide or magnesia has been used extensively in making refractories and magnesia cements. It is also important in the manufacture of crucibles, furnace linings, and insulating and fireproofing compounds. Magnesia is an ingredient in face powder and toilet preparations, as well as in paints and varnishes. It is used in medicine and it is found in mineral waters.

Magnesium chloride MgCl2

Magnesium chloride is the substance from which, by electrolysis, metallic magnesium is derived. It is used in making hydrochloric acid, magnesia cements, stucco, flooring and fire-extinguishing compounds, and ceramic materials. It is also an ingredient in medicine. It has many other uses.

Magnesium sulphate, MgSO4

Like magnesium chloride, magnesium sulphate is used in ceramics, dyeing, and medicine. It is used in manufacturing printing ink, frosted paper, matches, motion picture snow, and explosives. It is used in fertilizers, tanning, sizing paper, and fireproofing and waterproofing textiles.

Magnesium carbonate, MgCO3

Magnesium carbonate is used largely in making refractories and, in general, fire-resisting materials. It goes into the making of cosmetics, tooth-paste, varnishes, paints, printing ink, fertilizers, linoleum, oilcloth, and many other substances. It is also used in medicine.

Magnesium silicate, 2H2Mg3Si4O12

Magnesium silicate is used in paints, lacquers, and varnishes, in ceramics, refractories, rubber compounding, and as an oil-bleaching agent.

Magnesium silicofluoride, MgSiF6

Magnesium silicofluoride is used in ceramics. It is also an ingredient in insecticides. It is employed in hardening and waterproofing concrete.

Sources of Required Processing Materials

Calcined limestone (quicklime), or calcined dolomite, and fuel are the basic raw materials needed in the extraction of magnesium compounds from oil field brines. The practicability of magnesium extraction is, therefore, directly related to the availability of these basic raw materials or to the cost of the substance to the producer at the processing plant. Fortunately, limestone, including chalk, is abundant in Kansas and, in most cases, is close to the oil fields (fig. 2). Dolomite, which could be used instead of limestone, is available in limited quantities in Rice, Reno, and Kingman counties, where the Stone Corral dolomite crops out, and in Clark county where the Day Creek dolomite occurs.

Figure 2—Map of Kansas showing location of areas of abundant limestone, chalk, and dolomite, basic raw materials needed in magnesium recovery from brines. After J. M. Jewett.

Map of Kansas showing location of areas of abundant limestone, chalk, and dolomite, basic raw materials needed in magnesium recovery from brines.

At the present time there are no lime kilns operating in the state, although in former years lime kilns were not uncommon. Calcined limestone or quicklime is manufactured, however, in connection with the making of Portland cement at six plants now operating in Kansas. The Portland cement plants are located mainly in eastern Kansas, not too distant from the oil fields, at Bonner Springs, Wyandotte county; lola and Humboldt, Allen county; Chanute, Neosho county; Fredonia, Wilson county; and Independence, Montgomery county (fig. 3). It is conceivable and not unreasonable that quicklime plants might easily be established in the chalk area of western Kansas close to the important oil fields of that part of the state.

Figure 3—Map of eastern Kansas showing location of Portland cement mills, possible sources for calcined limestone needed in the recovery of magnesium from brines. After J. M. Jewett.

Map of eastern Kansas showing location of Portland cement mills, possible sources for calcined limestone needed in the recovery of magnesium from brines.

Sufficient cheap fuel in the form of natural gas or fuel oil is available in most of the oil fields, or is within easy reach. In eastern Kansas, sufficient coal resources are at hand to replace the gas or oil for fuel if necessary. Apparently there is no necessity for shipping in from great distances the required processing materials, and certainly there is no need for shipping from outside of the state.

Costs

It is impossible to calculate the actual cost involved in establishing a plant designed to process the oil field brines for magnesium. In general, the cost of the brine should not be charged against the recovery of the magnesium when the brine is a waste product pumped up with the oil and when the extraction plant is operated in connection with oil production. The only legitimate cost involved, so far as the brine is concerned, is for pipe lines to be used in transporting the brine from a number of leases to a central recovery plant. In cases where brine is specifically produced as a raw material and is not related to oil production, the cost of drilling both brine well and disposal well, as well as producing and disposing of the brine, will necessarily have to be charged against the cost of recovering the magnesium. Burwell (1942) summarized the cost of a brine-treating plant as follows:

  1. Cost of construction of the brine-treating and magnesium recovery plant.
  2. Amortization of equipment and buildings.
  3. Cost of brine (if produced or purchased for extraction only).
  4. Cost of power, water, and fuel.
  5. Cost of labor.
  6. Overhead.

