Do- u-— ~o o ,- \ .. \‘ \ 40" ..¢ .- . . . ' 1 1. b. This is to certify that the 5 thesis entitled Studies in the Isolation of an Anti-tumor Growth Factor From Boletus'gggilg ‘ ,' presented by Alfred Ernest Ritchie has been accepted towards fulfillment of the requirements for __E._ degree hwy ‘-__. \\\J a Major grofessor Date Aug. 29. 195l__ ‘ \ 0-169 - - l STUDIES IN THE ISOLATION OF AN ANTI-TUMOR GROWTH FACTOR FROM BOLETUS EDULIS BY Alfred Ernest Ritchie A THESIS Submitted to theSchool of. Graduate Studies of Michigan State College of Agriculture and Applied Science in partial fulfillment of the requirements for the degree or MASTER OF SCIENCE Department of Chemistry 1951 ’7! IFMISTRY DFPT. Tbla‘0\ E Reefi PREFACE The work to be described was undertaken as a cooper- ative project of the departments of Chemistry and Horti- culture at Michigan State College. It was initiated as a result of the observation of Dr. E. H. Lucas that a tumor growthrinhibitor could be extracted from the mushroom Boletus edulis. The primary aim of the study was to determine, if possible, a practical means of concentrating or isolating this principle. This thesis will deal with the evolution of a pro- cedure for the separating from crude material extracts the factor or factors responsible for the inhibitory activity. The author wishes to eXpress his sincere thanks to Dr. E. H. Lucas for the origin of the problem and the financial assistance given the author throughout the study and for his friendly counsel and encouragement. The author also wishes to express his sincere thanks to Dr. R. U. Byerrum for his intimate association and helpful suggestions that stimulated the author in his work. TABLE OF CONTENTS CHAPTER I. CHEMICAL STUDIES OF BOLETUS EDULIS . e e . . . HISTORICAL BACKGROUND. . e . e . e e e e . . . Tumor growthvinhibitors from sources other thanBoletusedulis........... Tumor growth-inhibitor from.Boletus edulis METHODS AND MATERIALS . . . 0 Method of Biological Assay. Experimental details. . . Interpretation of assays. Source of Materials . . . . Methods of Concentration. . Extraction. . . . . . . . Preoipitating agents. . . Acetic acid . . . . . . Ammonium.su1fate . . . . Ethanol . . . . . . . . Acetone . . . . . . . . Dialysis. . . . . . . . . Lyophilization. . . . . . RESULTS. . . . . . . . . . . . Stability Tests . . . . . . Stability toward acid . . Stability toward alkali . Page OOOQQQQQQGQQGO‘tbfifi-NH H O TABLE OF CONTENTS CONT. Page Thermal stability e e e e e e e e e e e e e e 10 Preparation of Samples. . . . . . . . . . . . 50 Per cent ethanol precipitation . . . . . Acetic acid precipitation . . . . . . . . . 50 Per cent ammonium sulfate precipitation. 50 Per cent ethanol precipitation . . . . . Dialysis and absorption techniques of detoxification. e e e e e e e e e e e e e 50 Per cent ethanol followed by acetone precipitation e e e e e e e e e e e e e 0 Stability and fractionation (acetone) tOOhDIQUBSe e 0'. e e e e e e e e e e e e A01d stability. e e e e e e e e e e e e e Alkali stability. 0 e e e e e e e e e e 0 Stability at 80 - 90 per cent acetone concentrations. 0 e e e e e e e e e e 0 Acid hydrolysis e e e e e e e e e e e e e Re-extraction and modified ethanol precipitation technique . . . . . . . . . 50 Per cent ethanol followed by dialysis and acetone fractionation . . . . . . . . 50 Per cent ethanol, dial sis, and acetone) fractionation (modified e e e e e e e e 0 Direct acetone precipitation (rapid method) Direct acetone precipitation and re-precipitation. e e e e e e e e e e e e Detoxification technique (Pancreatin d1808t10fl). e e e e e e e e e e e e e e e Acetone fractionation (2 step method) . . . Detoxification technique (Trypsin digestion). 11 12 13 13 15 16 2O 22 23 25 27 28 30 33 56 57 39 c“; 4? TABEE OF CONTENTS CONT. Page 55 Per cent acetone precipitation (IiflglOBtOPMB‘bhOd)eeeeeeeeeee 48 Acetone fractionation (variable time method).................. 48 SUMMARY.....................61 CONCLUSIONS 0 O O 0 O 0 O 0 O O 0 0 O 0 O O O O O 52 BIBLIOGRAPEO O O O O O O O O O O O O O O O O 0 O 54 Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 LIST OF ILLUSTRATIONS Page CHAPTER I CHEMICAL STUDIES OF BOLETUS EDULIS HISTORICAL BACKGROUND The origin of studies in the isolation of tumor- growth inhibiting substances from natural sources is unknown. Tumor-growth inhibitors from sources othgr_than Boletus edulis. In 1924 Matsushita (7) reported that treatment with a plant enzyme or enzyme-like substance dispersed in oil resulted in necrosis and gradual resorption of tumors and was said to have clinically cured thirty-five per cent of 3,417 patients and others improved. Shortly after, Torrey and Kahn (ll) injected directly into rat tumors preparations of proteolytic enzymes from Bacterium.histolyticus with destruction of the growth in from 50 per cent to 75 per cent of the animals. However, Gye (2) found this preparation inactive against other mouse tumors. The chemical nature of these preparations was never reported since the work was not confirmed by the later investigation of Gye. For several years beginning in 1959 Lewisohn (5), Laszlo (3), and Leuchtenberger (4) studied extracts of polished rice, pearled barley, and Lactobacillus casei and reported that anti-tumor factors could be demonstrated from these sources and could be quantitatively compared with -inositol standards. Although the natural extracts were impure they were more active unit for unit of weight than inositol itself. Further study, following this observation, suggested that the "folic acid concentrates" of these prep- arations might contain the active principle. This was found to be the case, but not all of the activity could be ascribed to these fractions of "folic acid". Other materials studied by these workers included a yeast and S; Lactis 3;, Sugiua (10) reported that his work with the preparations of Lewisohn, Laszlo, and Leuchtenberger could not confirm their findings. In 1951 Reilly and Stock (8) reported that studies carried out on culture media in which strains of Aspergillus fumigatus were grown showed that a substance was present- which exhibited tumor-growth inhibitory preperties. This activity was measured against the mouse sarcoma 180 and was found to inhibit the growth of the tumor. The active agent of Aspergillus fumigatus strain 943 was isolated by complete saturation of a filtrate of the culture medium.with ammonium sulfate, suspension of the resulting precipitate in water, and dialysis.. The activity was non-dialyzable and was lyo- philized. The anti-tumor substance seemed to be protein in nature and was not one of the four bactericidal agents that this fungus is known to produce. Further purification of the active principle did not result in any appreciable decrease in its toxicity for mice, and thus it has not proven to be a promising therapeutic agent. Tumor-growth inhibitor £322 Boletus edulis In 1950 Lucas (6) prepared water extracts of dry, crude material from.§; edulis which consistently inhibited the growth of the mouse sarcoma 180. Although the inhibition was not complete and the dose levels were toxic, these obser- vations warranted further investigation. Treatment of the extract with 0.01 per cent formaldehyde destroyed the activity of the samples. Likewise, refluxing for two hours at 100°C. resulted in loss of the activity. 'The activity however was not destroyed by treating the dry, crude material with.absolute ethanol prior to the water extraction. These observations led to a preliminary belief that the substance responsible for the activity might be proteinaceous or closely associated with the protein extracted.from.the crude material. METHODS AND MATERIALS Method of Biological Assay Experimental details. An in vivo test (1, 8, 9) was employed by the Sloan- Kettering Institute for Cancer Research in New'York to ascertain the tumor-growth inhibiting activity of the samples prepared. Preliminary to the inhibition test, single dose toxicity limits were determined so that the inhibition test could be carried out at a maximum.tolerated dosage. As will be seen from.the results reported here, the single-dose toxicity test could not be perfectly correlated with the in vivo inhibition test results. The inhibition test consisted of treating groups of five mice (20 g.1:2 White Swiss), 24 hours previously sub- cutaneously implanted with the Crocker Mouse sarcoma 180, with intraperitoneal injections of the various fractions prepared from §:_edulis. Injections were usually 1 cc. or less administered twice daily for seven days. Mice of similar age and weight Were implanted with the tumor but received equivalent amounts of physiological saline to serve as controls. At the end of seven days the tumors of both the treated and control animals were measured in two diameters by means of calipers. The inhibition of the 5 tumors in the treated animals was based upon the develOpment of the tumors in relation to the untreated controls. ‘leight changes of the treated animals and controls were determined and reported. Interpretation 93: m. The single dose toxicity test results were reported as numbers within the limits of 0.5 and 5.0. Five-tenths represented extreme toxicity accompanying a single injection 01:10.5 cc. of the sample, and 5.0 represented non-toxicity at dosages of 5.0 cc. Numbers between these two figures represented gradations of the toxicity within these arbi- trary limits. For the inhibition test an arbitrary system‘cf grading was also adopted. It was as follows: flanked inhibition (+) - The average diameters of the tumors in the treated animals were one-quarter or less than that of the control animal tumors. Good inhibition.