HI I | H 'H ll‘l'lHl * l 3% W THE REMOVAL OF BOWUNUS TOXiN FROM WATER Them for {€19 Qwaas of in. 8. MéCHIGAN S?A?§ COLLEGE Aifsad M. Wafibrsfik E9733 This is to certify that the thesis entitled THE REMOVAL OF BUIULINIB TOXIN FROM WATER presented by Alfred M1118 Wall'bank has been accepted towards fulfillment of the requirements for M degree in W8? 9 ' _ l. . K1431 %u\\.- '\ 1 M» \L\,' y \_1 Ma or professor Date July 93 1953 0-169 THE REE ‘AL OF EOTULINUS TOXIN FROM U‘TER By Alfred M. Wellbank Submitted to the School of Graduate Studies of Hichigen State College of Agriculture and Applied Science in partial fulfillment of the requirenents for tne degree of MASTER OF SCIEKOE Department of Eacteriology and Public Health Year 1953 “l HhSIS \O l lJ I as La i. .'l “ . lir' . u-_,.‘ Acknowledgehent The author wishes to eXpress sincere appreciation to Dr. W. L. Hallmann for his interest and guidance in these studies. Appreciation is also extended to Dr. J. P. Newsan and Irving L. Dahljelm. To Richard Hetherington of the Rhom and Hass Company for the strong base anion exchange resin XE-QB, and T. L. Gresham of the B. F. Goodrich Company for Beta- PrOpiolactone the author is indebted for generous samples to carry out the following exgeriments. I. PURPOSE During the past war, crystalline botulinus toxin, type A was develOped as a bacterial warfare weapon. Statements have been made that the use of botulinus toxin as a weapon could be as effective as an Atom Bomb as far as destruction of humans is concerned. Vany methods of dissemination are possible sucn as dusting over heavily pOpulated areas and con- taminating water reservoirs and water distribution systens. Inasmuch as there is little data available on the destruction of botulinus toxin in water an eXploratory 'study of chemical and physical methods of destruction ap;eared advisable (1). If a chemical method of des- truction could be evolved tiat would fit into a water treatment process, preventive measures would be possible in case of enemy attach. II. REVIEN OF TTE LITLRATJFE The crystallization and isolation of type A toxin was accomplished simultaneously and indegendently by two different groups of workers. Lamanna et. al. (2,3) reported crystallir e toxin with an L350 of 239.9 x 106 per milligram of nitrogen. Toxin prepare by Abrams C); et. al. (4) contained 220 x 105 n.L.D. per milligram of nitrogen. Eoth toxins, prepared by different methods, met the usual criteria of protein purity. Botulinus toxin is 15,003 times as active on a weight basis as the most toxic drug known, aconitin, and a mole- cule of toxin is 200 million tiies as tcxic as a molecule of the dru3 (5). The K.L. D. for a 20 gram mouse is 3 x 10'll grams of crystalline toxin, and if man is as susceptible on a body wei;ht basis s the mouse, 0.25 91 micr03rams of the pure toxin would kill a 70 kilogram man (6). Finally, to ex;ress its activity in terms re- cently used by an official of an international health or- ganization, seven ounces cistribu ted prOperly WCLlld kill the entire pOpulation of the world (5). he toxin mole mile has a molecular wei ht of 900,000. This brin3s up the question: how does this toxin injure the tissues of hi3her er Lima.ls? Chemical analysis has failed to answer this question. The toxin