Document 6RyEbpgyJ8qD5m0xXrn3rkz2m

CLINICAL TOXICOLOGY 11(1), pp. 107-118 (1977) N* 10?| NOTICE: THIS MATERIAL MAY BE PROTECTED BY COPYRIGHT LAW (TITLE 17, U. S. CODE) Enhanced Polychlorinated Biphenyl Lesions In Moloney Leukemia Virus-Infected Mice LOREN D. KOLLER, D.V.M., Ph.D.' National Institute of Environmental Health Sciences Research Triangle Park, North Carolina INTRODUCTION Polychlorinated biphenyls (PCB)are potential environmental con taminants that are used In electrical capacitors and transformers, heat transfer systems, plasticizer applications, hydraulic lubricants, and other miscellaneous applications [1). In 1968, the Ingestion of K rice oil contaminated with PCB Kanechlor 400 (48% chlorine) pro duced the disease ''Yusho'' In Japan (2). The disease was character ized by Increased eye discharge, follicular accentuation, acne-form eruption, sweating palms, weakness, and pigmentation of the skin and nails. Polychlorlnatsd biphenyls are hepatotoxlc In mammals [3-5] but produce edema formation In birds [3]. Since PCBs are hepatotoxlc and neoplasia produced by Moloney leukemia virus (MLV) may Involve the liver, the present study was dsvlssd to determine If different formulations of PCB may affect In duction of neoplasia by MLV or If MLV may affect the toxicity of PCB. `Address reprint requests to Dr. Loren D. KoLler, School of Veterinary Medlclne-Oregon State University, Corvallis, Oregon 97331. 107 copyriitri C 1977 by Mticcl Dckbet, IM. Ml Xiyhly Rnmed. Ntithtr thii work nor any pin miy be reproducedortransmitted In any form or by any meant, electronic or mechanical, Including photocopying, microfilming, and recording, or by any Information storage and retrieval lyitem. without peimtmiofi in witting (torn the publisher. MONS 001167 108 ROLLER MATERIALS AND METHODS Balb/c male mice 28 days old were used In the experiment. The anlmala wero divided Into 10 groups. Nine groups of 100 mice each received PCB Aroclor 1221, 1242, or 12S4 (Monsanto Co., St. Louis, Mo.) mixed In the feed (Ralston Purina Lab., St. Louts, Mo.) and 115 controls were given non-PCB-contamlnated feed. The PCB formula tions contained 21, 42, and 54% chlorine. The PCB-exposed groups received either 375, 37.5, or 3.75 ppm of each Aroctor (1221, 1242, or 1254) (Table 1). Twenty-five mice In each of the nine PCB groups were Inoculated tntraperltoneally (IP) at 42 days of age with 0.3 ml of either 1 x 10, 1 x 10` *'*, or 1 x ioc dilution of Moloney leukemia virus (MLV) (NCI, NIH by University Lab. Inc., Highland Park, N.J.), and the remaining 25 were Inoculated IP with sterile physologlc saline (Table 1). Fifty control mice (with out PCB) were each Inoculated IP at 42 days of age with 0.3 ml of 1 x 10, 1 X 10'*`, or l x 10"1 dilution of MLV, and 25 mice received neither PCB nor MLV. The PCBs were fed for six months at which time one-half of the animals In each group were killed. Each mouse was weighed and necropsled. The liver, spleen, and kidneys were weighed and placed In buffered 10% formalin. Feeding of the PCB-contamlnated food was discontinued at six months and mice that had been receiving 37.5 or 3.75 ppm Aroclor 1254, 37 5 ppm Aroclor 1242, and no PCB were fed another three months of PCB-free diet These animals were then killed, weighed, and necropsled. The liver, spleen, and kidneys were weighed and placed In 10% formalin. The mice remaining In the other PCB groups were killed, examined for gross and microscopic lesions, and discarded after the six of months of feeding PCB since lesions had not occurred by that time. Microscopically, hepatic lesions were graded from + to +++. The most prominent lesions of each grade were as follows: + was repre sented by mild centrolubular granular degeneration and necrosis of hepatocytes and a slight variation In cell size; ++ was determined by moderate vacuolar degeneration and necrosis of the centrolobular hepatocytes (Fig. 1) and several hepatocytes were enlarged; +++ changes consisted of severe centrolobular.cytoplasmic vacuolar degeneration and necrosis of hepatocytes that often Involved the entire