(t*) - ‘Average tumor diameters in the treated animals were one-fourth.to one-half of those of the controls. Slight inhibition (1?) -- Average tumor diameters in the treated animals were one-half to three-fourths of those of the controls. Negative (-) -- Average tumor diameters in the treated animals were three-fourths of or equal in diameter of those of the controls. mew Boletus M grows naturally in wooded areas of Germany from which the material was obtained. After the mushrooms were gathered, they were thoroughly air dried and packed for shipment. . Samples for this work were taken from three different shipments from Germany all of which were shown to contain the active principle. Methods 9; COncentration " htraction. In all instances reported here the dry material after grinding to 60 mesh in a Wiley mill was extracted with dis- tilled water. The extractions were made either in a ceramic morter with sand or in a Waring Blender without the use of sand. The ratio of weights of sample to extrath was be- tween the limits of 1:10 and 1:30 with the mjority of ex- tractions carried out at 1:20. Hereafter the solution obtained from the extraction or the fungus with water .111 be referred to as the extractive. Precipitatigg agents. As discussed previously (page 5), the possibility that the active principle might have been proteinaceous led to the use of common protein precipitants as trial methods for the concentration studies. All precipitations were carried out in the cold at 7.0013. in standard beakers or Erlenmeyer ‘ Condensation,gconoentration, condensation and concentrate are used synonymously in this paper. flasks. Acetic acid: the use of acetic acid was limited to lowering the pH of the extractive to ca. pH 4.0 and collect- ing the resulting precipitated materials. Armenian sulfate: fifty per cent saturation with ammon- ium sulfate was used as a method of precipitation followed by dialysis to remove the excess salt from the collected precipitate. Il'he method used consisted of adding an equal volume of a saturated solution of amonium sulfate to the extractive of the §_._ M material. The saturated solution of amonium sulfate was clarified by the addition of ammonium hydroxide (cone.) to a pH of 9.0, heating for two hours on a steam bath, allowing to stand for 48 hours and decanting to remove the hydrous oxides of the heavy metals. The pH of the decanted solution was readjusted with C.P. sulfuric acid to ca. 5.2 (to the pH of a satur- ated solution of G.P. ammonia sulfate). After the pH adjustment crystalline 0.P. ammonium sulfate was added to insure complete saturation. Ethanol: ethanol was used in a concentration up to 50 per cent by volume by the addition of the calculated amount of '70 or 95 per cent ethanol to the extractive. Acetone: acetone was used over a wide range of concen- trations from 30 per cent by volume to 90 per cent by volume as. an attempt to fractionate the precipitated materials. Dialysis: the apparatus used for dialysis was of the rotating tank type driven by a fractional horsepower motor geared down by either reduction drives or pulleys to a speed at ca. 50 rpm. The dialyzing bag was imersed in the rotating tank excentrically to facilitate agitation with consequent shorter equilibration time. The ratio of the solution in the bag to the dialysate varied within wide limits depending upon the nature of the material in the bag and the purpose for which the dialysis was made. The lower limit of ratio was ca. 1:1 and the higher limit greater than 1:45. Usually the dialysis was carried out at room temperature with a few runs made in the cold at 7.0°0. 'The dialysate was distilled water in all cases. Lyophilizaticn: the apparatus used in 1yophilization of some of the samples utilized a standard Cenco vacuum pump with a pistol type mercury diffusion pump in series to develop a vacuum of ca. 0.001 mm Hg pressure. The freezing unit consisted of a steel tank of ca. five liters capacity into which ethanol and solid carbon dioxide were placed. The temperature of this system was ca. 42.0%. The plan of this equipment as designed and constructed by Diang is shown in Figure 1. b Figure 1* C: x d A Figure l. Freezingodehydration tank A. Side section view B. Top section view a. freaing chamber. b. center pipe. c. freezing cone, d. 250 ml centrifuge bortle. e. adapter, f. rubber ring b .- C d bUclamp F csetdngscrew dwccdecblod: Cid-'00 4L re l to mechanical pump ’0 .— P P B l—J l k. f”:'721_____i:a I Civ :3 Figure 3. Assembly of apparatus A. Freezing-dehydration tank B. mcruxry condensation pump C C. mechanical pump D. coil trap E. McLeod gaub-e F. dry air inlet G. we Way stopcock * Courtesy of Stephen Ljang (M.S.C. thesis in preparation) RESULTS Stability Tests Previous experience and the reported findings of other investigations had suggested that the anti-tumor factor or factors from natural sources were of an unstable nature. In order to obtain definite information concom- ing the risk of losing the activity in the course of the isolation processes, samples were prepared and tested in order to ascertain stability limits of the material under various conditions. Stabilin toward acid. ‘ An extraction was made of the crude material and the extractive made acid to a pH of 2.0 by the addition of concentrated hydrochloric acid. After a short period of time (ca. 2 hours), the pH was adjusted to 5.1 with 10 per cent sodium hydroxide added dropwise. The upper limit of pH 5.1 was taken since the pH of the extractive was deter- mined as 5.1 with a pH meter. The tumor inhibition test result of this sample was negative. Another extractive was made acid to a pH less than 1.0 with concentrated hydrochloric acid and allowed to stand in the cold (7°C.) for four days. The solution was then dialyzed until the pH had risen above 4.0 and no test for 10 carbohydrates (Molisch) was observed. The tumor inhibition test result was negative. From these results, it was assumed that the active principle was acid labile and all subsequent preparations were made without lowering the pH of the extractive. Stability toward alkali. An extractive was made alkaline to a pH of 8.9 for about two hours with 10 per cent sodium hydroxide, then adjusted to 5.1 with concentrated hydrochloric acid. The inhibition test result was negative and further preparations were made without raising the pH of the extracting medium. Thermal stability. The stability toward heat was determined by Lucas as described previously (page 3). As a result of the loss of anti-tumor activity by refluxing for two hours, all samples prepared in this work were kept from obtaining a temperature greater than 35°C. in any step in their preparation. Loss of activity by low temperatures (7.000.) was never observed, except through the action of extreme concentration of acid in the cold. Stabilig toward dialysis. It was observed that the active principle was non- dialysable, but no specific experiment to determine its stability during dialysis was carried out. Activity was demonstrated after three days of dialysis at room temperature. Preparation pf samples The sequence followed here is in the same order as the samples were prepared in the development of a generalized procedure for concentrating or isolating the active principle from Boletus 293153. The description of the procedures followed will be divided into appropriate parts with separate headings to facilitate referencing and marative examination of the work. These headings will include the method of extraction and filtration, dialysis, precipitation, special treatments, collection of fractions, solubilization and results of the tuner inhibition tests. A discussion of the motives for modification of the procedures will also be presented under the description of the methods of sample preparation. A descriptive title will be given to a specific type of preparation or to groups of samples similarly prepared. Illustrations were prepared for representative pro- cedures throughout this study to summarise the treatments followed in the preparation of the samples. These will show the method of preparation and the results of the tumor inhibition test for the sample described. g2 29}; 9333 ethanol precipitation Lng M 9gp precipi- m (R-B 1 and 8-8 2). . Extraction and filtration: a 34 g. sample was tritur- ated in a porcelain morter with 340 ml. of distilled water for 20 minutes and then filtered on a Buchner funnel using 12 No. 2 Ihatman paper. Recovery was 260 ml. Filtration was extremely slow*due to the small particle size of the sus- pended material. The recovered extractive was divided equally for treatment separately as follows: A. 30 per cent ethanol precipitation (R-B 1) Fig. 2 Precipitation: a 150 ml. portion of the ex- tractive was placed in an Erlenmeyer f1ask.which.was immersed in a beaker of crushed ice in the cold (7.0°0.) for ca. 20 minutes. One hundred.ml. of 70 per cent ethanol was then added and the mdxture allowed to stand overnight in the cold. Collection of precipitate: the precipitate was centrifuged, but the supernatant was not decanted. The bottles were placed on the lycphilizer, after freezing, for 10 hours to remove the ethanol and water. The sample was removed and allowed to stand overnight in a vacuum.desic- eator over P205. The sample was shipped in the dry state. ‘leight ca. 0.6 g. Solubilization: solubility was determined in water, physiological saline, and phosphate buffer of pH 7.5. The material was readily soluble in the phosphate buffer, but slightly less soluble in water or saline. Result:. Single weight change