is made up of proteins composed of the szme amino aciis found in the normal tissue proteins of the host itself. In the case of type A bot- ulinus toxin, a complete amino acid analysis has revealed no unusual chemical groupings that mi3ht provide a clue as to why it is toxic. (i The calculated elementary iormula of tue toxin is: C40.298 H62.679 N10,472 012,534 P15—17 S123' Its amino acid composition is represented by the ex- pression: Glycine166, Alanine394, Valine406, Leucine708’ Iso- leucineggo, Prolineeoj’ Phenylalanine64, Cystine SH20' (Cystine 5-)40, Methionine64’ TryptOphaneag’ Arginine239, Histidine6o, Lysinep77’ Asparagin61370' Glucine953’ Serine374’ Threonines42’ Tyrosine672 (7). Comparison of the effects of'botulinus toxin and curare (8) has appeared in the literature for many years but Guyton and VacDonald (6) have recently presented work which indicates teat its action is different from that of curare. Acetylcholine and nicotine injected intra-arteri- ally still caused contraction of the muscle after botulism poisoning. With curare poisonin3 such is not the case. This indicates a fundamental difference between curare and cotulinus toxin. Eridence is presented which indicates that the principal action of botulinus toxin is probably at the myoneural Junction, thou3h possibly in the tirminal nerve fibrils. About the treatment of botulism poisoning Guyton and MacDonald (6) said, "Treatment of botulinus poisoning consists of massive doses of antitoxin, the use of artificial respiration and in cases of severe poisoning, the administration of vasoconstric- tor drugs. The fact that poisoning lasts for many months makes the results of such treat- ’ment discouraging. The use of artificial respiration for several months or longer is not practical, and if a patient is poisoned sufficiently to require vasoconstrictor drugs he will probably die anyway. The only real salvation seems to be the early use of anti- toxin in doses greater than 100,000 units of multivalent serum. Though antitoxin has been shown to be of value for guinea pigs as long as two days after poisoning, it is still true that its effect decreases eXponentially with time. One must remember that once toxin has reached the nerve ending and produced its damage this action is irreversible for many months." Lamanna (9) observed that type A botulinus toxin will cause hemagglutination of a red cell suspension. After this work was published many believed that this method of determining toxin activity would replace the eXperimental animal. Since then Lamanna (10) has found a lack of iden- tity between hemagglutination activity and toxicity of the toxin. There have been previous reports in the literature of attempts to inactivate tie toxin. Abrams (4) found that at room temperature the toxin was most stable between pH 1.0 and 6.0 with maximum stability between pH 4.0 - 5.0, while above pH 7.0 the toxin was rapidly destroyed. He found also that a temperature of 60 C. at pH 5.0 was 'sufficient to destroy its activity. Their method was most peculiar in that they treated the toxin wits form- alin for one hour at room temperature and then refrig- erated it for 18 hours before testin3. Samples treated with hydrochloric acid were kept at room temperature for one hour and a half