lobule, marked' variation In cell size, and nucleoli that were often prominent; ++++ lesions were characterized by extensive bile duct proliferation and periportal fibrosis, marked variation In cell size but most all were en larged, necorsts of hepatocytes, and the nucleoli were distinct with marglnation of the chromatin (Fig. 2). Fat droplets occurred In some hepatocytes at all grades of alteration, but there was never an abundant accumulation of fat. The spleen was considered to be altered by Moloney leukemia virus MONS 001160 TABLE 1. Mean Liver Weights (gm) of Mice Given Three Different Aroclore of Polychlorinated Biphenyls for Six Months and Inoculated with Three Dilutions of Moloney Leukemia Virusa Dilution MLV PCB Aroclor ppm No virus 6 mo. 9 mo. l x 10 6 mo. 9 mo. 1 X 10" 6 mo. 9 mo. 1 x 10'1 6 mo. 9 mo. 1254 375 10.0 9.46 8.82 9.10 375b 5.48 6.01 5.79 6.05 37.5 2.57 2.01 2.47 1.96 2.60 1.86 2.55 1.91 3.75 2.11 1.87 2.07 1.57 2.08 1.84 1.96 1.79 1242 375 3.11 1.98 2.B5 2.43 2.79 2. 56 3.27 2.41 37.5 1.97 2.06 1. 98 2.01 3.75 1.98 2.05 1.93 1.74 1221 375 1.62 1.75 1.83 1.99 37.5 2.13 1.9G 1.91 1.84 3.75 1.71 1.92 1.88 1.70 Control None 1.74 1.03 1.79 1.76 1.73 1.80 1.66 1.B2 *Moan liver weights are included for threo exposures of PCB In which PCBs had been removed for three months after the six-month exposure (9 mo.). Analysis of variance revealed the increase m mean liver weights were highly significant (p<k0.01) In each of the Aroclor 1254 groups and in the 375 ppm Aroctor 1242 group at six months. There was a highly significant (p<s0.01) decrease In mean liver weights when the PCB was removed from the diet for three months in the 37.5 ppm Aroclor 1254 groups and in the 375 Aroclor 1242 group. bDted before six months. HONS 001169 no KOLLER FIG. 1. Centrolobuiar necrosis of the Uver that was considered as a + PCB lesion. Notice the vacuolated hepatocytes. FIG. 2. Bile duct proliferation and early fibrosis that was typical of a ++++ PCB lesion. Notice the variation In cell size and the prom inent nucleoli In some of the enlarged nuclei. HONS 001170 POLYCHLORINATED BIPHENYL LESIONS 111 (neoplastic) when there was excessive hematopoesis, enlarged lymph oid nodules, or neoplastic lymphocytes in the red or white pulp. The spleen weights also increased when these alterations were evident. Since the spleen was considered to be the organ of origination of the neoplastic cells (lymphocytes), accumulations of neoplastic lympho cytes in the liver were considered as metastasis. RESULTS Many of the mice that received 375 ppm Aroclor 1254 died during the fifth and sixth month due to PCB toxicity. This dose of PCB was the only one that was toxic during the six-month feeding period. Those that died and were not Inoculated with MLV had severe centrolobular to diffuse cytoplasmic vacuolar degeneration and necrosis of the bep- atocytes. Many hepatic cells were enlarged but there was a marked variation of size throughout. The nucleoli were often prominent with margtnatlon of chromatin In cells that had enlarged nuclei. These histopathologic changes were considered to be +++. Those mice that received 375 ppm Aroclor 1254 and 1 x 10 or 1 x 10' ** MLV that had spleens affected hyjhe virus had Increased liver damage from +++ to ++++ (Table 2). Histologically, there was usually extensive bile duct proltferation and periportal fibrosis of the liver. The hepatocytes varied considerably In size but most were enlarged. Necrosis of the cells was prominent and several contained hyattnized bodies. The nucleoli were distinct in the enlarged nuclei and the chromatin was marglnated. These lesions were characteristic of a ++++ liver response to PCB (Fig, 2). Those livers from mice that did not exhibit splenic change were similar to the nonvirus group and had +++ liver change. Only eight mice survived for six months on the 375 ppm Aroclor 1254 diet. These mice had ++*4 liver lesions and seven had splenic Involvement. Mice given 37.5 ppm Aroclor 1254 without virus had + liver lesions characterized by a mild centrolobular granular degeneration and necro