dose Dose Result in . toxicity’ ‘ cc. Treated Controls~ Remarks 3.0 0.5-0.2 - -3.0 ' 1 died -1e5 Figure 2 RAB l and 348 2 Crude Haterial 1. Ground to 60 mesh 2. Extracted with H20 (1:10) in.morter with sand 3. Filtered with suction (No. 2 Whatman paper) Solid residue discarded Extractive (filtrate) Divided equally R-i3 1 ., R—L 2 H 1. Eade 30% ethanol at 7°C . pH lowered to h.3 with Glacial 2. Stood overnight at 7°C acetic acid 3. Centrifuged 2. Stood overnight at 7°C h. Lyophilized 10 hours to 3. Centrifuged dryness h. Lyophilized 10 hours to dryness 5. Stood overnight in descicator 5. Stood overnight in descicatcr over P205 over P205 Inhibition test results (3-8 1) Inhibition test results (R98 2) Toxicity - (3.0) Toxicity - (3.0) Inhibition - (-) Inhibition — (-) B. Acetic acid precipitation (R-B 2) Fig. 2 Precipitation: a 130 ml. portion of the extrac- tive was cooled in the cold (7.0%.) and then treated with glacial acetic acid to a pH of 4.5 as determined by a pH meter. The solution was allowed to stand overnight in the cold. Collection of the precipitate: the precipitate was centrifuged and with the supernatant was lycphilized for ten hours followed by standing overnight in a vacuum desiccator over P205. The sample was shipped in the dry state. Weight ca. 0.5 g. Sclubilisaticn: solubility was determined in water, saline, and phosphate buffer of pH 7.3. The material was readily soluble in the buffer, but less soluble in water or saline. Result: Single Weight change dose Dose Result in . Remarks toxicity ' cc. ~ ‘ Treatedfiontrcls 5.0 0.8-0.3 . .400 .1e5 53 Le; M ammonium sulfate precipitation (R-B 5). Extraction and filtration: an 18 3. sample was ex- tracted with 160 m1. of distilled water for 20 minutes in a morter and filtered on a Buchner funnel with No. 2 What- .man paper. Recovery was ca. 120 ml. Precipitation: the extractive was cooled in the cold 14 rocm.and then.an.equal volume of saturated ammonium.sulfate was added and the mdxture allowed to stand overnight in the cold. The precipitate was filtered off with.suotion and placed in a cellophane dialysing bag. The sample was dial- yzed against 5 liters of distilled water with one change after ca. 2 hours. Thermaterial was then lyophilised for ten hours and dried over P205 overnight. The sample was shipped in the dry state. 'Weight ca. 0.4 g. Solubilization: solubility was determined in water, saline, and a phosphate buffer of pHIV.5. The material was readily soluble in the buffer but less soluble in water and saline. Result: Single ‘Weight change dose Dose Result in . Remarks toxicity cc. Treated/gontrcls 3.0 00"002 . p '6 .U .105 Discussion: although.the results of these three methods ‘were all negative, ethanol as a.precipitating agent was selected for further study at higher concentrations due to its ease of removal from.the precipitated material. Also the extreme difficulty of filtration through.paper prompted its replacement with.unbleached muslin to increase the speed of filtration. The overall time required for the preparation of the samples was possibly a detriment to the demonstration of anti-tumor activity. 93 £11; 9335 ethanol precipitation (R-B 4 and R-B 5) Extraction and filtration: a sample of ca. 28 g. was extracted with distilled water at a ratio of 1:10 in a flaring Blendor. lt was found difficult to carry out the extraction at this low ratio and water was added to raise the ratio to 1:15. After ca. 3 minutes of blending the material was transferred to a clean square of unbleached muslin and was squeezed by hand (maxim pressure) to attempt clarification. Considerable solids were extruded in this process. Recovery ca. 370 ml. Precipitation: the extractive was cooled to 7°C. and made 50 per cent by volume with redistilled ethanol and allowed to stand overnight in the cold. Collection of fractions: the precipitate was centri- fuged off and dried on the lyophilizer. The precipitate was sent for testing as sample 3-3 4. The supernatant was concentrated from a volume of ca. 650 ml. to 10 ml. under a vacuum.aspirator at room.temper- ature (ca. 22°C.) or at 35°C. on a water bath. The conden- sation required ca. 18 hours. The 10 ml. condensate was diluted to 40 ml. for shipment as R-B 5. Results: Single ‘ieight change Sample dose Dose Result in . Remarks ‘ toxicity cc. Treated Controls R-B 4* - 0.5 - -5.5 dil. 1:10 -1.5 R-B 4* - 0.2 - ‘ -2.5 dlle 1:10 -1.5 16 Results: cont. Single weight change Sample dose Dose Result in . Remarks - toxicity cc. Treatedfiontrols 11-3 5*” . 1.0-0.5 + -5.0 1 died dil. 1:10 , 1'- :3 4* Suspended in 100 cc. saline H Diluted 1:2 with distilled water Discussion: the results indicated that the activity was apparently not precipitated with the "crude protein” at this concentration of ethanol, however the level of ~ dosage of the precipitated sample (R-B 4) was lower than that of the supernatant (R-B 5) which exhibited activity and might have accounted for the inability to demonstrate inhibition with the precipitate. The excessive solids extruded during clarification of the extractive resulted in a large amount of precipitate upon the addition of ethanol which was but slightly soluble and my have contributed to the results obtained with R-B 4. Since the activity was apparently not destroyed by the ethanol during this process and the length of time required for a preparation comparatively short, further studies using ethanol were attempted. The toxicity of R-B 5 was extremely high even at the dilution (1:20) used in the inhibition test and suggested the study of methods of decreasing this toxicity. Dialysis and absorption techniQue g; detoxification (R-B 6 , R-B 7, R-B a, R-B 9) 17 Extraction and filtration: a 40 g. sample was ex- tracted with distilled water (1:15) in a Haring Blender for 5 minutes and filtered with suction followed by addition- a1 filtration through a muslin bag pressed by hand. Precipitation: an equal volume of 95 per cent ethanol was added to the extractive and the mixture allowed to stand overnight in the cold. The precipitate was filtered off on a Buchner funnel and was discarded. The filtrate was condensed in a split-resin flask under reduced pressure with an aspirator to a thick syrup after 44 hours of evaporation. The condensation was carried out at room temperature. The condensate was washed into a graduate cylinder up to a volume of ’75 ml. It was noted that a lipid-like film developed on the walls of the flask and an attempt was made to scrape it off and combine it with the condensate. Separation and special treatment: the condensate was divided into three equal portions of 25 ml. each and treated as follows: 3. 11-5 6 -- 25 m1. of the condensate was packaged in a sterile bottle for testing without further treatment. B. R-B 7 -- a 25 m1. portion was trout-cc with 0.5 g. of Ruohar m and shaken for ca. 10 minutes and filtered twice with suction. About 7.0 ml. of the original treated solution was lost due to a water pressure drop at the as- pirator which allowed tap water to back into the filtering flask. The remaining sample was diluted to 55 ml. and 18 filtration continued. The filtrate was bottled for testing. The sample weight represented'by this fraction was ca. 9.5 g. whereas the samples R-B 6, R-B 8, and R98 9 represented ca. 15 g. of crude material. C. R-B 8 - a 25 m1. aliquot was dialyzed against 5 successive portions of 150 ml. of distilled water. The volume of this solution increased to ca. 52.5 ml. and was bottled for testing. D. R-B 9 - the dialysate from.R-B 8 was condensed under vacuum to a volume less than '70 ml. and was bottled for testing. Results: ...... _F' Single leight change Sample dose Dose Result in . Remarks - - toxicity- cc.‘ ‘ . ‘ -Treated-Controle R98 6 5.0 T Dil.to , 80 OOe R-B 7 5.0 0.6-0.5 17 -5.0 2 died 0 RpB 8 5.0 0.4-0.2 ? 5 died 3-3 s (retest) 1.0-0.5 t“ -e.5 1 died * 0 3-3 9 sec 0e4 " '2e5 0 Discussion: the inconclusive result reported for R-B 6 was probably due to its high toxicity. Treatment with Ruchar xxx apparently lowered the toxicity but not within practical limits for therapeutic use; however it did not result in loss of the activity of the sample. This lower 19 toxicity of the IIch sample might have resulted from the loss of a portion of the sample during filtration. Dialysis resulted in no significant decrease in toxicity. The nega- tive report of R-B 9 indicated that the active principle was non-dialyzable under the conditions of preparation. The discarding of the 50 per cent ethanol precipitate with the demonstration of the activity in the supernatant was taken as confirmation of the results obtained with R-B 4 and R-B 5. Pressing the extractive through muslin seemed to be a rapid means of crude clarification of the extractive only if further treatment provided for discarding the initial precipitate of ”crude protein". 1 The dialysis apparently removed the major portion of soluble carbohydrate since it was carried out until a Molisch test was negative, which tentatively suggested that the active principle was in the non-carbohydrate fraction. Consideration of the lowering of the surface tension and di-electrio constant of the extractive by the addition of ethanol with resultant precipitation of “crude protein“ suggested a study ofthe effects of acetoneas a preoipi-e tating agent since it likewise lowered the surface tension and di-electric constant of aqueous solutions. Since the hydroxyl and carbonyl functional groups in compounds confer different characteristics to them, the properties of materials precipitated by these two classes of compounds should be somewhat different. 