Other items involved are the cost of the quicklime or calcined dolomite-s-costs that are variable with location of the recovery plant and source of raw materials.

Prices of Magnesium and its Compounds

In 1942, metallic magnesium sold at 22% cents per pound, or at 450 dollars per ton. The price of other magnesium compounds in 1942, according to Burwell, are listed in table 16.

Table 16—Prices per ton of magnesium compounds in 1942

Magnesium oxide, powdered $58.75
Magnesium oxide, U. S. P. light $400.00
Magnesium oxide, heavy $500.00
Magnesium chloride, flake, 97% MgCl2 · 6H,O $32.00
Magnesium chloride, anhydrous $260.00
Magnesium sulphate, technical $36.00
Magnesium sulphate, U. S. P. $40.00
Magnesium carbonate, precipitated, technical $125.00
Magnesium carbonate, precipitated, U. S. P. $180.00
Magnesium silicofluoride, technical $400.00

Factors Affecting Magnesium Recovery from Oil Field Brines

The commercial practicability of recovering magnesium from oil field brines, aside from the cost of erecting and maintaining a recovery plant, is dependent upon several factors: (1) the magnesium content of the brine, (2) the amount of brine produced per well, (3) the total number of wells producing brine in the field, (4) the number of days per year the wells are producing, (5) the presence or absence of deep disposal wells, (6) the selling price of the recovered magnesium or its compounds, and (7) special chemical characteristics of the brine that would either inhibit or aid magnesium recovery.

At present, magnesium is being profitably extracted from ordinary sea water which has a magnesium content varying from 1,040 to approximately 1,400 milligrams per liter. Many of the Kansas oil field brines (tables 5 to 14) not only have a magnesium content equal to that of ocean water, but some of them have a much greater content, in some cases as much as double or triple the amount. So far as the magnesium content is concerned, many of the Kansas oil field brines qualify for magnesium recovery.

Important as the magnesium content of a brine may be, it is, nevertheless, of little value for commercial magnesium recovery unless sufficient brine is produced. This relationship of high magnesium content to volume of brine produced is well illustrated by the brines coming from the Kansas City-Lansing formations. Brines produced from this pay zone have practically the highest magnesium content of any of the Kansas oil field brines (table 4). Analyses of the samples collected (table 5) show a magnesium content varying from 972 to 3,910 milligrams per liter, with an average of 2,525 milligrams. So far as the magnesium content is concerned, the Kansas City-Lansing brines are very favorable for magnesium extraction. The amount of brine produced from wells drilled into this formation, however, is insignificant. Many of them produce practically no brine and most yield less than 20 barrels per day. In a few cases some of the wells furnish from 60 to 150 barrels of brine per day. Such wells, however, are exceptional. Table 17 has been prepared to show the minimum number of barrels of brine required to produce 2,000 pounds of metallic magnesium (or 6,840 pounds of magnesium chloride) from brines containing from 1,000 to 3,500 milligrams of magnesium per liter.

Table 17—Number of barrels of brine required to produce 2,000 pounds of metallic magnesium

Mg. (milligrams
per liter)
Barrels
1,000 5,700
1,100 5,181
1,200 4,755
1,300 4,381
1,400 4,065
1,500 3,802
1,600 3,559
1,700 3,350
1,800 3,165
1,900 3,000
2,000 2,850
2,100 2,714
2,200 2,587
2,300 2,478
2,400 2,372
2,500 2,278
2,600 2,191
2,700 2,110
2,800 2,033
2,900 1,967
3,000 1,900
3,100 1,838
3,200 1,781
3,300 1,727
3,400 1,676
3,500 1,629

The number of barrels of brine required to furnish 2,000 pounds of metallic magnesium varies inversely with the milligrams per liter magnesium content of the brine. In other words it takes a smaller number of barrels of brine to produce a given amount of metallic magnesium from a high magnesium brine that it does from one low in that constituent.

Since a large amount of brine is necessary to insure the success of a recovery plant, and since chloride and other constituents are not removed, it follows that provision must be at hand for the disposal of the brine after the magnesium has been extracted. The most satisfactory means of disposing of the processed brine is by means of deep disposal wells. In many of the Kansas oil fields, deep disposal wells are now in existence; especially is this true in the oil fields of western Kansas. In such cases there would be practically no added cost in disposing of the waste brine.