and tien refrigerated for 18 hours. This may have been done because they were testing hemagglutinating activity of the toxin as well as toxicity. Jude et. al. (ll) reported on their efforts to inactivate the type D botulinus toxin. Type D toxin was sensitive to potassium permanganate, to an organic form of iodine, and a quaternary ammonium derivative. Bellinger et. al. (12) reported that after standing for 12 hours at 18 C. neither patulin, strepomycin, penicillin, hydroquinone, benzalacetonethiosemicarbazone, patulin thiosemicarbazone, 4-formy1antipurine thiosemi- carbazone, antihestimic drugs nor vitamin D2 had'any effect on the botulinus toxin. The oxidizing agents potassium permanganate and a solution of elementary bro- mine in distilled water neutralized this toxin while quinone, quinhydrone, and hydrOgen peroxide as well as aldehyde compounds failed to do so. 0f the numerous dyes tested, only crystal violet detoxified botulinus toxin after one hours combination. A recent communication by Littauer (13) indicates that five percent c0pper sulfate and silver ions were used with no adverse effects on the type A toxin. Potassium iodomercurate in concentrations of one and two-tenths percent caused inactivation. III. MATERIALS AND METHODS A. Medium and Organism The work by Lewis and Hill (14) has shown that clarified corn steep liquor (two-tenths to four-tenths percent total solids), two percent powdered skim milk or one-half percent casein (technical grade), two-tenths to six-tenths percent commercial grade glucose (cerilose) at a pH of 6.8 to 7.6 gives a high yield of toxin. This medium is inoculated with two percent of an actively growing culture of the "Hall strain" of Clostridium botulinus, type A, and in- cubated at 35 C. for 48 to 72 hours. EXperimental Animals The mouse was selected because of its sensitivity to the toxin. The mice used were from 16 to 24 grams for preliminary work and 18 to 22 grams for final de- terminations. Dosage Five-tenths of a ml. inoculated intraperiton- eally was used because it is believed that this is the most sensitive method for determining toxicity. D. Dilution of Toxin for Injection A buffer made up of two-tenths percent gelatin phosphate solution adjusted to pH 6.5 was used in the early eXperiments. In the later experiments all dilutions were made with sterile distilled water be- cause under the conditions of these experiments no appreciable loss in toxin titer was observed. Toxicity The toxicity was determined on a LD50 basis rather than the M.L.D. because it is statistically more valid (3). Eight animals were used at a given point but for preliminary work three animals were used. The animals were checked daily for five days. Time of Contact of Agent with Toxin All inactivating agents except the methylene blue chloride, ultra-violet light, and ion-excnange resins were allowed to remain in contact with the botulinus toxin for 30 minutes at room temperature (22 - 25 0.). Samples that were treated with chlorine were kept at room temperature for 30 minutes with enough chlorine to give a solution that had a no chlorine demand, then they were treated with the experimental dosage and allowed to stand for 30 minutes. In all eXperiments except with the use of active carbon and ion-exchange resins