20 52 P33 gent ethanol followed 13; acetone precipitation (R-B 10) Extraction and filtration: a 10 g. sample was extracted with 200 ml. of distilled water in a Haring Blender for 5 minutes and filtered with suction. Recovery ca. 1’70 ml. Initial precipitation: to the filtrate from above was added an equal volume of 95 per cent ethanol in the cold and allowed to stand ca. 6 hours. The precipitate was filtered off on a Buchner funnel with No. 2 whatnnn paper and discarded. The filtrate was collected and treated as follows: Condensation: the filtrate was condensed under re- duoed pressure in a split-resin flask at room temperature to a volume of ca. 18 m1. Dialysis: the condensate was washed into a dialysing bag and dialysed against successive changes of distilled water until the dialysate gave a negative Holisch test. Collection of fractions (R-B 10 and R-B 11): the residue in the dialysing membrane was collected in a beaker and cooled to 7°C. in equal volum of cold acetone was then added and the mixture allowed to stand 1} hours in the cold. The precipitate was dark brown in color and was very smll in weight and fine in texture. The precipitate was dissolved from the surface of the filter paper with distilled water (ca. 50 ml.) and filtered again to remove the inso1uble granules and paper. This fraction was sent for testing as R-B 10. The acetone supernatant from R-B 10 was condensed under 21 reduced pressure to a volume of ca. 10 m1. and transferred with washings toga sterile bottle for testing as R-B 11. Final volume 25 m1. Results: . Single ‘Weight change Sample dose Dose Result in . Remarks ' toxicity* cc. ‘ Treated Controls R-B 10 5.0 0.8-0.4 is" 4.0 2 died D11. to 80 Elle .5 o with dis. 320 ’ R“B 11 3.0 Oe5 2 3 diOd Dile to 80 Ille . with dis. 320 Discussion: although the weight of the precipitate of R-B 10 was small, the results indicated that the use of acetone as a precipitating agent should be further studied since it seemed not to destroy the activity. in interesting observation was noted in the results of the inhibition test of sample R-B 10. The apparent non- toxicity of the single dose treatment actually resulted in a cumulative toxicity during the course of the test killing two mice which suggested that an anaphylactic shock might have arisen from the repeated injections of the sample. That the dialysate fraction was extremely toxic and the test results inconclusive could not be interpreted as indica- ting the ability of 50 per cent acetone to effect complete separation of the active principle from the supernatant of the 50 per cent ethanol treatment. 22 Stability g; fractionation (acetone) techniques (R-B l2, ReB 13, R-B 17, R-B 13, R-B 19, R-B 20, Res 21, R-B 22, 8-3 25, 3-3 24, R-B 25). Extraction and filtration: a sample of ca. 45 g. was extracted with water (1:20) in a Waring Blendor for 5 minutes. After blending, the mixture was squeezed through a muslin bag to speed up the clarification. Considerable extrusion of the crude solids was noted. The extractive was measured at ca. 8'70 ml. Precipitation: after cooling the extractive to 7°c. an equal volume of 95 per cent ethanol was added and the mixture allowed to stand overnight in the cold. The pre- cipitate was filtered off with suction and discarded. The filtrate was transferred to a split-resin flask for con- densation. Condensation: the filtrate was evaporated under re- duced pressure for 6 hours in the flask. This process was not well adapted to such a large volume of solution and an alternate method attempted. The contents of the flask were transferred to a porcelain-lined photographic pan 14" x 18" x 2‘? and placed on a water bath at 55°C. under an exhaust. hood for 17 hours until the volume was reduced to ca. so ml. Dialysis: the condensate, which was dark brown in color and viscous, was washed into a dialysing membrane and dialyzed for 5 days against 2 liter portions of distilled water changed at intervals of ca. 6 hours except for 11 to 12 hour intervals overnight. The dialysis was discontinued 23 after the dialyzable portion of the pigment was removed (no apparent color change in.dialysate). The volume of the solution in the membrane was measured at 210 ml. which was an increase in volume of ca. 150 per cent. This solution was still extremely viscous. The solution was divided into 4 equal portions of ca. 50 ml. each and treated separately as follows: A. Acid stability (R-B l2, R-B l7, R-B 21) Fig. 3 .A 50 ml. portion was treated with ca. 5 drops of concentrated hydrochloric acid until the pH dropped to 2.0. ‘While at this low'pH the solution was shaken with.ca. 2 - 3 per cent Nuohar'xxx and filtered with.cuotion. The Huohar was added to the solution in a 250 ml. centrifuge bottle and shaken.by hand for ca. 2 minutes. After filtra- tion, the pH‘lIl raised to 5.1 with.lO per cent sodium hydroxide (pH of the solution prior to acid addition) and the solution condensed under a vacuum.to a volume of 14:ml. Separation of fractions (3-3 12, RAB 17, 8-3 21) Fig. 3: the 14 ml. condensate was made 80 per cent by volume of acetone by the addition.cf'55 ml. cf’acetone and allowed to stand 15 - 30 minutes at room.temperature. The precipitate was centrifuged and the supernatant decanted for further treatment as RAB 17. The precipitate was dried under a stream.of air, dissolved in 50 m1. of water and bottled for testing as R-B 12. The acctone supernatant from.R-B 12 was evaporated under a stream.of air to remove the acetone for ca. 3 hours ligure 3 fi—B l2, d-L 17 and 1+: 21 Crude Laterial 1. Ground to 60 mesh _ 2. Extracted with H20 (1:20) in Waring filendor 3. Clarified through uncleached muslin h. fade hQZ by volume with 95% ethanol at 703 5. Stood overnight at 7°C 6. Filtered with suction (Ho. 2 Hhatman paper) 5’ v 6 Extractive l. Concentrated under reduced pressure 2. Concentrated on 35°C water bath 3. cialyzed 3 days at ca. 2103 I t . it Lembrane solution oialySite discarded 1. pH lowered to 2.0 with NC a. Shaken with Huchar liX b. ?iltered with suction - Solid residue discarded l 1 Iuchar discarded Filtrate . 1. pH raised to 5.1 with HaOH 2. Condensed under vacuum 3. Lade 30» acetone by volume h. stood 15-30 minutes at ca. 2103 S. Centrifuged 7—3 12 l {—7 I Lrecipitate Supernitint l. tried under air current I 2. Lissolved in H20 fl ‘ . l. concentrated under air current .. . . .. a ""4, ‘3’)! ' a -- Inhlzutlon test results (.i—y; 12)- 2. ..:;-de ,5 ace/torque by volmaem Toxicity _ < 1.0) ,. icood' or ca. 2 hours at 7 t Inhioition _ (’) b. centrifuged 1—7 17 _2:B 2l Yrecipitate Supernatant 1. dried under air current 1. Iried under air current 2. Lissolved in HQO 2. Residue dissolved in H2O Inhibition test results (3-3 1?) Inhibition test results (24% 21) Toxicity — ()l.O) Toxicity — C)l.O) Inhibition - (-) ' Inhioition - (-) 24 and it was observed that as the volume lowered white cry- stalline materials appeared at dry surfaces left by the receding solution. The condensate, however, remained a clear straw color. After the condensate was evaporated to 6 ml., 54 m1. of acetone were added giving a solution 90 per cent acetone by volume which.was allowed to stand in the cold for ca. 2 hours. A precipitate was formed and was centrifuged, decanted, air dried and dissolved in.40 ml. of water and shipped as 3-3 17. - The decanted supernatant from R-B 17 was evaporated to dryness and the residue dissolved (with difficulty) in 30 ml. of water and shipped as R-B 21. Results: _fl' Single weight change Sample dose Dose Result in . Remarks toxicity co.' Treated/gontrols R-B 12 1.0 0.8-0.4 - -5.0 dil. 1:5 ‘5'— R-B 17 1.0 0.8 - g dile 135 O R-B 21 1.0 Oe5.0e25 - -3.0 1 d16d 0' Discussion: the results prompted two major con- siderations of the procedure. First, it was not known whether the activity was actually present in the medium after the prolonged periods of condensation and dialysis, but previoue experience suggested that its stability under these processes was very good and that it could be demen- 25 strated just prior to the acid treatment. Secondly, the high concentrations (80 and 90 per cent) of acetone were not known to be injurious to the active principle, but concen- tration of 50 per cent acetone had not been shown to destroy the active principle (R-B 10). These results, assuming-the activity present prior to acid addition and nonpdostruotion of activity by 80 - 90 per cent acetone, were interpreted as indicating that the active principle was acid labile. B. Alkali stability (R-B 15, R-B 18, R-B 22) A 50 ml. aliquot of the original extractive after treatment with.50 per cent ethanol, condensation, and dialysis was treated with a 10 per cent solution of sodium hydroxide to a pH of 8.9 and then shaken with 2 - 5 per cent Euchar'xxx.and filtered with.suotion. The pH was lowered to 5.1 with concentrated hydrochloric acid after filtration, and the solution condensed under vacuum.to 21 ml. Separation of fractions (R-B l5, RAB 18, R-B 22): the 21 md. condensate was made 80 per cent acetone and allowed to stand 15‘ - so minutes then centrifuged. The supernatant was decanted and treated further as R-B 18. The precipitate was dried under an air current and dissolved (with.difficulty) in.4o ml. of water for testing as 8-3 15. The supernatant was evaporated to a volume of 11.5 ml. similarly to R-B 17 above, cooled to 7°C. and acetone added to a concentration of 80 per cent. It was noted that the cloudiness observed in the medium.at this concentration of 26 acetone during the acid treatment was not present and the concentration of acetone was increased to 90 per cent. After standing in the cold for ca. 2 hours, a slight gummy precipitate, dark brown in color, was centrifuged down. The supernatant was decanted and treated as R-B 22. The precipitate was dried under an air current and dissolved in water for testing as R-B 18. The supernatant was not further fractionated but was evaporated to dryness in a stream.of air and the residue dissolved in water as 3-8 22. Results: Single ‘Weight change Sample dose Dose Result in . Remarks toxicity cc. Treated Controls, R-B 15 0.5 0.8-0.4 - -l.5 dil. 1310 o 8-3 18 I 1.0 0.5 - -c.5 0 3-8 22 1.0 0.5 - g 0 _ Discussion: the difference in weight of the precipitates collected from the acid and alkali treated samples suggested that either the alkaline medium enhanced the absorptive ability of the Euchar’xxx toward the material in solution or that appreciable hydrolysis occurred during the short interval (ca. 15 hours) that the medium.was alkaline to a pH of 8.9. That the latter was the case was suggested by the viscoue nature of the alkaline treated 27 precipitate as compared to the fluffy nature of the acid precipitate. Following the assumptions made in the interpretation of the results of R-B 12, R-B 17, and R-B 21, the results of these tests were interpreted as indicating the alkali lability of the active principle. 