.~ $1.11.? 5;. ‘n it I‘Ou‘ll u .. HM . u—.,. .. .. ._ gy. I . ‘ o "(14:3 {Fir 1.. Ah.bnu- 1m. ‘ar. w.“ »-—-.... .. .... .......:'.. ““ .. “a h “a mm a»... 'é‘u‘JJ‘ A 1511 . ~o . ‘ “on”: , ‘ ....,. 4; >u........ m -.-, .1...“ ~ .4‘ , w...“ .. or“, “Nun"...hu 7.. -~ A { ‘1‘: . 2”; :n:» ‘r ‘4; J I... ! O ‘r'srfiz- 3233% EM ”I t 33!“: 4‘. "4.“ a: 5H t. ‘l“t‘ .l 5 V I : "a,“h'dfid- ’ . a I : v 225 'l v! 95%:ng "if"; , $32?" I x‘llfigfigfiz' 5W5, ’fiili t” n ». . i. . ,. :3; t In :1," .v v :15: x ‘: ~55 a‘ ‘1 '1 )5” t "1 7 if! ‘1 :" 6’9?! u: " m z .. . 3... 3‘ .o ‘- Irr .- 1- g . "D J": o». nu- . i V ‘u' Q 1 I! A i I #3 I.‘ “A 4%?” g, a 1:1 4:5 \ ‘i ! I '3; ,3 ii A 1“ t l. . 5:. mafia . - IQ“ 1*— 1f "2 .‘ 5 H - an” o.- gram—v»: ‘- 4... ‘1'"; - L . 'u a .. bl»... nm-m ....,4 3'3? .2. .7; .a» f":'-4:1£:'.'JL . . ...:L" «n...» wuuv.» ._. ,_,, u. .. , ‘ '33:?“ .1! 4 u , at”... a: :m ‘ x... .v . ‘ - . ”Of- nu \. 3:10 . £3311.“ 313‘ um .y‘Z.‘ .u-m-A ":f'; 12%.;- ’r{i' “M... “3‘ . ”:3: " .11.. V , . . n. I . 95,43 W1: fin»J VI 32: ‘ fir. .igfi . «y; ‘1‘ 34"“ i _‘ .w w: 3... a, La“;;3 . .... : ”-7” 21.72% «VJ-Vi ‘V 4— u- 2.34: . w... . , .. ’;~— 1 i- N a n...-; w. .3? .4 This is to certify that the thesis entitled THE DELAYED NEUROTOXIC EFFECTS OF TRIPHENYL PHOSPHITE (TPP) IN THE JAPANESE QUAIL presented by REJEEV GEORGE VARGHESE has been accepted towards fulfillment of the requirements for M.S. degreein ANIMAL SCIENCE . Major pro essor Date 10/ 'q/q"! 07639 MS U is an Affirmative Action/Equal Opportunity Institution LIBRARY Michigan State Unlverslty PLACE ll RETURN BOXtonmovomb Mouflom ywrrocord. TO AVOID FlNEB mum morbdonddoduo. DATE DUE DATE DUE DATE DUE [II In E: Vii—7 MSU lsAnNflnn‘lwAcflmEqnl Opponunlly lawman THE DELAYED NEUROTOXIC EFFECTS OF TRIPHENYL PHOSPHITE (TPP) IN THE JAPANESE QUAIL BY Rejeev George Varghese A THESIS Submitted to Michigan State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE Department of Animal Science 1994 ABSTRACT THE DELAYED NEUROTOXIC EFFECTS OF TRIPHENYL PHOSPHITE (TPP) IN THE JAPANESE QUAIL BY Rejeev George Varghese Certain organophosphorus chemicals (OPs) cause a condition called organophosphorus-induced delayed neurotoxicity (OPIDN) . Since previous studies indicated Japanese quail were resistant to Type I OPIDN compounds, the purpose of this study was toldetermine the sensitivity of this species to triphenyl phosphite (TPP), a Type II OPIDN compound. Quail were administered single subcutaneous doses of TPP at concentrations up to 500 mg/kg. At 24 hrs after dosing, half of the birds from each dose group were assessed for whole-brain neurotoxic esterase (NTE) activity. The remaining birds were observed daily for up to 20 days for the development of OPIDN clinical signs. Brains from some of these birds were examined for degeneration. All doses of TPP resulted in NTE inhibition which ranged from 11 % to 87 % and clinical signs as soon as 3 days post-dosing. Widespread degeneration in the brain was also noted. ACKNOWLEDGEMENTS I would like to thank my major advisor, Dr. Steve Bursian for the mentoring, valuable thoughts, guidance and friendship. Special thanks also go to the members of my guidance committee, Dr. Duke Tanaka, Dr. Richard Balander and Dr. Robert Poppenga for their valuable help in my graduate program. I am.thankful to Dr. Duke Tanaka for helping me with the research in.neuropathology and.to Dr. Richard Aulerich for his comments on my manuscript. Personal appreciation goes to my uncle, Dr. Sam Varghese; for introducing me into the field of Animal Sciences, for his valuable help, suggestions and advice. Special thanks go to my friend Sally Gaff for helping me with the chemical diagrams and printing. I am very grateful to my family for their support in my career pursuits; whose prayers have been my strong foundation. Above all, I thank the Lord God for His mercy and blessings. I only hope that I can strive to please Him in all that I do and through my academic endeavors. iii TABLE OF CONTENTS LIST OF TABLES . . . . . . . . . . . . . LIST OF FI INTRODUCTI LITERATURE MATERIALS AND METHODS . . . . . . . RESULTS DISCUSSION GIIRE S O O O O O O O O O O O O 0 ON 0 O O O O O O O O O O O O 0 REVIEW . . . . . . . . . Organophosphorus Compounds Two Kinds of OPIDN . . . . History & Incidence . . . . Chemical Structure 8 Reactivity Latent Period . . . . . . . . . Clinical Signs . . . . . . . . Neuropathological Features . . Role & Inhibition of Neurotoxic Age Sensitivity . . . . . . . . Species Selectivity . . . . . . Test Species and Husbandry Treatment . . . . . . . . . Neurotoxic Esterase Assay . Clinical Observations . . . Neuropathological Assessment Statistical Analysis . . . . Animal Use and Care . . . . . Clinical Signs NTE Assay . . . . . . Histopathological Assessment Clinical Signs . . . . . . NTE Assay . . . . . . . . Neuropathological Studies . CONCLUSION . . . . . . . . . . . . . . . LIST OF RE FERENCES O O O O O O O O O O 0 iv ooMoooooooo o o o o o o o o o 0 ff. 0 o o o o o o LIST OF TABLES The effects of TPP and TOTP on the development of clinical signs characteristic of OPIDN in adult.Japanese qua i 1 O O O O O O O O O O O O O O O O O O O O O O O 4 3 The effects of TPP and TOTP on whole-brain neurotoxic esterase (NTE) activity in Japanese quail 24 hours post- administration . . . . . . . . . . . . . . . . . . . 46 The distribution of degeneration in the forebrain of the Japanese quai l perfused at various times after TPP administration 0 O O O O I O O O O O O O O O I O O O 56 LIST OF FIGURES The chemical structures of tri-o-tolyl phosphate (TOTP), o-tolyl saligenin phosphate (TSP) and bis(1-methylethyl) phosphorofluoridate (DFP) . . . . . . . . . . . . . 14 The chemical structure of triphenyl phosphite (TPP), a Type II organophosphorus compound . . . . . . . . . 17 Darkfield photomicrographs of parasagittal sections through the forebrain of the Japanese quail illustrating the dense axonal and terminal degeneration present in the lateral forebrain.bundle (FPL), caudal neostriatum (NC), and ectostriatum (E) 9 days after a single subcutaneous injection of 125 mg TPP/kg body wieght . . . . . . . 49 Photomicrographs illustrating control and TPP-exposed Fink-Heimer silver impregnated sections through the caudal neostriatum and ectostriatum . . . . . . . . 51 TPP-induced degeneration in the Japanese quail brain (sagittal median view) . . . . . . . . . . . . . . . 52 TPP-induced degeneration in the Japanese quail brain (sagittal lateral view) . . . . . . . . . . . . . . 53 TOTP-induced degeneration in the Japanese quail brain (sagittal median view) . . . . . . . . . . . . . . . 54 TPP-induced degeneration in the chicken brain (sagittal median VieW) O O O O O O O O O O O O O O O O O O O O 67 TPP-induced degeneration in the chicken brain (sagittal lateral view) . . . . . . . . . . . . . . . . . . . 68 vi INTRODUCTION Organophosphorus compounds are used extensively in industry and agriculture as pesticides, flame retardants, plasticizers, petroleum additives, and intermediates in the manufacture of pharmaceuticals (Davis and Richardson, 1980; U.S. Environmental Protection Agency, 1985). Exposure to certain of these organophosphorus compounds results in a neurological condition characterized by progressively developing hindlimb ataxia and paralysis, inhibition of the enzyme neurotoxic esterase (NTE) and development of axonal degeneration in both the central (CNS) and peripheral (PNS) nervous systems (Johnson, 1975a,b, 1982; Davis and Richardson, 1980; Abou-Donia, 1981; Baron, 1981; Abou-Donia and Lapadula, 1990; Tanaka et al., 1990a,b, 1991, 1992a). Since 1978, this effect has been termed organophosphorus—induced delayed neurotoxicity or OPIDN (Abou-Donia, 1978). OPIDN's major visible consequence is the motor dysfunction resulting from neuropathic lesions, though there are other significant changes that precede or accompany clinical manifestations. These changes occur at various levels: changes at the molecular level are apparent as neurochemical changes, changes at the cellular level are apparent as neurophysiological changes, changes at the tissue level are apparent as 1 2 neuropathological changes, and changes at the organism level are apparent as functional changes, ie neurobehavioral and neurological alterations. The term "neurotoxic" is a general term to encompass all of these changes and is adequate enough to fully