The selling price of magnesium or its compounds is another factor to be considered in establishing a magnesium recovery plant. The many uses to which magnesium and its compounds are adaptable, together with the growing demand for these substances, are certain to insure a fair selling price, not only during the war emergency but also in the future. Prices of magnesium and its compounds for 1942 are listed on page 67 of this report. It should be recognized that magnesium recovery from Kansas oil field brines is not on a competitive basis with larger establishments erected solely for the purpose of securing magnesium or its compounds. It is probable that Kansas oil field brines can never yield magnesium as more than a by-product of oil production. Such a by-product industry might pay the cost of brine disposal although showing little or no profit in itself. As an illustration, during the past five years, more than 6,863,100 barrels of brine having a magnesium content of 3,199 milligrams per liter have passed through a single disposal system in the Burrton oil field in Reno county. One barrel of such brine contains 1.123 pounds of metallic magnesium. On that basis, 7,707,261.3 pounds, or 3,853.6 tons, of metallic magnesium were returned to the underground strata during a five-year period. On the basis of the 1942 price, this amount of magensium has a value of $1,734,120.

Possible Magnesium Recovery Plants in Kansas Oil Fields

High magnesium content, a large volume of brine, and the existence of deep disposal wells make several oil fields in Kansas worthy of study for possible establishment of magnesium recovery plants. Only those oil fields that theoretically could yield 1,000 tons of metallic magnesium annually are considered. The oil fields most worthy of consideration on the basis of the data at hand are: Burrton field, Reno county; Bornholdt field, McPherson county; Zenith field, Stafford and Reno counties; Welch field, Rice county; Hall-Gurney field, Russell county; and Oxford field, Sumner county. Data pertaining to these fields are summarized in table 18.

Table 18—Summary of data pertaining to Kansas oil fields worthy of further study for the possible establishment of magnesium recovery plants

Field County Horizon Producing
wells
Theoretical
brine
production
per year
(barrels)
Disposal
wells
Average
Mg.
content
(milligrams
per liter)
Average
metallic
Mg. content
(per barrel)
Theoretical yield (tons)
Metallic Mg. Anhydrous
MgCl2
Burrton Reno "Chat" 335 550,420,000 14 2,263 0.773 212,737.3 858,655.2
Bornholdt McPherson "Chat" 150 23,118,750 2 1,516 0.526 6,080.2 24,043.5
Zenith Stafford
Reno
Simpson
Viola
301 21,973,000   1,275 0.4.48 4,922.0 19,336.7
Welch Rice "Chat" 24 11,826,000 1 1,395 0.492 2,909.2 11,471.2
Oxford Sumner Topeka
Hoover
Stalnaker
Layton
19 4,401,900 1 2,874 1.000 2,200.9 8,759.7
Hall-Gurney Russell Kansas City-Lansing 396 2,168,100   2,912 1.010 1,094.8 4,368.7

The calculated tonnage of metallic magnesium given in table 18 is only of relative and comparative value and is based upon two assumptions. In computing the total amount of brine produced in any given field during the year, it was assumed that the wells were pumped daily and at the same rate throughout the period. The amount of brine is, therefore, a variable factor and can be computed accurately only from actual pumping data. The amount of brine in barrels per year in the table is accordingly too high. In ascertaining the amount of metallic magnesium in a barrel of brine, as well as the potential yield, the specific gravity of the brine was taken as 1. On the basis of the chemical analyses, of the brine was taken as 1. On the bisis of the chemical analyses, the specific gravity ranged from 1.014 to 1.159. If the latter variable specific gravities had been used instead of 1, the metallic magnesium content per barrel would be higher than those indicated in the table. Consequently, the theoretical yield of metallic magnesium would have been increased correspondingly. It must also be pointed out that not all of the metallic magnesium as given in the table can be extracted from the brine in the recovery process.