the chemicals were added to 10 ml. of toxin-water solution. To 100 ml. of toxin-water solution active car- bon (activated Charcoal) was added to give the desired concentrations. The solution was shaken in a dilution blank 25 times, then poured into centrifuge bottles and centrifuged at 100 x G for 30 minutes. Kethylene-blue chloride photodynanic effect was determined by eXposing the toxin-dye solution in a Bioassay Petri dish to a 200 watt electric light bulb at a distance of 15 centimeters for 15 minutes. Tee ultraviolet light (General Electric Germi- cidal Lamp - 15 watts) was placed two centimeters away from the toxin in a Eioassay Petri dish and was exyosed for periods of one and ten minutes. The column technique was used for most of the experiments with ion-exchange resins. Thirty grams of resin was placed in tme column and then regenerated. The resin was tsen wasged well with water to get rid of the excess regenerant. The toxin-water solution was then poured through the column very slowly. In the batch technique 10 grams of resin was re- generated, then washed well with water, and all of the excess water poured off. The toxin-water solution was added to the resin in a dilution blank and hen shaken 25 times. The supernatant was withdrawn for testing after 15 minutes. Controls All chemical compounds were tested intraperitone- ally the saie as he toxin. Controls were allowed to stand for 30 minutes and the hiyhest concentration used in tie exneriment was used as a control. Chlorine Determinations Concentrations of the chlorine solutions were de- termined by the amperonetric method of titration (15). Calorine demand of tne toxin was found by the Ortho- Tolidine-Arsenite Test (16). hcccal Chlorine I__.I (1‘ O '(M i c I) Q; (n * SCLtTOlS v. 3 ’— able II Effect of Chemicals on 500 Mouse LDSQ'S "I. j 2-; qu “‘ n a" dé‘ w‘AAs .L V '4‘- rormaldohyi: hocca 3111 c r i ne Iotassium Fern;ngxr;te ~ {3. l I O :,-- ()1 1'. 13 *_-o Solloi ll 2/ J J J, I. ‘ 1A ...~- "r.-1-'1 ,5 IT? .l..___4 J... Effect of Chemicals on 30,000 ‘ .- and ‘1 -\ d 'x.‘;’1" L¥UV-4v'aL ‘ '3 - -'. i V __._.~. .L;_\-: U H _“-I n_—'-.t-,; ~‘-. .‘ . * ' w‘ A. u u-~......L.c\... l v.1. .n. H» ml--. o... :1 ‘ r ’ n 'T‘ . . UUJ—.LU.Luvvl .LbuJ--&U s "I I. A, ‘ . ,1; ' : ’. _. ~ r'~‘ ALLOVU UL ‘U—5V5.A.LV.~-'-L U11 .fi an. —o q. _ 3 _ _-1 aLQLLLL‘QL—J— 4614c}. l‘l'OulOL, C A. (l- 0.1 (. >- H mouse Lb;~ ‘+d house he: A JO 8 J‘J v LAL 001-8 . p; Li '.___ h} E] Q C‘ I.) all" '.-.3 —7... 2"" J: J 0-0 J The firs t cherica l givei cor siferation was chlorine oe- cause it is being used in this country for treating m'1_y water supplies. Tables I, I, and III show that it would take 200 ppm to inactivate the toxin. this would be too much chlorine to use in water treatient. ()1 Totassiun p:r:un;a:ate was the next cheaical Ni ere beca se it has bee h used in some countries for water treat- ment. Tables I, II, and III show that 10; Lim had sone . .. , 1 A"A ,I. ‘,‘ .I- L. ~LA’ 1‘. J. (gr... -q‘ -'.I .."‘ . ., L‘- ac HIV tsr (kn-Q C|JKI I‘; “If; l-.aCUlVC~U‘;: _"l'3 LC/J\_LLL. -1Cr'3 C, 11,-; Lille J .. ‘ - P' ‘_;J’- n.‘ - ..- a r J- , . f. \. ‘fi '\ .’l v‘~‘:‘ L : «.(_' -- . -' f‘. .2 r3 4 -.