0. Stability at 80 and 90 per cent acetone concen- trations (R-B 19, R-B 20, R-B 23) The pH of a 50 ml. portion of the extractive after 50 per cent ethanol treatment, condensation and dialysis was determined as 5.1 with a pH meter. The sample was treated with.Nuchar*xxx.as described under 3-8 12 (acid stability) above. The filtrate was con- centrated to 15 ml. and.made 80 per cent acetone and allowed to stand in the cold for ca. 2 hours. The precipitate was considerably heavier than observed in the acid or alkali treatments and was centrifuged for collection. The super- natant was decanted for further treatment as BpB 20. After drying the precipitate in an air current, it was taken up in 40 m1. of water for testing as R-B 19. The supernatant of 3-8 19 was evaporated to a volume of 9 ml. and.made 90 per cent acetone by the addition of 81 ml. of acetone and.allowed to stand overnight in the cold. The supernatant was decanted from the precipitate and treated as R-B 23. The precipitate was taken up.in.45 ml. of water for testing as RPB 20. 28 The supernatant from.R-B 20 was evaporated to remove the acetone but was not carried to dryness. The final volume was less than 45 ml. and was bottled for testing as 3-3 23s Results: Single 'Weight change Sample dose Dose Result in g. Remarks toxicity co. . Treated/Controls 3-13 19 1.0 0.5-0.1 t’ -:5.0 1 died 3-3 20 1.0 0.5 - -1.0 0 3-8 23 1.0 1.0 - -1 0 an. 1.35 "'6':- Discussion: the results seemed to confirm the stability of the active principle through.extended periods of time under the conditions described for condensation and dialysis at room.temperature. Also its stability at 80 per cent acetone concentrations was indicated and suggested further study of acatone as a direct precipitating agent. The negative result at the 90 per cent acetone level could not be interpreted as indicating instability but rather that the active principle was precipitated from.the medium.at the lower concentration. The result of RPB 19 was taken as confirmation of the activity of fraction RPB 10. D..Acid hydrolysis (R93 24, R-B 25) From.the original sample after 50 per cent ethanol treatment, condensation, and dialysis the fourth 29 aliquot of 50 ml. was treated with concentrated hydrochloric acid to a pH less than 1.0 and allowed to stand in the cold for 4 days. The solution was dialysed to a pH ca. 4.0 until the dialysate gave no test for carbohydrates (Molisch). After dialysis, the solution was concentrated and then made '70 per cent acetone and allowed to stand in the cold over- night. The precipitate was centrifuged and the supernatant decanted and treated as R-B 25. The precipitate was dissolved in 45 m1. of water and bottled for testing as R-B 24. The supernatant was evaporated to 7.5 ml. and made 80 per cent acetone without any sign of formation of a pre- cipitate (cloudiness). The concentration of acetone was increased to 90 per cent and the mixture allowed to stand overnight in the cold. No precipitate was formed and the solution was evaporated to remove the acetone and the residue (ca. 6 ml.) was diluted with water to 45 m1. and bottled for testing as R-B 25. Results: Single Weight change Sample dose Dose Result in 3. Remarks toxicity cc. A Treated/Controls R-B 24 1.0 0.5-0.25 - 9_ O R’B 25 1.0 0.5 - 9. 0 Discussion: the results clearly confirmed the acid} lability of the active principle. 30 Re-extrac_t:_igp_ _an_g._ modified ethanol precipitation W (R-B 26, 11-13 27, R-B 28, and R-B 29). Extraction.and centrifugation: a 20 g. sample was water extracted (1:21) in a'waring Blender for 5 minutes and was centrifuged. The precipitate was separated from the supernatant and was treated as R-B 27. The supernatant was treated as follows: Precipitation: the supernatant was made 50 per cent by volume with 95 per cent ethanol and allowed to stand overnight in the cold. The precipitate was filtered off with suction and the filtrate condensed.under an air current to 15 ml. The condensate was washed.into a dialyzing meme brane and dialysed for several days at room.temperature against 2 liter portions of water with.frequent changes until a cloudiness was observed in the dialysate. It was also noted that a precipitate had formed in the bag. Collection of fractions (R-B 28, RAB 29): the solution in the dialyzing bag was centrifuged and the supernatant decanted and treated as R-B 29. The precipitate was dried in an air current and taken up in physiological saline for it appeared to be globulin-like in.nature. This fraction was numbered 3-8 26 for testing. The supernatant.frcm R-B 26 was made 60 per cent ace- tone and allowed to stand in the cold. The precipitate formed was centrifuged, dried in air and taken.up in water for testing as R98 29. Re-extraotion (R-B 27 and R-B 28): the solid residue 31 after separation from the extractive by centrifugation was re-extracted with.water (1:20) in a flaring Blender for 5 minutes to ascertain if the method of extraction was quan- titative with a single extraction. The further treatment of this additional extractive was similar to that as described under R-B 26 and R-B 29. It consisted of filtration, treatment of the extractive with 50 per cent ethanol, condensation and dialysis for the same periods of time. It was observed that the cloudinets of the dialysate develOped and a precipitate formed in the dialyzing bag similarly to fractions R-B 26 and R-B 29. Collection of fractions: the precipitate in the bag was centrifuged, dried and taken up in water for testing as R-B 27. The supernatant of R-B 27 was not further treated with acetone to 60 per cent to precipitate the active prin- ciple since the concentration of the active principle in the second extraction was unknown and the quantitative separation with.acetone had not been confirmed by previous treatments. This supernatant was diluted to 45 ml. with water and bottled for testing as R-B 28. Results: Single weight change Sample dose Dose Result in . Remarks toxicity cc. Treated/gentrols R-B 26 5.0 0.6-0.5 1;" -2.0 orig. dile O 1:100 R-B 26 (retest) 0.6 - -3=5 orig. dil. 1.5 1:1000 52 Results: cont. Single Weight change Sample dose Dose Result in . Remarks toxicity cc. Treated/gontrols 8.3 27 5.0 0.5-0.25 " -105 0 R-B 28 1.0 0.25 1? -5.0 0 R'B 29 3.0 005.002 $.- 7.0 orig. dil. 0 1:100 3-3 29 (retest) 0.3-0.7 ;* -3.o orig. dile 1.5 1:1000 Discussion: the most significant result reported to date in this study was that of fraction R-B 29 which.was diluted 1000 fold and, given at a relatively low'dosage level, yet produced greater inhibition than at a higher concentration. This result suggested that the active factor was not identical with.the toxic portion of the prep- aration and could possibly be separated from.it; but this could not be interpreted to mean that the active factor was inherently non-toxic. The results of R-B 26 and R-B 27 seemed to be conflicting in that the two precipitates formed upon prolonged dialysis gave quite different results; however, the relative concen- tration of the active principle in the first extractive was perhaps several times greater than in the second extractive which might account for these results.