sis of hepatocytes and a slight variation In cell size. Those that were Inoculated with MLV and had splenic involvement had ++ liver lesions (Table 2) represented by a moderate vacuolar degeneration and necro sis of the centrolobular hepatocytes (Fig. 1). Several hepatocytes were enlarged and variation In size was apparent. Liver lesions did not de velop In the 3.75 ppm Aroclor 1254 and nonvirus group, but ++ liver lesions occurred when mice were inoculated with lx 10 virus and ex hibited splenic alterations. Mice that received 375 ppm Aroclor 1242 without MLV had +4 liver lesions while those that were Inoculated with 1 x 10 virus and had splenic Involvement bad +++ liver lesions (Table 2), A similar effect MQNS 001171 TABLE 1 Severity of Hepatic Leelona In Mice Exposed to Three Different Aroclore of Polychlorinated Biphenyls and Inoculated with Three Dosages of Moloney Leukemia Virus* Dilution of MLV PCB Aroclor 1254 1141 1221 Control ppm 37&0 375.0* 37.5 3.75 375.0 37.5 3.75 375.0 37.5 3.75 n*>ne No virus 6 mo. 9 mo. 4444 444 4 - 44 * - 4 - - - 1 x 10 6 mo. 9 mo. 4444 w+c 44 44 444 44 - - 4 4 4 tO 444 - 1 x 10' 0 mo. 9 mo. 4444 4444 4 - 44 - - - 4 - 4 tO 444 - l x ur* 6 mo. 9 mo. 4444 444 4 - 44 - _ - 4 - -- - No hepatic lesions. , mild centrolobular degeneration and necrosis hepatocytes, slight variation In slse hepatocytes. ++, moderate centrolobular degeneration and necrosis hvpalocylos, ncvct.il hepato* cytss enlarged. 444, severe centrolobular degeneration and necrosis hepatocytes, marked variation In cell site, nucleoli prominent +++, bile duct proliferation, periportal fibrosis, marked variation in cell size, necrosis of hepatocytes, distinct nucleoli with marglnatlon of chromatin. bDied before six months. ^Increase In lesion severity for each vtrus*lnoculated group occurred only In those mice that developed splenic lesions due to MLV. HONS 001172 POLYCHLORINATED BIPHENYL LESIONS 113 occurred at 37.5 ppm Aroclor 1242. Liver lesions did not occur unless splenic lesions were evident In the MLV-inoculated mice and then liver lesions developed. At six months, regardless of the virus dose, whenever there was evidence of neoplasia In the spleen by histopathology and Increased spleen weight, the PCB liver lesions were increased In severity by one +. At nine months (three months after discontinuing PCB feed), mice In the 375 ppm Aroclor 1242 group without virus did not manifest liver lesions, but those Inoculated with 1 x 10 MLV had liver changes ranging from + to +++ (Table 2). Seventy-three percent had lesions; the majority (36%) had advanced lesions (+++). However In the 1 x lO"1'* MLV group, 71% had liver lesions ranging from + to +++ but the majority (43%) had only mild lesions (+). Microscopically, alter ations did not occur In the spleens nor wers their weights Increased In the vlrus-lnoculated animals as was observed In the six-month animals. Apparently, the virus enhanced PCB liver change, but did not produce neoplasia In the spleen as It had In other animals. The livers from mice given 37. 5 and 3.75 ppm Aroclor 1254 for six months and then removed from it for three months had lesions similar to those at six months, (Table 2), indicating that liver damage from PCB was not reversible In the three-month period. However, livers from mice given 375 ppm Aroclor 1242 had ++ PCB lesions at six months, but lesions were not present at nine months, Indicating that the liver had regenerated. The mice that lived for six months in the 375 ppm Aroclor 1254 group had the largest livers (Table 1). Those that died early also had livers that were markedly enlarged and that were three times larger than control livers. The liver weights in 37.5 and 3.75 groups decreased in size accordingly but remained larger than the controls. The livers were smaller in the 37.5 and 3.75 ppm groups at nine months than at six months, suggesting that the lesions had regressed. The PCBs did not produce hepatic neoplasia In the six-month feed ing period nor did MLV produce liver pathology other than Infrequent metastasis of neoplastic cells to the liver