-‘ anoant 01 Iciueinfhiwte is toc xii. fol ;,-43tICIl consideration. h -4 P 3- ~~ "\ ‘ ‘ 1" o - F ~‘ ..' " '4" 3‘ ‘- -‘ ’N . ‘- ". "N ' fl oone oi the ether cnmicali tel :: cl theoretical il.t'3cht r‘u ~r~ -,- " . fw J" '. "a“ "r‘ 1," '. A 'L ‘A 3‘ ‘ ‘*‘ ' ' 1‘ '~‘ '. "‘1 ive an inalcablch Cl now Cereal. chciical gro ps mloflt ”sounds could not be used in treating $13 0 cr 0 :1 << 0 P r+ c o 0 water because of toxicitv a d the others could not be used until lon tern toxicities were de tci mined. H Tables I, II, and I I iadicate that fcrzaldehyde at 200 ppm did not inactivate botulinus toxin. 'V‘ ihe results in Iables I, II, and III reveal th: (1* HI O .J H :1 (D H ‘- P .-‘ 4- 3 M ‘ \ 1‘ -" r- l r“ “A I r \ T ixx:ic-t-s hit 10 -H -c no eiiezt on 30' Ls~m s. i bis I I r'- i 4- ‘- n n_ . 1“ .... ‘15 _': , - v , ,‘, ' 4 .r‘ . 1- ‘VI fl- ,- , ‘ diuxeloses that 2u0 ppi c- noccul was toxi; icr the fiuuueo H Y (J H (D H D O 5' (I (‘4’ .r c+ (1' (D (f- ‘5 ’— F) ) a )J ( L (W I) ('3 r\ \l O "J :. ‘) "1 O -14- - h . m . .i - - . w ”I. n is en IOn 30ncentration on 5,012 LOuse LDSO s Dilution .1" ‘,-V..\ ,3 Oi enuiz c '1 10'2 13‘3 10-4 F4 C) r 2;... 7/7: 2/“: 7 '2 n/‘z e«~~-LD 2/ x 2/ 2 x J b} J “H 10.10 Uilltilcrl 1 O 7 4 of 332313 lO-* 10-“ 10-) 10‘ T‘_ r. - 3 " ‘2' “ 7 7 7 teatime J/J /// 2/.) 0/2 '7 A L - " /"' A 5' O /7 C . __ (‘l 0‘ a u LII.) J,’ J U/_,. / J " .‘ 7" — 7' ‘ 4" -—--° J- h .— 0 r" J. . L'- r ..—'. " -. ' u - ‘ «H r . J rs 4: “a . 1 _ ‘ o . 34 ‘7; . _r‘N.f '% .T’ I. Aaiv-l f1“ 1.. «\A w \AVJ- ~.-... DJ ‘ .L l‘qu U CL- L.-AV tLaxLI'lo lk~4~l;; n-.U 3.4- J- .~ vv-‘ 4‘- 5-: -" ‘- -—-Y 1", r".- ’ t .7--.‘ 0‘. )‘A r- ., ." .,.. i: '1 A 1 d J. h‘ 1A T."‘ i$$w-CK—.L VVVUvK uvU i.'..l ’50)). :8 Ia... Uo“fv L-gabs ;_L& .LU O.L\J u-.~;¢. v Hm. x ’3 J— 7" J- . P we lv 1-- C uJ. Vw u). - o . J- 1 —.1 J P‘ 4 L F ‘7“2 - NDL ‘- - o A‘- ‘ ‘- L ‘ r. U‘ 'U— .— I—L— A-k H ‘1 —- U \. A \J U -- V- -L. v J...‘ l - ' LI -giv '1 i ‘ _~.. .. . - '7 3 ~ . L'. - W - It . J . -- V $. J. _ - - _ “j HAf-f‘ .‘t. ‘,fi Alf‘ ,‘ 1 ~~ ( 1a ’_ a y- Al ,1 . w p 7’ V -L b-UU\’vV a. 2.4 J \; «JV I!KJ\4£,L. v ‘. 'u— U-‘.~'_L»>J J-i-s-‘V Vo'h I —- NJ 9‘ I— -x. V'— ‘yu—a-s. - 15 - Table VI Effect of 400 ppm of Beta-PrOpiolactone on 10,000 Mouse LLBO'S Dilution of Sample 10"1 10‘2 10—3 10-4 Deaths 3/3 3/3 3/3 3/3 Beta-PrOpiolactone was of interest because it has been shown to be effective against bacteria and viruses in plasma and blood (17). It is an acylating agent possessing a low degree of toxicity (13). However, it had no activity agairst the toxin at the concentration used in these experinents. Photodynumic Effect of hethylene glue Chloride on 10,000 va '5 D So hetnylene :lue Chloride 1:2,000 Dilution 1 _q j of Sample 10‘ 10 L 10-3 10“+ Deaths 3/3 3/3 3/3 0/3 Hethylene Blue Chloride l:lO0,000 Dilution of sample 10-1 10-2 10-3 10-4 Deaths 3/} 3/3 3/3 3/3 Kethylene blue chloride was shown to be capable of in- activating tetanus toxin by an oxidation phenomena (19). It showed a slight effect against botulinus toxin at a concen- tration of 1:2,000 of the dye. - l7 - Effect of Active Carbon (Aqua Luchar A) on 5,012 Xouse LDJO's ./ 70 ppm of Active Carbon Dilution of Sample 100 io‘1 10'2 10'3 Deaths 3/3 3/3 3/3 3/3 140 ppm of Active Carbon Dilution of Sample 100 10-1 10-2 10-3 Deaths 3/3 3/3 3/3 3/3 Under the experimental conditions active carbon did