‘ Since the amounts of ,V 33 the two precipitates were comparable, it was improbable that they were in themselves actually the inhibitory factor, but that some of the activity was occluded in the formation of the precipitate from.the more concentrated solution of the first extractive. No explanation was given for the dilution of samples R-B 26 and R-B 27 which were apparently non-toxic in . single dose. This dilution may have accounted for the negative results obtained with these fractions. The precipitate formed in the dialyxing.memhrane may have been the result of insufficient clarification of the extractive by centrifugation. §_C_)_ £35; gent ethanol followed by dialysis and acetone f__1:_a_g- tionation (R-B 30, R-B 31, R-B 32, R-B 33) Fig. 4. Extraction and filtration: a 10 g. sample was extracted with.water (1:20) in a flaring Blender for 3 minutes and filtered on a Buchner funnel with.Re. 2 Whatman paper. Precipitation, concentration, and dialysis: the fil- trate from.abeve was made 50 per cent ethanol and allowed to stand overnight in the cold. The precipitate was filtered off and discarded. The filtrate was condensed under an air current to remove the ethanol and then dialyzed for 3i-days against successive 6 liter portions of distilled water. No precipitation occurred during this dialysis as observed with R-B 26 and R-B 27. Fractionation: the solution in the dialyzing membrane was fractionated as described below: Figure h R—S 30, R—B 31, R-B 32 and 3.3 33 Crude Katerial l. Extracted with H 0 (1:20) in Waring Blendor 2. Extractive made 0% ethanol at 7°C 3. Stood overnight at 7°C h. Filtered with suction r + Supernatant Precipitate discarded 1. Condensed under air current 2. Dialyzed 3% days at ca. 21°C 3. Kade hBZ acetone at 7°C h. Stood overnight at 7°C 5. Centrifuged + I 8:3 30 Supernatant Precipitate l. Eade 55$ acetone at 7°C :' éir diieg . q 0 2. Stood ca. 8 hours at 7°C ' “1880 vs 1n ‘2 3. Centrifuged Inhibition test results (R-B 30) Toxicity - (5.0) ng3¥31 1 Inhibition - (—) Precipitate Supernatant 1, Air dried . l. Iade 70% acetone at 7°C 2. sissolved in qu 2. Stood overnight at 7°C Inhibition test résuite: 3. Centrifused Toxicity -(S.0) Inhibition - (-) R~3_32 3—3 337 Precipitate Supernatant 1. Air dried l. Acetone evaporated in air 2. Dissolved in H20 2. Residue diluted with H20 Inhibition test results (3-8 32) Inhibition test results (2-3 33) Toxicity - (5.0) Toxicity — (5.0) Inhibition - (-) ’ Inhibition - (-) 54 Acetone was added to the solution until a cloudiness developed at a concentration of 48 per cent and the mixture allowed to stand overnight in the cold. The precipitation was very slight but was centrifuged and the supernatant decanted and treated as R-B 31. The precipitate was dried in air and taken up in water for testing as R-B 30. To the supernatant was then added sufficient acetone to develop a cloudiness (55 per cent) and the solution allowed to stand in the cold for ca. 8 hours. The precip- itation was slight but was centrifuged and the supernatant decanted. The precipitate was taken up in water for testing as R-B 31. The supernatant from R-B 31 was made 70 per cent ace- tone (first cloudiness) and allowed to stand overnight in the cold. The precipitation was again slight and the pre- cipitate collected by centrifugation, dried in air and taken up in water for testing as R-B 32. The supernatant from R-B 31 was evaporated to remove the acetone, diluted to ca. 40 ml. with distilled water and bottled and sent for testing as R-B 33. Results: Single 7 weight change V Sample dose Dose Result in . Remarks " ' * toxicity cc. Treated Controls R-B 30 5 00 0 .8 - .230 '0 R-B 31 5.0 0.8-0.4 - O 5* 1 died 5.5 R-B 32 500 0.6.0.4 "' -100 Oe 0| 55 Results: cont. Single ‘Weight change Sample dose Dose Result in 3. Remarks toxicity cc. Treated/Controls .n 3.3 53 5.0 0.0 - -105 0.5 Discussion: since activity had been.demonstrated in the supernatant after treatment with 50 per cent ethanol and dialysis for extended periods (R93 29) an attempt was made to use acetone as a fractionating agent. The criteria of fractionation was taken as first apparent cloudiness of the mixture. The results reported here indicated that the activity was apparently lost before the fractionation was attempted, however several factors were considered in the interpretation of these results. First, the weight of crude sample represented by these was small. Secondly, the amount of’precipitate collected at each.fracticnating con- centration of acetone was extremely slight. Also, the length of time that the material was in contact with high concentrations of acetone may have resulted in loss of activity. This total time at concentrations above 48 per cent acetone was greater than 36 hours. These results suggested three modifications in the general procedure: (1) to increase the weight of crude sample represented by the fractions, (2) direct precipitation with acetone after the 50 per cent ethanol treatment excluding the process of dialysis, and (:5) to decrease the length of time required for concentration and dialysis. 36 §_(_)_ 33;; gent etflol followed by dialysis 2.99. acetone gagg- tionation (modified - sample weight doubled) (R-B 34, R-B 35, R-B 36). Extraction and filtration: a 20 g. sample was ex- tracted with water (1:20) in a waring Blendor for 3 minutes and filtered with.suotion. Precipitation, concentration, and dialysis: the pro- cedure followed was the same as described under the prepar- ation of fractions R-B 30, R-B 31, R-B 32, and RPB 33 on page 33. The extractive after ethanol treatment, condensation, and dialysis was fractionated similarly to the previous sample with.twc exceptions: the upper limit of the fraction- ation was 65 per cent acetone instead of 70 per cent as in R-B 32 and the supernatant of the 65 per cent acetone pre- cipitate was not freed of acetone and tested for inhibition as was R-B 33. Results: Single ‘7 ‘leight change Sample dose Dose Result in g. Remarks toxicity cc. Treated/Controls" ‘ R93 34 5.0 0.8 1 3 died a-s :55 5.0 0.3 ..' -2,‘o 1 died -O.5 R-B 56 3.0 0.4-0.2 2 4 died Discussion: the inconclusive and negative results obtained with.these fractions could not be interpreted as confirmation of activity after the ethanol and subsequent 3'7 treatments prior to attempted fractionation with acetone : however, the low toxicity of a single dose followed by the cusmlative toxicity as observed with fraction R-B lo landed support to the belief that the activity was still present. The results seemed to indicate that acetone following ethanol would not effect the desired separation. is of necessity, the length of time required in the preparation of fractions by this procedure was long, and the possibility that the activity was lost or diminished on standing could not be excluded in suggestions for modification of this method. It was decided to shorten the time of concentration and dialysis, and to attempt a single acetone precipitation technique (after ethanol) at a concentration midway between that of R-B 34 and R-B 36, is. ca. 57 per cent acetone. Direct acetone precipitation (rapid method) (R-B 37, R-B as) b Extraction and filtration: a 20 g. sample was extracted with water (1:20) in a Waring Blendor for 3 minutes and filtered with suction using No. 2 Whatman paper. Precipitation and condensation: the extractive was cooled to 7°c. and made so per cent ethanol and the mix- ture allowed to stand overnight. The precipitate was filtered off with suction and discarded. The filtrate was condensed under vacuum using a dry ice trap. The time of condensation was ca. 4 hours. Dialysis and separation of fractions: the condensate was dialyzed on the rotating apparatus for 3% hours against two portions of 6 liters of distilled water. It was noted that a precipitate formed after ca. 2 hours in the bag. This pricipitate was collected by centrifugation, air dried, and dissolved in 50 ml. of water for testing as R-B 37. The supernatant was made 67 per cent acetone and allowed to stand in the cold for ca. 6 hours. The precipitate formed was collected by centrifugation and.was taken up in water and redialyzed for 2 hours to attempt removal of pigment. The pigment was non-dialyzable. The volume of the solution in the dialyzing membrane was measured as 90 ml. ‘An attempt to reprecipitate the active principle was made by making this solution 57 per cent acetone and allowing to stand overnight in the cold. There was no apparent separation effected.by the second precipitation. After the removal of the acetone by an air current, the residue was diluted and bottled as R-B 38. .Results: Single Height change Sample dose Dose Result in 3. Remarks toxicity ace. . ‘Treated/Controls 3.8 37 5.0 0.5-00‘ - .430 -100 3.3 as . 3.0 0.5-0.25 : p 3 died v—.._ —_—_ Discussion: the negative result of R-B 37 was inter- preted as confirmation of the assumption that the precipi- tates collected as R-B 26 and R-B 27 were not separated portions of the active principle. The inconclusive result .of £93 38 was attribued to the lethal effect on the treated mice and could not confirm.the assumption that the active 39 principle was present in the treated sample prior to the precipitation with acetone as carried out in this procedure. The results of the use of acetone following ethanol tech! niques as reported here, and consideration of the precipi- tating characteristics of these two substances suggested that a study be made utilizing acetone, without ethanol, to attempt isolation of the active principle. gigggt’aoetone precipitation agg.reprccipitation.(R-B 39, 863 40, 393 41, R-B 42, R-B 43, R-B 44) Fig. 5. Extraction.and filtration: a 15 3. sample was ex- tracted with water (1:25) in a waring Blendor for 3 minutes and filtered twice on a Buchner funnel. Dialysis: the extractive was dialyzed for 2% hours against 6 liters of distilled.water changed once at 1} hours. No precipitation was observed. I Precipitation: the extractive after dialysis was placed in the cold and made 31 per cent acetone and allowed to stand overnight in the cold. It was assumed that the character of the precipitate would‘be similar to that obtained with ethanol at 50 per cent concentration. The precipitate was collected by centrifugation, the supernatant was treated as described below. The precipitate was air .dried and taken up in physiological saline and.dialyzed for ca. 1%- hours against 1 liter of distilled water changed once. The suspension of the precipitate in the dialyzing bag was centrifuged, and the precipitate was taken up in Figure 5 3—3 39, 2-3 ho, 3-5 hl and R—B h2 Crude Katerial 1. EXtracted with 320 (1:25) in a Waring Blendor 2. Extractive dialyzed 2} hours at ca. 21°C 3. Extractive made 31% acetone at 7°C h. Stood overnight at 7°C 5. Centrifuged R-Z 3'? _ m at... ,i —»+ Preci itate :17 ‘r” d‘” 1. TakenPup in saline 1. Made Elk acetone at 7°C 2 Dialyzed ca 2 hours 2. Centrifuged (Supernatant R-B h3) . . 