define this effect (Abou-Donia, 1981). The series of poisonings caused by ingestion of tri-o- tolyl phosphate (TOTP) that occurred at intervals during the period from 1930 through the 1970s fully depicts the dangers of human exposure to GP compounds. In most of these cases, poisoning was from the ingestion of beverages or food adulterated with TOTP (Senanayake and Johnson, 1982). The characteristic syndrome was initially called "Ginger Jake paralysis" because of the consumption of illicit alcoholic beverages made from extracts of Jamaican ginger contaminated with TOTP. The victims displayed acute signs of vomiting and diarrhea which were followed by the onset of muscle pain, muscle weakness and parathesias. The chronic cases were characterized by individuals having signs of persistent ataxia and spasticity. Recently OPIDN has been divided into 2 categories designated as Type I and Type II, with each type possessing distinctive clinical and neurophysiological characteristics (Abou-Donia and Lapadula, 1990) . Type I is produced by exposure to organophosphorus compounds such as tri-o-tolyl phosphate or TOTP (also know as tri-ortho—cresyl phosphate or TOCP) , bis (I-methylethyl) phosphorofluoridate (DFP) , mipafox, and leptophos. Features of Type I OPIDN in animals include 3 inhibition of the nervous system enzyme neuropathy target esterase (NTE) in excess of 70 % and the presence of a relatively long delay period of 10 - 21 days before the onset of hindlimb ataxia and paralysis. The accompanying neuropathology is localized in.peripheral nerves, spinal cord and brainstem. Type II OPIDN may be produced by exposure to triphenyl phosphite or tri-ortho-, tri-meta-, or tri-para- cresyl phosphite. In contrast to Type I 0P compounds, delayed neurotoxicity induced by Type II compounds is characterized by NTE inhibition which may be less than 65 - 70 % and by a shortened delay period of 4 - 7 days before the onset of ataxia and hindlimb paralysis. Results of recent work by Tanaka et al. (1990b, 1992a,b) indicate that neuropathology resulting from exposure to Type II compounds involves not only the spinal cord and brainstem, but also the midbrain and forebrain. Type I 0Ps contain a central pentavalent phosphorus atom while Type II 0Ps contain a central trivalent phosphorus atom. To determine the suitability of a species as an OPIDN model, the pattern of degeneration in the central nervous system (CNS) is taken into consideration. The chicken is commonly used as a model to study the pathophysiology of this syndrome (Cavanagh, 1954) . Several studies using Type I (Tanaka and Bursian, 1989; Tanaka et al., 1990a) and Type II (Carrington et a1., 1988a; Konno et a1., 1989; Katoh et a1., 1990; Tanaka et al., 1991) OPIDN compounds have included a histopathological examination of nervous system tissue in the 4 chicken. The Fink-Heimer silver impregnation method has been effective in mapping the total extent of neuropathology following exposure to Type I and Type II OPIDN compounds in the chicken (Tanaka and Bursian, 1989; Tanaka et a1., 1990a,b, 1992a,b). Despite the susceptibility of the chicken to Type I and Type.II OPIDN, other avian species'have not.displayed the same sensitivity. For example, the Japanese quail has been shown to be resistant to the effects of the Type I OPIDN compound TOTP based on the lack of clinical signs (Francis et a1., 1980; Bursian et a1., 1983). The purpose of the present study was to determine if a species which is apparently resistant to Type I OPIDN will also be resistant to Type II OPIDN. Thus, specific objectives of this study were to: 1) determine if the Japanese quail, a species which is not sensitive to Type I OPIDN, is sensitive to the Type II OPIDN compound triphenyl phosphite (TPP) based on the development of clinical signs, whole-brain NTE inhibition and the presence of characteristic neuropathological lesions, and 2) if the Japanese quail was shown to be sensitive to TPP, to compare the characteristics of clinical signs, NTE inhibition and neuropathological lesions in the Japanese quail with those same parameters in the chicken. LITERATURE REVIE' 1. ORGANOPNOSPEORUS COMPOUNDS Organophosphorus (0P) chemicals