not remove any of the botulinus toxin from water. The use of active carbon was of particular interest be- cause it is used in some water treatment plants to remove particulate matter and excess chlorine. -18- Table IX Effect of Ultraviolet Light on 1,000 Mouse LD50'S One Minute Exposure at a Distance of Two Centimeters Dilution of Sample 100 lO 1 10-2 10"3 Deaths 3/3 3/3 3/3 3/3 10 Kinutes Exposure at a Distance of Two Centimeters Dilution of Sample 100 10‘1 10"2 10‘3 Deaths 3/3 3/3 3/3 3/3 Ultraviolet light was used because it was hought it might denature the protein but it had no apparent effect. _ 19 - Table X Effect of Passing 100 milliliters of 1,000 House LD5O's of Toxin Through 30 grams of Strong Base Exchange Resin- Hydroxy Form (Amberlite XE-98) in a Column. Dilution Of Sample 100 10-1 10-2 10-3 10-4 Deaths 0/3 0/3 0/3 0/3 0/3 Table XI Effect of Passing 100 milliliters of 10,000 House LD5O’s of Toxin through 30 grams of Strong Base Exchange Resin-Hydroxy Form (Amberlite XE-98) in a Column. Dilution of Sample 100 10‘1 10‘“ 10‘3 10"4 Deaths 0/3 0/3 0/3 0/3 0/3 An anion exchange resin was reported by LoGrippo (20) to absorb the Lansing strain of the Poliomyelitis virus and Theiler virus (T0). - 20 - Final Results Table XII Effect of Passing 100 milliliters of 10,000 Mouse LD‘O's of Toxin Through 30 grams of Strong Base Exchange Resin-fiydroxy Form (Amberlite XE-98) in a Column. Dilution of Sample 100 10‘1 10'2 Deaths 0/8 0/8 0/8 Table XIII Effect of Using the Batch Method of Ion Exchange on 100 milli- liters of 10,000 Mouse LD 's with 10 grams of Strong Base Anion Exchange Resin-Hydr xy Form (Amberlite XE-QB). Dilution of Sample 100 10"1 10'2 Deaths 0/8 1/8* 0/8 * Not a typical botulism death A strong base anion excnanger used in the hydroxy form proved to be successful in removing the toxin from water. Since strong base anion exchange resins are used in water conditioning for the removal of silica from water fed to high- pressure boilers (21) this should prove to be a practical method for removing type A botulinus toxin from a water supply. V. v V“- A. «.9 Sf — l. . _, I . -A-A‘L s in an FJ A study has been made of a number of cremica attempt to inactivate botulinus toxin type A. lone of the chemicals used were effective in low enough con- centrations to be of practical value for use in treat- ing a water supply because of toxicity. Chlorine was of prihary interest because it is used by gany water treatment plants. Evidence is given which indicates that a strong base anion exchange resin removes type A botulinus toxin from water. Further research should be done to determine if ion exchange resins could be used to concentrate the toxin and purify it. T43 concentration of the toxin would be helpful in detection in case of attach during war- time. Rosebury, Theodor and Rabat, Elvin.A. Bacterial Warfare Journal of Immunology 56; 7-96, 1947 Lamanna, Carl; McElroy, Olive E.; a Eklund, Henniig W. The Purification and Crystallization of Clostridium botulinum Type A Toxin Science 105; 613-614, 1946 amanna, Carl; Eklund, Kenning U.; XcElroy, Olive 2. Botulinum Toxin (Type A); Including a Study of Shaking with Chloroform as a Step in the Isolation Procedure Journal Bacteriology 52; 1-13, 1946 Abrams, Adolph; Kegeles, Gerson; & Hottle, George