3. Ppt. dissolved in H20 Inhibition test results (R-B 39) h' Dialyzeg 3 h°ur5 O toxicity _ no report 5. Made 51h acetone at 7 C Inhibition _ (1—) 6. StOOd 3% hours at 70C 7. Ce trifuged - T as ho, Supernatant Precipitate 1. Kade 55% acetone at 7°C ‘ ' l. Dissolved in H O 2. Stood h hours at 7°C Inhibition test results Rafi hO) 3. Centrifuged Toxicity - no report Inhibition - (-) :jfgigg I . R—B hz ._1 Precipitate ' ' Supergatant 1. Lissolved in H90 1. bade 75p acetone at 7°C ~ 2. Stood overnight at 7°C Inhibition test results (3.3 t1) 3- Centrifused Toxicity — no report R;B hp I Inhibition - (1*) f t Precipitate Supernatant discarded 1. Dissolved in H20 Inhibition test results (Rea h2) Toxicity - no report Inhibition - (s+) 4O physiological saline for testing as R-B 39. Fractionation above 31 per cent acetone (R-B 40, R-B 41, R-B 42, R-B 4:5, R-B 44) The supernatant from the 31 per cent precipitation was further treated with.acetone to a concentration of 57 per cent and allowed to stand overnight in the cold. The precipitate was collected by centrifugation and taken up in water for subsequent fractionation and the supernatant collected and treated as described below under R-B 43. The 57 per cent acetone precipitate after being disper- sed in water was dialyzed for 3 hours and fractionation attempted as follows: The solution was made 51 per cent acetone and allowed to stand in the cold for 3% hours. The precipitate was collected by centrifugation and taken up in water for test- ing as R-B 40. The supernatant from.R~B 40 was made 55 per cent acetone and the precipitate collected after 4 hours of standing in the cold. The precipitate was taken up in 35 ml. of water for testing as R-B 41. The supernatant from.R-B 41 was further treated to 75 per cent acetone and allowed to stand overnight in the cold. It was noted that the supernatant of the 75 per cent treatment was colorless after standing overnight and it was assumed that the separation of the precipitatable material was complete within practical limits. The precipitate was taken up in 50 ml. of water as R-B 42. 41 The supernatant from R-B 40, after the 57 per cent acetone precipitate was removed, was condensed.under an air currect to a volume of 240 m1. and then made 68 per cent acetone in the cold. After ca. 3 hours the precipi- tate was collected by centrifugation and taken up in water for testing as R-B 43. The supernatant from R-B 43 was then.made 75 per cent acetone and allowed to stand in the cold for ca. 3 hours. The precipitate was collected.by centrifugation and taken up in water for testing as R-B 44. Results: Single ‘leight change Sample dose Dose Results in . Remarks toxicity cc. Treats Controls - ' R-B 39 0.3-0.1 . if -2.5 ~2.0 R-B 40 0.3 - -2:O -2.0 R-B 41 0.5-0.1 1+ ~5,c 2 died .. "2.0 R-B 42 e.s-c.1 s.” :32 2 died -2.0 R-B 43 5.0 0.6-0.3 - ‘:;g§ .200 R-B 44 Samplelost after shipment Discussion: the result of R-B 39 indicated that a portion of the active principle was precipitated by 31 per cent acetone, which.was unexpected by the slight differences between acetone and ethanol as precipitating agents. The negative result of R-B 40 may have been due to an insufficient 42 amount of the active principle in the precipitate which in itself was slight. The demonstration of activity in samples R-B 41 and R-B 42 supported evidence that acetone could not be used as a fractionating agent in this procedure for separating the active principle from.the toxic materials. The negative result of R-B 43 suggested that the precipi- tation of the active principle was complete below an.acetone concentration of 68 per cent in the extractive. Experience prompted a serious objection to this particular method of isolation. The length of time during which the extractive was kept in the presence of high.concentrations of acetone, even.in the cold, may have altered the structure of the active principle and possibly its activity. The differences in concentration of acetone at which.fractions were collected did not seem to be far enough apart to be suitable in a generalized procedure involving the use of acetone due to its high.volatility even at the temperature of the cold room used (7°C.). After consideration of the results described here, it was considered advisable to modify this method of fraction- ation in an effort to shorten the 1ength.of time during which.the extractive was held in the presence of high.acetone concentrations. The method suggested was to employ a process involving only two precipitations from a single sample. This method was employed in the preparation of fractions R-B 46, R-B 47, R-B 48, and R-B 49. 43 Detoxification technique (Pancreatin digestion) (R-B 45). Extraction and filtration: a 15 g. sample was extracted with.water (1:20) in a waring Blendor for 3 minutes and filtered with suction. Ethanol precipitation: the extractive was made 50 per cent .thnnol'end allowed to stand overnight in the cold. The precipitate was centrifuged off and discarded and the supernatant treated as follows: Concentration: the supernatant was condensed under vacuum.using a dry ice trap to remove the alcohol. Time ca. 5 hours. . Dialysis: the condensate was dialyzed for 4% hours against 6% liters of distilled water with.two changes. No precipitation was noted. Acetone fractionation: the residue in the dialyzing membrane was made 48 per cent acetone and allowed to stand overnight in the cold. The precipitate was collected.by centrifugation and stored in a refrigerator for ca. 24 hours. The supernatant was treated with additional acetone to a concentration of 57 per cent and allowed to stand in the cold for ca. 24 hours. The precipitate was collected by centrifugation and combined with the precipitate collected at 48 per cent acetone. This combined.material was taken up in 45 ml. of water and treated as follows: Pancreatin digestion: the solution of precipitates was allowed to stand 18 hours at room temperature after the addition of 0.5 per cent pancreatin? and mixing. After 18 hours, the mixture was filtered with.suotion and the filtrate collected. The volume of the filtrate was 64 ml. and was bottled for testing as R-B 45 without dilution. Results: Single weight change Sample dose Dose Result in g. Remarks toxicity cc. Treated/Controls R-B 45 3e0 0e4-003 1 3 died Discussion: this inconclusive result could not be interpreted as indicating that the panoreatin digestion was effective in detoxifying the active fraction, but rather suggested that either the pancreatin in solution was toxic to the mice or that possibly bacterial toxins were produced in the medium during the period of digestion.** ‘Acetone fractionation (2 step method) (R-B 46, R-B 47, R-B 48, R-B 49) Fig. 6. Extraction and filtration: three separate 15 3. samples were extracted with.water (1:20) in a Faring Blendor for 3 minutes and filtered on separate Buchner funnels using No. 2 Whatman paper. The three filtrates were treated individually as follows: 4* Panel-satin (ms-P. XI). Line. by Difoo Laboratories. ii The use of enzymatic digestion as a means of detoxi- fication was suggested by Dr. C. 0. Stock of the Division of Experimental Chemotherapy, Sloan-Kettering Institue for Cancer Research. figure 6 1".) ‘ L7 3.116. 11-; L3 Srudc Hatcrial {fronted in duplicate) 1. Extract with HaO (l: G) in tiring blender 2. ziltc red th suction' a. holid r~cuducf discarded (fixtructivcs treated separately A and *) It 1. Extractive made 553 acetone at 7°C 2. Stood 5: hours at 7°C 3. Centrifugcd ”_fi LE 1 Precipitate Gupcrna tant 1. Air dried i. Laue 60 acetone at 7Ou 2. Suspended in 320 2. ctood overnight at 7°C6 Inhibition test results \t-- 36) 3. Centrifuged Toxicity — (0.5} 7—3 Q7 1 lnhioition -<-) '—* M" ‘ I irocipitdte Supern;tant discarded 1. Air dried 2. hissolvcc in H60 InLiuition test results (fi-B h?) Soxicity - (3.0) B Inhinition - (1‘) 1. Extractive made 63% acetone at 7°C 2. Stood Sg hours it 70; 3. Jcntrifugcd Precioitate dis co rdcd Lun':rn tart 55 l. AVILUL -—/\J I) L. 3. 24:2 Precipitatc Air dried his solved in }.(O InhiJition test results (Y-B h8) Toxicity - (5.0) Inhibition — (i-) 17 4 l. ? acetone at 7°C Stood*cvc1night at 703 Centrifgped i Supernitint.discardcd 45 A. (R-B 46 and R-B 47): the extractive was made 55 per cent acetone and allowed to stand in the cold for 5% hours, the precipitate collected by centrifugation, air dried, and taken up in 80 ml. of water for testing as R-B 4d. The supernatant volume was measured and additional acetone added to a concentration or do per cent and the solution allowed to stand in the cold overnight. The pre- cipitate was collected‘by centrifugation, air dried, and taken up in 80 ml. or water for testing as R-B 47. B. (R-B 48): a second extractive was treated with acetone directly to a concentration of do per cent and allowed to stand in the cold for 5} hours. ’The precipi- tate was centrifuged down and discarded. The supernatant was then.made.65 per cent acetone and allowed to stand overnight in the cold. The precipitate was collected by centrifugation, air dried, and taken up in 80 ml. or water for testing as R—B 48. c. (R-B 49): the third extractive was treated with acetone directly to a concentration of 65 per cent and allowed to stand in the cold for 5% hours.- The precipitate was centrifuged down and discarded. The supernatant was then.made 70 per cent acetone and allowed to stand overnight in the cold. The precipitate was collected by centrifugation, air dried, and taken up in 80 ml. or water for testing as R-B 49. 