are used in agriculture as pesticides to kill undesired insects, worms, weeds and fungi, and in industry as plasticizers, antioxidants, stabilizers, plastic extenders, and oil and gasoline additives (Eto, 1979; Davis and Richardson, 1980; US Environmental Protection Agency, 1985; Cherniak, 1988). Cresyl phosphates and other related phosphates also impart flame resistance to fabrics (Fisher and Van‘Wazer, 1961). While 0P compounds have been very beneficial in terms of increased food production and protection of human health (Ecobichon, 1991), they also have adverse effects on both the peripheral and central nervous systems. The most extensively studied 0P effect is the acute inhibition of acetylcholinesterase (AChE), the enzyme which hydrolyses the neurotransmitter acetylcholine (ACh). ACh is released from nerve terminals of postganglionic parasympathetic nerve fibers, somatic motor nerves innervating skeletal muscles, preganglionic fibers of the autonomic nervous system and some neurons in the central nervous system (Murphy, 1975) . The OP molecule mimics ACh and phosphorylation of the serine-hydroxyl group at the catalytic center of the enzyme occurs. The potency of the 0P compound depends on the degree of enzyme phosphorylation. Inhibition 5 6 of AChE causes ACh to accumulate at the synapses and neuromuscular junctions causing excessive stimulation of muscarinic, nicotinic and CNS receptors. Effects of excessive stimulation of muscarinic receptors, which are present on smooth muscles, heart, and exocrine gland, are bronchoconstriction, increased salivation and lacrimation, vomiting, diarrhea and bradychardia. Effects of excessive stimulation of nicotinic receptors, located on skeletal muscles and autonomic ganglia, include fatigue, dyspnea, pallor, increased blood pressure, hyperglycemia and tachycardia. Accumulation of ACh at CNS receptors cause restlessness, anxiety, headaches, confusion and tension (Murphy, 1975; Barrett and Oehme, 1985). 0P-induced.death may occur 5 minutes to 24 hours post-exposure, depending on the chemical and the dose (Abou-Donia and Lapadula, 1990). In addition to its presence in the nervous system, AChE is also found in red blood cells. Assessment of AChE activity in red blood cells is commonly used as an indication of exposure to and absorption of GP compounds. In addition to acute inhibition of AChE, some 0? compounds have delayed neurotoxic properties (Abou-Donia, 1981) . Organophosphorus-induced delayed neurotoxicity involves permanent locomotor ataxia and subsequent paralysis that is apparent 10 - 21 days after exposure (Johnson, 1975a). In addition to the characteristic delay period and reproducible clinical signs, the delayed neurotoxic 0P compounds also inhibit the nervous system enzyme neurotoxic esterase (Johnson, 1982), and induce characteristic neuropathologic lesions in the peripheral and central nervous systems (Cavanagh, 1954; Tanaka.et.a1., 1990a,b, 1991, 1992a). Some animal species are resistant to the effects of typical OPIDN compounds as are the young of sensitive species. An adequate explanation for this apparent lack of sensitivity has yet to be offered. TWO KINDS OF OPIDN Soon after tri-o-tolyl phosphate was determined to be the cause of OPIDN in humans during the "Ginger Jake paralysis” incident in 1930, it ‘was apparent ‘that. organophosphorus compounds produced 2 distinct types of delayed neurotoxic actions (Lillie and Smith, 1932; Smith et a1., 1933; Aird et a1., 1940). However, only recently have these effects been defined through various studies (Veronesi et a1., 1986a,b; Veronesi and.Bvergsten, 1987; Padilla.et.al., 1987; Carrington and Abou-Donia, 1988a,b; Carrington et a1., 1988a; Abou-Donia and Brown, 1990). The OPIDN compounds can be assigned to 2 classes (Type I and Type II) based on the following criteria (Abou-Donia and Lapadula, 1990): - Chemical structure - Length of latent period between exposure and appearance of clinical signs and neuropathologic lesions - Morphology and distribution of neuropathologic lesions - Inhibition of NTE - Age sensitivity - Species specificity HISTORY E INCIDENCE - Type I OPIDN Before the 19303, cases of delayed neuropathy occurred