A. The Purification of Toxin from Clostridiun botulinum Type A Journal of BiolOgical Chehistry 164; 63-79, 1946 T1 va Heyningen, W. E. Bacterial Toxins Blackwell Scientific Publications, Oxford, England 133 pp. 1950 ‘fr‘ Guyton, Arthur C. and IacDonald, marshall A. Physiology of Botulinus Toxin Archives of Feurolcgy and Psychiatry 57; 378-592, 1 47 KO Buehler, Henry J.; Schantz, E. J.; & Lamanna, Carl The Elemental and Amino Acid Comrosition of Crystalline Clostridium botulinum Tyne A Toxin Journal of 3i010gica1 Cnenistry 169; 295-302, 1947 8. 10. ll. 12. 13. - 23 - Edmunds, Ch.rles J. and Lon , :3rr' Contribution to tfld Pat4010”ic Physio 0gv 0P sotulism Journal of tAe An-ric:* ' " ‘s 03 - ..1 ,- . Lamanna, Carl Hemagglutination by Lotulinal Ionin Proce e0 .i.1: 01' the Society 0; Bz-Lgeri...ent:.l Biology an; 7 —v':' .\},r_') Ledicine 69; 532-330, 1940 Lamamia, Sarl and Lowentix‘l, Josegh .c. The Lalo: of Identity Bet..e31- hemagvlutior and tie 101.111 of Type A Eotulinal 01.1n1sm Journal of Bacteriology 61; 751-752, 1951 Jude, A.; Gi arf, P. and Ctrrot, I. Destructive Action In vitro of Certain Chehical Agents on Botulinus an; Tetanus To: 1 s1t~s Ren;is de la Societe de :13 142; 318-319, 1949 ellinger, 3.; Xoernlein, I. and a he, A. as erhslten des Toxins von Clo ridiu:. bot linum und Sal: onella enteritidis geg enuoer chemotherapeutica, Antibiotica und Earbstoffen Zentralblatt fur Bakteriolo ie Parasite1.liunde, Intentionsir :heiten und Iyg ine, I Orig 153; 450-445, 1951 [‘1 U Litta zer, Uriel Ooservations on *he Tyge A Toxin of 310: ridium ootulinum Tature 107; 994, 1951 Lewis, K. H. and Hill, 3. V. Practical Iedia and Control easures for Producing Highly Toxic Cultures of Clostridium botulinun, Type A 1\ Journal of Bacteriology 53; 215-220, 1947 15. l7. 19. 20. 21. - 24 - Griffen, A. E. The Breai {point Process Technical Publication E0. 215, 25 pp "allace a Tiernan Co., Inc. .Stan dard Iethods for the Examination of Hater and Sewage Ameiic n Public Health Association, Yew York 2C6 pp: 9ti edition, 1946 Hartman, F. W. ; Piepes, S. L.; 0nd .allba n:, A. I. Virucidal and OBac tericidal Pro1erties of B- -Pr0piolactone Federationr9100eedings 10; 553, 195 Kelly, A. 3., and Hartman, E. H. Beta-PrOpiolactone; Its Toxicity, Degradation Products aid Comparison with litro Etrusteid O¢Cfl Federation Proceedin 10; 561, 1951 Lippert, Karl n. he Photody namic Effect of lethyle ne Blue on Tetanus Toxin Journal of Immunology 28; 195-205, 1955 LoGrippo, Gerald A., and Berger, Bernard Use of Ion Exchange Resins in Partial Purification and Concentration of Poliomyelitis Virus Journal of Laboratory and Clinical 1 Iedicine 39; 970-973, 1952 Ton Eyeiang e The fiohm and Hess Cthany The Resinous Products Division 23 pp. 1950 .“'._’ n l,- .3" 1 -~ .- . ‘..~ ;~~. ' x- < :1" » ~ t i v .. .t' 4"g "">‘. ‘ ‘.. ‘ A ,' " ”WV-M 13f ~..~;4.~:,,",‘,-..-- "'53? . d- .1? TE}. '5? " NH“ vr‘NJ- .. A a - '1 , ”V. t" 32; M19?!» .‘y ‘1',» a!" r‘f'. .3? . . , ’9 C .'/1n' \ ‘ .L L "I": ' g .’ . ‘5 2.." a 1.4 «1 ' - '9'"; $1st .4“ w.”- 512 a, \\. $‘t‘ ." d_"' . h. i}. [v V’l’f .' .Iv . ‘ z. ' N ,. . «4' ‘ '- 5‘” +' .. ~13: - ,91' . - '4 g x .r, _ .. -‘o \ 1' g A ’. ‘Ké‘ijag. 'r RCN‘F‘V ”if? * MCI HIGAN STATE UNIVERSITY LIBRAR I II|||II|I|I||I||II I IS