46 Results: Single ‘Weight change Sample dose Dose Result in 3. Remarks toxicity cc. Treated/Controls R-B 46 0.5 0.6-0.5 1" -3.0 2 died dil. 1:5 -1,o R-B 46 (retest) 0.6 1* -:5.0 dile 1:5 ~2.0 R-B 47 3.0 0.5-0.2 xf’ -5.5 1 died -100 R-B 47 (retest) -0.5-0.25 '1’ -5,0 .290 R-B 48 5.0 0.6-0e3 :- .5” 2 6.1“ -1.0 R-B 49 5.0 0.6 1' -3.5 1 died -l.0 Discussion: the results could not be interpreted as a confirmation of the ability of acetone as a fractionating agent for the active principle within this range of concen- tration. : The apparently conflicting toxicity results were inter- preted as confirming the extreme toxicity of the “crude protein" precipitated at relatively low acetone concentrations and suggested that the cunmlative toxicity could be attrib- uted to the active principle. That the activity was appar- ently evenly distributed in the 55 - 60 per cent, 60 - 65 per cent, and 65 - 70 per cent precipitations and that a comparatively lower toxicity was observed with these frac- tions supported the belief that the two step method could be modified to obtain the major portion of the active prin- 47 ciple in the extractive relatively free from.the highly toxic “crude protein“. The modifications suggested by these considerations were two in number: (1) that the range of acetone concentrations over which.a single pre- cipitate be taken be widened using 55 per cent acetone as a lower limit and 75 per cent as an upper limit, and (2) that rather than utilize different acetone concentrations as criteria for fractionations, allow time to be the vari- able with a constant concentration of acetone. Detoxification techniquo‘(Trypsin) (R-B 50, R-B 51) Extraction and filtration: duplicate 15 g. samples were extracted with.water (1:20) in a Waring Blendor for 5 minutes and filtered with suction. The extractives‘were treated as duplicates in the fractionation procedure followed below. The extractives were made 55 per cent acetone and allowed to stand in the cold for 5% hours, the precipitates centrifuged down and discarded. The supernatants vere further treated with.acetone to 75 per cent and allowed to stand overnight. The precipitates were centrifuged, air dried, and taken up in 80 ml. of distilled water for the tryptic treatment. These samples were numbered as R-B 50 and R-B 51 and shipped to Dr. C. 0. Stock, Division of Experimental Chemotherapy, SloanAKettering Institute for Cancer Research, New York, New York, for further treatment with crystalline trypsin. 48 The technique of the tryptic digest was not reported for these samples, but the inhibition test results were reported. Results: Single 'Weight change Sample dose Dose Result in 3. Remarks - toxicity cc. Treated/Controls R-B 5O dil. 1:10 1.0 - -230 -105 R-B 51 1 control for trypsin _ 1.0 ' .2'e5‘ -155 2 control for trypsin :- l.O ~4,o -l.5 Discussion: these results could not be interpreted as confirming the ability of crystalline trypsin to detoxify the active principle, bum suggested further study. _5_§ £93; 9322 acetone precipitation (single stop method) (R-B 52, R-B 53, R-B 54). The result of a retest of fraction.R-B 46 indicated that although the single dose toxicity was extremely high ’ (o.5) no mice died during the inhibition test. It was re- quested by Dr. Stock that a similar preparation be sent to be tested for anti-tumor activity against other tumors (spectrum). For these preparations, 15 3. samples were treated in triplicate following the procedure described under R-B 46 (page 45). , The triplicate samples of 80 ml. were numbered R~B 52, R-B 53, and R-B '54 respectively and shipped for testing. The results of the spectrum.had not been reported at the date of this writing, but the results of the sarcoma 180 test were reported. Results: Single ‘Weight change Sample dose Dose Result in . Remarks toxicity oc." “ ‘ ‘Treated Controls R-B 52 1.0 1.0-0.5 1 4 died d11e 185, Discussion: this result indicated that the toxicity of the "crude protein" in this preparation was apparently responsible for the inconclusiveness of the inhibition test. leetone fractionation (variable time method) (R-B 55, R-B 56). is was suggested in the discussion of fractions R-B 46 - R-B 49 a study was made of the effect of’time on the charac- teristics of the material precipitated by acetone from the extractive. Excessive acetone (90 per cent) was selected as the "constant“ factor in this procedure and two fractions were obtained: the first collected about 10 minutes after the addition of the acetone to the extractive, and the second after allowing the mixture to stand overnight in the cold. Extraction and filtration: a 15 g. sample was extracted with.water (1:20) in a waring Blendor and filtered with 49 suction. Fractionation: the extractive volume was measured as 250 m1. and placed in the cold (7°C.). After reaching thermal equilibrium.sufficient cold acetone (1,950 mi.) to be excessive (90 per cent) was added to the extractive and mixed by swirling. Immediately after mixing, the solution was filtered with suction as rapidly as possible (ca. 10 min.) on two 6 inch.Buchner funnels using No. 50 Whatman paper. The precipitate was dissolved with.difficulty from the filter paper in ca. 94 ml. of water and bottled for testing as R-B 55. The filtrate was placed in the cold and allowed to stand for 12% hours. The precipitate was collected on a Buchner funnel using No. 50'lhatman paper and was dissolved (readily) in so ml. of water and bottled as R-B 56 for testing. Results: ‘ Single __ weight change Sample dose Dose Result in . Remarks toxicity" cc. Treated/gcntrols R-B 55 . 1.0 1.0-0.3 - ~535 dil. 1:5 -1,5 R-B 56 5.0 0.25-0.15 t“ -l.0 ’ -105 Discussion: these results indicated that the method described in this procedure was the most successful one carried out in this study in an attempt to separate the active principle from the toxic materials. The fact that the treated.mice lost less weight than did the controls 50 suggested that a study be made to determine whether an increase in the dose level or an increase in the concen- tration of the active principle in the sample tested would result in a corresponding greater inhibition of the growth of the tumors. SUMMARY l. The lability of’an.anti-tumor growth substance from Boletus edulis in acid or alkaline medium was demonstrated. 2. a procedure for the concentration of the active prin- ciple from.water extractives of Boletus edulis samples was tested and modified. 3. A procedure for the separation of the active principle from the toxic factors in water extractives of Boletum edulis was apparently successful. CONCLUSIONS Several attempts have been.made to determine a prac- tical means of concentrating an anti-tumor growth factor from.Boletus edulis. The use of acetone as a precipitating agent for the concentration of the factor from crude extrac- tives is to be preferred for it has been shown not to de- stroy tne tumor-growth.inhlcitory activity at concentrations as high.as 90 per cent. Admittedly, the quantitative separation of the active principle was not realized in the course of this study and.mmst necessarily await further investigation. It is suggested that the procedure to be employed for the separation of the active principle from the toxic materials in the crude extractives be the method as de- scribed under R-B 55 and R-B 56 (page 48). The removal of the initial precipitate immediately after treatment of the extractive with excessive acetone appears to be the critical step in this method and deserves further study. That the active principle when quantitatively iso- lated will be inherently non-toxic to the test animals may not be concluded from this study and further study of de- toxification techniques is suggested. Although.the use of the biological assay method for testing the inhibitory ability of the samples was conven- 55 ient, the results reported here suggest that a study be attempted to determine a method of testing which will give quantitative results without the interference of the toxic effects of the preparations. This test, if developed, should be a chemical test involving an analytical method and must await the isolation and characterization of the active factor. l. 2. 5. 4. 5. 6. '7. 3. 9. BIBLIOGRAPHY Buckley, S. M., C. C. Stock, M. L. Crossley and C. P. Rhoads. Scientific proceedings. Cancer Research, 10:208-209, 1950. Gye, W. E. Problem of cancer: retrospect and prospect. Lancet, 2:1515-1317, 1955. Laszlo, D. Studies on tumor growth inhibitory sub- stances. Approaches 32 2919.3 Chemotherapy, A.A.A.S., pp. 148-156, 1947. Leuchtenberger, C. Results of treatment of spontaneous tumors with "folic acid' and allied substances. Approaches to W Chemotherapy, A.A.a.S., pp. 157- 162, 1947. Lewisohn, R. Review of the work of the laboratory 1937- 1945.. Approaches 333 m ChemOtherapl, A.A.A.S., pp. 159-147, 1947. ‘ Lucas, E. H. Unpublished data. Hatsushita, T. New cancer remedy, carcinolysin. Deut. Med. Wchnschr., 50: 15-14, 1924. Reilly, H. C. and C. C. Stock. Studies on a tumor- retarding agent produced by Aspergillus ftunigatus. Cancer Research, 11:566-569, 1951. Stock, 0. C. Aspects of approaches in experimental cancer chemotherapy. The American Journal of Medicine, I“ ’1 e D H D O O Q ., D e s Q 0 D [I 55 8:658-674, 1950. 10. Sugiura, K. Effect of intravenous injection of yeast and barley extracts and 9.9. page; factor upon spon- taneous mammary adenocarcinoma in mice. Approaches to Tumor Chemotherapy, A.A.A.S., pp. 208-215, 1947. 11. Torrey, J. c. and M. c. Kahn. Treatment of Flexner- Jobling rat carcinomas with bacterial ferments. Jour. Cancer Research, 11:554-576, 1927. JUN 3 "-'.‘ a“ ‘llllMINIHIIIIWHIHHNlllllHlm|||H|H||ll||||||1Hl| 31293 02446 7858