occasionally in tubercular patients being treated with phosphocreosote, a mixture of esters derived from phosphoric acid and coal tar phenols (Davis and Richardson, 1980) . However, the medicant was not realized to be neurotoxic until a massive outbreak of poisoning in the United States occurred in 1930 when approximately 20,000 people were affected. This condition, marked by permanent ataxia and paralysis of the legs and commonly referred to as "Ginger Jake paralysis", was caused by a mixture of cresyl phosphates used to extract ginger for the purpose of flavoring distilled liquors (Smith et a1., 1930a,b, 1932; Smith and Lillie, 1931; Kidd and Langworthy, 1933). The symptoms of "Ginger Jake paralysis" started as a slowly developing paralysis in the legs followed by tremorsw Even after 6 years, studies conducted on many of these patients showed little recovery with muscle weakness being replaced by spasticity, hyperflexia and abnormal reflexes (Aring, 1942). The historical and epidemiological aspects of this "Ginger Jake" delayed neuropathy have been reviewed extensively (Cavanagh, 1973; Johnson, 1975a,b; Hess et a1., 1978). Similar cases were reported in European publications shortly after the US outbreak (Barrett and.0ehme, 1985). This delayed paralysis, which was found only in women, was linked to "Apiol", an abortifacient containing between 28 and 35 % TOTP. During the next 30 years, studies showed that TOTP was the causative agent in a number of paralytic incidents (Cavanagh, 1964a) . Fifty eight cases of delayed neurotoxicity occurred in Durban, South.Africa in 1938 after cooking oil was contaminated with TOTP. Another incident involved 11 people who were affected after drinking water from drums which were used to store cresyl phosphates (Susser and Stein, 1957). In 1942, three employees involved in the manufacture of TOTP lubricants in Great Britain developed "polyneuritis" after exposure by inhalation during black-out conditions (Hunter et a1., 1944). Susser and Stein (1957) quoted Walthard's (1947) description of the syndrome in 80 men of the Swiss army who also had been poisoned with TOTP-contaminated cooking oil. Since the early studies showed that only the ortho isomer among the symmetrical cresyl phosphates produced a toxic effect (Smith et a1., 1930a,b, 1932), it became customary for mixed esters to be prepared from coal-tar stock containing less than a specified low'amount of ortho-cresol. In spite of this precaution, further outbreaks of poisoning occurred from time to time. In 1953, three workers who were engaged in the laboratory production of a prospective organophosphate pesticide (mipafox or 1L. N'-di isopropyl 10 phosphordiamidofluoridate) were reported to have developed clinical signs typical of OPIDN (Bidstrup et a1., 1953). Laboratory studies concluded that there was no essential difference between mipafox—induced neurotoxicity and neurotoxicity caused by some other alkyl phosphoryl esters and by the triaryl phosphates such as TOTP (Barnes and Denz, 1953). It was determined that a major outbreak of OPIDN in Morocco in 1959 was due to TOTP-contaminated lubricating oil deliberately used to dilute olive oil which was later sold as cooking oil (Smith and Spalding, 1959; Cavanagh, 1964a; Metcalf, 1982) . As a result, over 10,000 people were affected with ataxia and paralysis in this outbreak. Dogs also displayed characteristic signs of OPIDN after ingesting the same contaminated substance (Smith and Spalding, 1959) . Other examples of TOTP-contaminated food products which resulted in human cases of OPIDN include cooking oil in India (Vora et a1., 1962; Anon., 1988), flour in the Fiji Islands (Sorokin, 1969), alcohol in Rumania (Vasilescu and Florescu, 1980) and Morocco (Abou-Donia and Lapadula, 1990) , and sesame oil in Sri Lanka (Senanayake, 1981). Unintentional and intentional exposure to GP insecticides like EPN, omethoate, leptophos, lenthion, trichloronate, tr ichlorphon , phytosol , tamaron , methamidophos and chlorpyriphos have resulted in clinical signs characteristic of OPIDN (Bidstrup et a1., 1953; Fukuhara et a1., 1977; Hierons and Johnson, 1978; Xintaras et a1 . , 1978; Jedrzejowska 11 et a1., 1980; De