Burrton oil field

The Burrton oil field is chiefly in Reno county east of Hutchinson in T. 22, 23, and 24 S., R. 4 W. The pool extends into Harvey county in T. 23 S., R. 3 W. Production is mainly from the Mississippian "chat" and from the "Hunton." Four brine samples were collected, each one of which showed on analysis a magnesium content of over 2,000 milligrams per liter (table 8). The brine originated in the "chat" at a depth varying between 3,300 and 3,400 feet. Data relative to the amount of brine produced were obtained from only one well, the Sinclair-Prairie well in sec. 15, T. 24 S., R. 4 W. This well is reported to yield 4,000 barrels of brine per day. Should the other "chat" wells, 335 in number, produce an equal volume of brine, the field would produce yearly 550,420,000 barrels of brine, exclusive of the salt water yielded by the 72 "Hunton" wells in the field. On the basis that the magnesium content of the 550,420,000 barrels of brine is the same as the average of the four samples collected and analyzed (2,263 milligrams per liter) and that each barrel of brine contains 0.773 pounds of metallic magnesium (table 19), the Burrton "chat" well brines capable of being produced during the year would contain 21,273.7 tons of metallic magnesium. At the 1942 price, 21,273.7 tons of metallic magnesium are worth $9,573,165. At the present time, there are 14 disposal wells now in use in the Burrton field (table 20) with two disposal associations operating. The North Burrton Disposal Association, operated by the SinclairPrairie Company, takes care of much of the brine in the north part of the field; whereas, the South Burrton Disposal Association, operated by the Sinclair-Prairie and Barnsdall companies, disposes of the brines in the south end of the field. The disposal wells are distributed in twelve different sections, six in T. 23 S. and six in T. 24 S.

Table 19—Metallic and other magnesium content of one barrel of brine (42 gal.)

Mg.
(milligrams
per liter)
Metallic Mg.
(lbs.)
MgCl2
(Anhydrous)
(lbs.)
Mg(OH)2
(lbs.)
MgO
(lbs.)
1,000 0.351 1.39 0.848 0.582
1,100 0.386 1.52 0.926 0.640
1,200 0.421 1.66 1.010 0.698
1,300 0.456 1.80 1.094 0.756
1,400 0.492 1.94 1.180 0.816
1,500 0.526 2.08 1.262 0.873
1,600 0.562 2.22 1.348 0.932
1,700 0.597 2.36 1.432 0.932
1,800 0.632 2.50 1.516 0.991
1;900 0.667 2.64 1.600 1.049
2,000 0.702 2.78 1.684 1,107
2,100 0.737 2.92 1.768 1.165
2,200 0.773 3.05 1.855 1.223
2,300 0.807 3.19 1.936 1.283
2,400 0.843 3.33 2.023 1.339
2,500 0.878 3.47 2.107 1.457
2,600 0.913 3.61 2.191 1.515
2,700 0.948 3.75 2.275 1.573
2,800 0.984 3.86 2.361 1.633
2,900 1.017 4.02 2.440 1.688
3,000 1.053 4.16 2.527 1.747
3,100 1.088 4.30 2.611 1.806
3,200 1.123 4.43 2.695 1.864
3,300 1.158 4.57 2.779 1.922
3,400 1.193 4.75 2.863 1.980
3,500 1.228 4.85 2.947 2.038

Table 20—Disposal wells now in use in the Burrton oil field

Company or operator Location
Lloyd, Frost, and Study SE 2-23-4W.
Ledo and Wilcox W2 SW NW 12-23-4W.
Barnsdall NW SE SE 11-23-4W.
Sinclair Prairie SE NE SE 14-23-4W.
North Burrton Disposal
Association (Sinclair-Prairie)
NW NW NE 14-23-4W.
NE NE SE 23-23-4W.
NE NE SW 26-23-4W.
NW NW SE 26-23-4W.
Skelly S2 SW NW 2-24-4W.
Gulf NW SE NW 3-24-W.
South Burrton Disposal
Association (Sinclair-Prairie)
C NE NW 15-24-4W.
Texas NW NW SE 17-24-4W.
South Burrton Disposal
Association (Barnsdall)
NW SW 20-24-4W.
Nadel and Gussman NW NE NW 30-24-4W.

The available data suggest that the Burrton oil field offers the best possibilities for magnesium recovery of any field studied. The other oil fields studied are listed, however, because further study may reveal the practicability of using their brines for magnesium recovery, at least to the extent of offsetting the cost of present brine disposal. Any fields theoretically capable of producing approximately 1,000 tons of metallic magnesium annually are considered.

The Bornholdt oil field

The Bornholdt oil field is in McPherson and Rice counties. The major part of the field is in T. 20 S., R. 5 W., McPherson county. In 1941, there were 150 wells in the field, all producing from the "chat" at a depth of around 3,340 feet. Three brine samples were collected from this field (table 8). The average magnesium content of the brines analyzed is 1,517 milligrams per liter, somewhat higher than average sea water. Data as to the amount of brine produced were obtained from two of the wells. The average volume produced was 425 barrels per day. At that rate the 150 wells in the field would produce annually 23,118,750 barrels of brine. Since one barrel of brine having a magnesium content of 1,500 milligrams per liter (table 19) contains 0.526 pounds of metallic magnesium, the total potential volume of brine capable of being produced per year would contain 6,080.2 tons of metallic magnesium having a value of $2,736,090, based on the 1942 prices. There are at least two disposal wells in the field, one in sec. 25, T. 20 S., R. 6 W., and one in sec. 29, T. 20 S., R. 5 W.