from the spleen. DISCUSSION Hepatic toxicity produced by PCBs was enhanced by MLV. Hepatic lesions In the mice exposed to PCB for six months were Increased In severity by MLV only when the virus produced evidence of neoplasia In the spleen. Regardless of the virus dose, whenever there was an Increase In weight and histologic alteration of the spleen, the hepatic lesions were more pronounced. When MLV did not affect the spleen, the PCB liver lesions were similar to those of non-virus-inoculated MONS 001173 114 HOLLER mice. Three months alter removal trom the PCB diet, hepatic lesions were attain advanced by MLV. However, the spleens were usually free of histologic evidence o( neoplasia and their weight was comparable with spleens from non-vtrus-tnoculated control mice. Liver weights corresponded with the dose oIPCB given. The htgh-est dose of Aroclor 1254 produced the largest livers, and the livers decreased In size as the dose diminished (Table 1). Only the highest dose of Aroclor 1242 (275 ppm) produced enlarged livers, while the other doses of 1242 and 1221 had no effect on liver weight. Hlstopathology coincided with liver weights since hepatic lesions were apparent only at those doses that resulted In Increased liver weights. Liver weights decreased and returned near the non-PCB-exposed liver weights In those mice that were removed from the PCB feed at six months and were then fed a PCB-free diet for an additional three months. Histologically, the livers had recovered from the toxic hepa titis In the 37$ ppm Aroclor 1242 group (Table 2), but hepatic lesions remained apparent In the 37.5 ppm Aroclor 1254 mice. Perhaps the residues of Aroclor 1254 are detoxified more slowly by the liver than (hose of Aroclors 1242 and 1221. However, since PCBs are stored in fat (61 and Aroclor 1254 appears to be more toxic than Aroclor 1221 and 1242 (5), small quantities of residues may be released continu ously from fat depots, prolonging complete detoxification by the liver. PCBs have promoted the Induction of chemically Induced neoplasms by benzene hexachiorlde In mice (7). In the current study, PCBs did not promote the Induction of neoplasia by MLV. Many environmental contaminants have been reported to be synergistic to Infectious agents (5-13), but only two have been Incriminated to activate an oncogenic virus [14]. Several of those contaminants [15-17], Including PCBs [16, It); are apparently Immunosuppressive. Since oncogenic viruses are often activated In tmmunosuppressed hosts (20, 21], and PCB In creased the pathogenectty of a nononcogenic virus [8], It was antici pated that PCB would activate MLV. This did not occur in our experi ment. Perhaps the Immunosuppression, if it did occur, was not suffi cient to activate the virus. These results conform with a recent study [13] In which methylmercury chloride increased the susceptibility of mice to a nononcogenic (encephatomyocardltls) virus, but not to an oncogenic (RLV) virus. The PCBs, 500 ppm Kanechlor 500 and 300 ppm Aroclor 1254, pro duced neoplastic changes in livers of mice when fed for eight and eleven months, respectively [7, 22]. In the present study, neoplasia did not occur in mice fed 375 ppm PCB Aroclors 1254, 1242, and 1221 for six months. The results of this experiment demonstrated that an oncogenic virus (MLV) enhanced PCB-lnduced hepatic toxicity but conversely, PCBs did not appear to activate MLV. It was also demonstrated that PCBproduced hepatic lesions (noncirrhotic) do regenerate after removal HONS 001174 1 POLYCHLORINATED BIPHENYL LESIONS US of PCB from the dlot To my knowledge, thin is the first report to Indicate that an oncogenic virus enhances toxicity of an environ mental contaminant. SUMMARY The hepatic toxicity produced by polychlorinated biphenyls (PCB) was enhanced In mice that were Inoculated with an oncogenic virus, Moloney leukemia virus (MLV). Whenever there was neoplastic in volvement of the spleen by MLV, the hepatic lesions produced by PCB were more pronounced than In those of non-MLV Inoculated mice. Mice were exposed to PCB Aroclors, 1254, 