Jager et a1., 1981; Senanayake and Johnson, 1982; Vasilescu et a1., 1984; Metcalf et a1., 1985; Lotti and Morretto, 1986; Abou-Donia and Lapadula, 1990). In addition to human cases of OPIDN, an incident in Egypt resulted in over 1300 water buffaloes developing OPIDN from exposure to leptophos (Abou-Donia et a1., 1974). HISTORY & Increases - Type II OPIDN As early as 1930, it was apparent that there were 2 types of OPIDN. Smith and colleagues (Smith et a1., 1930a) were the first to study the effects of triphenyl phosphite (TPP), the prototype Type II OPIDN compound, in various animal species. Since the Type II compounds had not resulted in human cases of OPIDN, interest in Type II OPIDN faded. It wasn't until the 19808 that the delayed neurotoxicity effects of TPP were again examined in chickens (Carrington et a1., 1988a,b; Konno et a1., 1989; Tanaka et a1., 1992a,b) and in rats (Veronesi et a1. , 1986a; Padilla et a1. , 1987; Veronesi and Dvergsten, 1987). Ironically, TPP has evaded scrutiny, unlike TOTP, and is still being used in industry and agriculture as a rubber and plastic stabilizer, a diluent of epoxy resins, a metal scavenger, an anti-fungal foliar agent and as an insecticidal synergist though it is known to be an OPIDN-causing compound (0.8. Environmental Protection Agency, 1985). 12 CHEMICAL STRUCTURE 8 REACTIVITY - TYPO I OPIDN Type I OPIDN compounds have a pentavalent phosphorus atom and are derivatives of 'phosphoric, phosphonic, and phosphoramidic acids and.phosphofluoridates. The pentavalent phosphorus atom has a tetrahedral configuration. Type I OPIDN compounds also include sulfur analogs. TOTP and DFP are examples of Type I compounds (Figure 1) (Stuart and Oehme, 1982). The presence of the ortho-methyl group in the aromatic series may be responsible for the neurotoxic property of these types of GP chemicals (Casida et a1., 1961; Nomeir and Abou- Donia, 1984, 1986) . TOTP has to be metabolized to tolyl saligenin phosphate (TSP) (Figure I) to be neuroactive (Eto et a1., 1962, 1967; Bleiberg and Johnson, 1965; Johnson, 1975b; Davis and Richardson, 1980; Abou—Donia, 1984) , while DFP doesn't have to be metabolized to cause OPIDN (Barrett and Oehme, 1985). The chemical reactivity of the Type I OPIDN compounds depends on the phosphorus atom; on its ability to phosphorylate and on its electrophilic character (0.8. Environmental Protection Agency, 1985). CHEMICAL STRUCTURE E REACTIVITY - TYPO II OPIDN Type II OPIDN compounds have a trivalent phosphorus atom and are phosphorus acid derivatives (ie. triphosphites and presumably their sulfur analogs). Triphenyl phosphite is an 13 Figure 1. The chemical structures of tmi-o-tolyl phosphate (TOTP), o-tolyl saligenin phosphate (TSP), and bis (l-methylethyl) phosphorofluoridate (DFP). These chemicals are Type I OPIDN compounds. TSP is the neurotoxic metabolite of TOTP. Ca oils, cna‘ Trl-o-tolyl phosphate (TOTP) C 3 " 0—P-‘O / \ 0 CH2 o-tolyl saligenin phosphate (TSP ) CIH3 P——— F CH3—- CIH— 0/ CH3 Bis(1 -methylethyl) phosphorofluoridate ( DFP ) 15 example of a Type II compound (Figure 2). The trivalent phosphorus atom.has a pyramidal configuration (Abou-Donia and Lapadula, 1990). Neurotoxicity of Type II OPIDN compounds does not depend on metabolism which in turn means that any aryl phosphite can cause Type II OPIDN; The trivalent phosphorus atom has a pair of electrons which binds with other atoms, making it very reactive regardless of other substituents (U.S. Environmental Protection Agency, 1985). LATENT PERIOD Both Type I and Type II OPIDN are characterized by a delay in the onset of clinical signs. However, the period between the time of exposure to the OP compound and the time of onset of clinical signs varies between Type I and Type II compounds in that the latent period is shorter for Type II compounds. It takes only 4 - 6 days for the onset for clinical signs in hens after TPP administration (Carrington and Abou-Donia, 1988a; Carringtoniet a1., 1988a; Katoh.et a1., 1990; Tanaka et al., 1992a,b) compared.to»6 - 14 days for TOTP (Abou-Donia, 1981). Ferrets injected with.DFP started showing signs around day 14 post-dosing (Tanaka et a1., 1991) and ferrets dosed with TOTP started showing signs by day 50 post- dosing (Stumpf et a1., 1989). In contrast, ferrets injected with TPP started showing signs of ataxia by day 4 post-dosing and severe paralysis by day 8 post-dosing (Tanaka et a1., 16 Figure 2. The chemical structure of triphenyl phosphite (TPP), a Type II organophosphorus compound. 