Zenith oil field

The Zenith oil field is in stafford and Reno counties and had, in 1941, 301 producing wells. Production is mainly in the Mississippian Misener formation and Viola limestone 'of Ordovician age. Four samples of brine were collected, one in Reno county and three in Stafford county (table 12). According to information received, production was from the Simpson formation at a depth of approximately 3,600 feet. Analyses showed that the brines had an average magnesium content of 1,275 milligrams per liter, or approximately the same as that of ordinary sea water. Two hundred barrels of brine were produced per day from the one well on which data were obtained (table 12). Should all the wells in the field produce at the rate of 200 barrels of brine per day, a total of 21,973,000 barrels of brine would be produced during the year. Even at the low magnesium content of this brine, it contains 4,922 tons of metallic magnesium which, on the 1942 basis of prices, would be worth $2,214,900. Four well-distributed disposal wells in the field now provide for disposal of much of the brine produced.

Welch oil field

The Welch oil field is in Rice county. The 24 wells producing from the "chat" are theoretically capable of producing 11,826,000 barrels of brine annually. This volume of brine, on the basis of analyses (table 8), contains 2,909.2 tons of metallic magnesium. In 1942, 2,909 tons of metallic magnesium were valued at $1,309,050. At least one deep disposal well is located in the field.

Hall-Gurney oil field

The Hall-Gurney oil field is in Russell county. In 1941, 396 wells were producing from the Kansas CityLansing rocks. On the basis of three samples collected (table 5), the brine contains, on the average, 2,912 milligrams of magnesium per liter. In spite of the low production of brine per well per day, the calculated total brine production for the year amounts to 2,168,100 barrels. This volume of brine, because of the high metallic magnesium content per barrel (table 19), contains 1,094.8 tons of metallic magnesium, worth approximately half a million dollars.

Oxford oil field

The Oxford oil field is in secs. 14 and 23, T. 32 S., R. 2 E., Sumner county. In 1941, 13 wells were producing from the Stalnaker formation, 6 from the Layton, and 21 from the Arbuckle. Four brine samples were collected, one each from the Topeka, Hoover, Stalnaker, and Layton pay zones (table 14). The samples came from the Amerada Petroleum Corporation wells, all of which were located in an area less than 10 acres in extent. The analyses showed an average magnesium content of 2,874 milligrams per liter. All of the non-Arbuckle wells in the field, if pumped daily, would produce, per year, 4,401,900 barrels of brine containing 2,200.9 tons of metallic magnesium worth approximately one million dollars. The volume of brine and, therefore, the metallic magnesium content could be increased materially if all or part of these wells penetrated all four of the pay zones, a possibility suggested by the offset wells from which some of the samples were collected. All of the brine of the sampled wells is returned into subsurface strata by means of a deep disposal well.

References

Burwell, A. L., 1942, The possibility of magnesia from Oklahoma oil field brines: Oklahoma Geol. Survey, Mineral Report no. 14, pages unnumbered, fig. 1, tables 1-6.

Frye, John C., and Jewett, J. M., 1492, Magnesium; in, Kansas mineral resources for wartime industries, by John M. Jewett and W. H. Schoewe: State Geol. Survey of Kansas, Bull. 41, pt. 3, pp. 69-180, figs. 1-13, tables 1-26. [available online]

Gann, John A., 1930, The magnesium industry: Industrial and Engineering Chemistry, vol. 22, no. 7, pp. 694-700, figs. 1-6, tables 1-4.

Jones, Odgen S., 1942, The state's responsibility in oil and brine pollution originating in oil fields: Kansas State Board of Health, pp. 1-20, tables unnumbered.

Pawel, George W., 1942, Olivine: potential source of magnesia: Mining and Metallurgy, vol. 23, no. 426, pp. 331-333, figs. unnumbered.

Ver Wiebe, Walter A., 1942, Exploration for oil and gas in, western Kansas during 1941: State Geological Survey of Kansas, Bull. 42, pp. 1-123, figs. 1-42, tables 1-28.


Kansas Geological Survey
Placed on web Jan. 15, 2019; originally published July 30, 1943.
Comments to webadmin@kgs.ku.edu
The URL for this page is http://www.kgs.ku.edu/Publications/Bulletins/47_2/index.html