1242, and 1221 for six months. Aroclors 1254 and 1242 were bepatotoxlc with Aroclor 1254 causing death. Aroclor 1221 did not affect the mice. Liver weights tn mice that were fed PCBs for six months and then maintained on a PCB-free diet for an additional three months were comparable with those of non-PCB exposed mice. These results sug gest that the PCB-produoed hepatic lesions (nonclrrhbtlc) regenerate after removal of PCB from the diet. Polychlorinated biphenyls did not affect (promote or Induce) the oncogenesis of MLV In this study. ACKNOWLEDGMENTS The author thanks Dr. J. A. Moore, Mrs. L. D. Lawson, and Mr. Z. McCoy for valuable assistance and Dr. Roger Peterson for statis tical analysis. REFERENCES [1] L C. T. Nlbet and A. P. Saroflm, Rates and routes of transport of PCB's In the environment. Environ. Health Persp.. 1. 21 (1972). (2] 14. Kuratuse, Y. Yoshlmura, J. Matsuxaka et al.. Epidemiologic study on Yueho, a poisoning caused by Ingestion of rice oil con taminated with a commercial brand of polychlorinated biphenyls, Environ. Health Persp.. 1, lit (1872). IS] A ft Vos, Toxicology of PCB's for mammals and for birds, Environ. Health Persp.. 1, 105 (1972). [4] A D. Kimbrough, ft. E. Under, and T. B Gaines, Morphological changes In livers of rata fed polychlorinated biphenyls, Arch. Environ. Health. 26. 284 (1972). , HONS ooll-75 116 KOLLER [6] L. D. Roller and J. G. Zlnkl, Pathology of polychlorinated bi phenyl* in rabbit*. Am. J. Pathol. 70, 363 (1973). , [6] A. Curley, J. W. Burse, M. E. Grim, et al., Polychlorinated bi phenyls: Distribution and storage In body fluids and tissues of Sherman rats, Environ. Res., 4, 481 (1971). [7] L Nobuyukl, H. Nagasaki, M. Aral, et al., Histopathologic studies on liver lumortgenesls Induced In mice by technical polychlorin ated biphenyls and Its promoting effect on liver tumors Induced by benzene hexachlorlde, J. Natl. Cancer Inst., SI, 1637 (1973). [8] St Friend and D. O. Trainer, Polychlorinated biphenyl: Interac tion with duck hepatitis virus. Science. 170, 1314 (1970). |9) J. H. Gainer and T. W. Pry, Effects of arsenlcals on viral Infec tions In mice, Am. J. Vet. Res., 33. 2299 (1972). [10] J. H. Gainer, Increased mortality In encephalomyocardltls virus Infected mice consuming cobalt sulfate: Tissue concentration of cobalt. Am. J. Vet. Res., 33, 2607 (1972). [11] G. A. Fairchild, J. Roan, and 3. McCarroll, Atmospheric pollu tant* and the pathogenesis of viral respiratory Infection, Arch. Environ. Health. 25, 174 (1972). [12] F. E. Hemphill, AT L. Kaeberle, and W. B. Buck, Lead suppres sion of mouse resistance to Salmonella typhlmurlum. Science, 172, 1031 (1971). [13] TTd. Roller, Methylmercury: Effect on oncogenic and non-onco- tenlc viruses In mice, J. Am. Vet. Med. Assoc.. 36. 1501 (1975). [14] J. H. Gainer, Activation of the ftauscher leukemia virus by metals, J. Natl. Cancer Inst., 51, 609 (1973). [15] L. D. Roller, Immunosuppression produced by lead, cadmium, and mercury, Am. J. Vet. Res., 34, 1457 (1973). [16] M. Wassermann, D. Wassermann, D. Kedar, et al., Immunologic al and detoxication Interaction in p,p-DDT fed rabbits, Bull. En viron. Contam. Tox., 6, 426 (1971). [17] L. G. Roller and S. Rovaclc, Decreased antibody formation In mice exposed to lead, Nature, 250, 146 (1974). [16] L. D. Roller and J. E. ThlgpenTHeductton of antibody to pseudo rabies virus in polychlorinated biphenyl-exposed rabbits, Am. J. Vet. Res.. 34, 1805 (1973). [19] 3. O. Vos and T. D. Rol), Immunosuppressive activity of a poly chlorinated biphenyl preparation on the humoral Immune re sponse in guinea pigs, Toxicol. Appl. Pharmacol., 21, 549 (1972). [20] M. 8. Hlrsch, P. H. Black, and M. R. Proffitt, Immunosuppression and oncogenic virus Infections, Federation Proc., 30, 1852 (1971). [21] W. S. Ceglowskl and H. Friedman. Virus TumorlgeneslB and Im- munogsnesls.- Academic, New York, 19*13, pp. 82-63, 131-133 [22] R. D. Kimbrough and R. E. Linder, Induction of adenoflbrosls and hepatomas of the liver In Balb/dJ mice by polychlorinated biphenyls (Aroclor 1254), J. Natl. Cancer Inst., 53, 547 (1974).