18 1990b). CLINICAL srsns - Type I OPIDN The clinical signs of organophosphorus-induced delayed neurotoxicity are similar in all susceptible species. Smith and associates (1930a) were the first to report on OPIDN clinical signs in various species of animals. These initial reports were followed by detailed descriptions of clinical signs in humans by Smith and Spalding (1959). A single injection or oral dose of an OPIDN compound is sufficient to initiate the irreversible clinical response (Abou-Donia and Graham, 1979). Low-level dietary administration (Kinebuchi et a1. , 1977; Abou-Donia and Graham, 1978a,b; Hussain and Oloffa, 1979) and dermal administration (Abou-Donia and Graham, 1978a,b; Hess et a1., 1978) of TOTP have also been shown to induce delayed.neurotoxicity4 Some of the early studies by Smith and colleagues (Smith et a1., 1930a,b; Smith.and.Lillie, 1931; Smith.et a1., 1932) indicated that small, individually ineffective doses of TOTP ingested over a period of time can give rise to ataxia and severe paralysis, if the total dose ingested approached the minimum acute dose for paralysis. Smith et al. (1930b) reported that 40 mg TOTP/kg body weight was sufficient to produce OPIDN in humans. Hopkins (1975) reported calculations by Staehelin (1941) that suggested as little as 2 mg TOTP/kg body weight (made from feedstock low in ortho cresol) may cause a 19 neurotoxic response in man. Ingestion of TOTP by humans may cause some immediate gastrointestinal distress with nausea, vomiting, and.diarrhea which may last a few hours to a few days. A latent period of 8 - 18 days generally follows, depending on the size of the dose and length of exposure. This is followed by a sharp, cramp-like pain in the calves and numbness and tingling inche feet and the hands of the patients. This in turn is followed by increasing weakness of the lower limbs. 'The patient cannot keep his balance and bilateral footdrop has been reported. Depending on the severity, there may be weakness at the knee or hip. Ankle jerks are absent. Knee reflexes may be normal or occasionally depressed. The patient may experience weakness in the hands a week or two after the onset of paralysis in the lower limbs. Wrist-drop and weakness up to the elbow“may also be seen in some individuals. IMany patients exhibit sensory loss, conforming roughly to the degree of motor loss. Sensory loss in the upper limbs usually appears a few days after it develops in the lower limbs (Susser and Stein, 1957). The results reported by Smith and co-workers (1930a) on the response of hens to TOTP and other neurotoxic OP esters were remarkably similar to OPIDN clinical signs reported for humans. Birds treated with TOTP appear normal for a period of 10 - 14 days following acute administration. After this period, they spend more time in a sitting position. When exercising, birds begin to display a clumsiness of gait, 20 accompanied by overt weakness, which is a characteristic sign of ataxia. At 15 - 20 days post-treatment, the birds may become severely paralyzed in the legs and the wings are obviously weakened (Bursian et a1., 1983; Calabrese and Bursian, 1984; Tanaka and Bursian, 1989). At low neurotoxic doses, the birds experience a slight initial weight loss which later is reversed. The birds are able to maintain their health, although the proper use of affected limbs may not be fully regained. In contrast, at. higher acute doses, a 'more severe terminal clinical neurotoxicity is observed. The animal loses its ability (or desire) to eat and subsequently dies following a severe‘weight loss and.complete paralysis of the legs (Smith and Elvove, 1930; Smith.et al., 1930a, 1932; Smith and Lillie, 1931; Lillie and Smith, 1932). In ferrets treated with DFP, the clinical signs at 21 and 28 days post-treatment ranged from slight hind limb weakness to severe ataxia or hindlimb paralysis (Tanaka et a1., 1991). Ferrets exposed to TOTP dermally had diarrhea which was the only sign of acute toxicity (Stumpf et a1., 1989). The motor defect was confined to the hind limbs. Occasionally, the treated animals exhibited hopping movements rather than normal movement and occasionally animals would fall side to side. Ferrets treated.orally’with 1000 mg TOTP/kg body’weight showed detectable clinical signs of ataxia and high-stepping gait by day 11 post-dosing. 21 cnznxcnr arena - Type II OPIDN Clinical manifestations of Type II OPIDN have been studied in various species (Smith et a1., 1933; Roberts et a1. , 1982; Veronesi et al., 1986a; Tanaka et a1., 1990b, 1992a,b) . TPP administration causes ataxia in chickens, rats, cats and ferrets. The pattern of clinical signs produced by TPP are very similar to that produced by neurotoxic phosphoric acid esters like TOTP and DFP (Abou-Donia, 1981). However, ataxia and paralysis tend to develop sooner relative to animals treated with Type I OPIDN compounds (Carrington et a1., 1988a; Katoh et a1., 1990). Early signs of neurotoxicity can be observed before 7 days post-dosing. TPP Houmumq 90> unflaoq mundasooz Hmmuoo DEA msmaosz unannflumm> mswpcoummo 90> mamaosz mummcdulmaflomuo muommaoo whom msoHOdz owamawne .msmaoaz Hmucofimoa mcflucomloadossomm 0mm. MOHumumom mamaomfiuoucfluomuoa momaooz Hmcwmmmumsm mm msmaosz Hm0w>uoo Honouoq mamaooz maausom Houmumq am whammfisaou Mosumusd msoaosz hum>wao HowuoucH Ho asaamnoumu aduowuumomz Hopsoo Oz mwumaooflucoq mmnd A30w> spasms kuuwmmmv Gamma Hanan ommsmmmn on» Ca cowumuosoomp poonpcflnmma .m shaman 00 ma AU 40 m0 .Hd 53 asunwuumooamm m aduowHUmooz Hoodoo oz mwaouuoo whom .mdoaoaz owamnmoosommz Hmumumq GAS fiduowuumouom m Asmfi> Hummuma Hmuufimmmv :Houn meav uncommon map as coaumumcmmmo pmusocwlmma “Hutu-00o ”.m............u .o mudmflm 54 090Hosz Hmadnwum0> H0u0u0A 90>. msHBMA mHMHHdo0S Hmmuoo can 090H052 Hmaonwum0> msfion0om0a 00> 050Hooz 0u00cdon0awumuo ouommaou whom mfi0aooz owfimamca £50,392 Houn0fim08 0swusomloafiocso0m 09H. Howu0umom 0u0flo0fiu0psfllomuoo ma0Hosz Hmsflmmmumdm mm m§0aooz Hmoa>u0u H0H0unq md0aosz 0swucom H0H0umq Am mudmmwaaoo H0flu0uc4 090Hosz mu0>wao Howu0usH Ho . fidaa0n0h0o adumwuumo0z Housmo Oz mannasuwus0q owns A30fl> smao0fi downwmmmv manna Hands 000cmm0h 0gp cw coau0u0s0m0o p0osocwlmaoe .b 0Hsmfim 00 m0 AU 3 m0 Ad 55 nucleus. The cerebellum showed degenerating spinocerebellar fibers. The deep nuclei in the cerebellum had light to moderate degeneration. The granule cell layers of foliae I - VI had heavy mossy fiber degeneration whereas lighter fiber degeneration was noted in the underlying white matter of foliae VII - IX. Moderate to heavy degeneration was noted in several nuclei of the midbrain and forebrain. Degenerating fibers extended from the paleostriatum primitivum to the lateral forebrain bundle and ansa lenticularis. A group of fibers terminated at the dorso-intermediate posterior thalamic nucleus and pedunculopontine tegmental nucleus. Some fibers extended from the lateral spiriform nucleus into the deeper layers of the optic tectum. Brain Auditory System : The 3 principal auditory nuclei in the quail brain which showed degeneration were the lateral mesencephalic nucleus, pars dorsalis, the thalamic nucleus ovoidalis, and the neostriatum caudalis (Table 3 and Figure 6). Seven of the 14 quail examined had degeneration in all of the above 3 areas while 7 Ibirds had. degeneration in 'the thalamic. nucleus ovoidalis and neostriatum caudalis. Degenerating fibers originated from.the nucleus ovoidalis, and passed through the lateral forebrain bundle and dorsally and caudally into the neostriatum caudalis (Figure 3a). The nucleus ovoidalis 56 TABLE 3. The distribution of degeneration in the forebrain of the Japanese quail perfused at various times after TPP administration. (Auditory) (visual) To! Day noso“ MLD 0v no NR ES BSC Post-dosing‘ 556 7 62.5 + + ++ 0 0 O 557 8 62.5 0 + ++ 0 O 0 566 9 125 0 + + 0 0 + 567 9 125 ++ ++ +++ ++ +++ +++ 568 9 125 0 + + 0 O O 570 9 125 + ++ +++ + +++ 0 571 7 250 +++ +++ +++ +++ +++ ++ 572 7 250 + +++ +++ ++ ++ ++ 573 7 250 +++ +++ +++ ++ +++ ++ 575 7 250 0 ++ ++ O 0 ++ 513 3 500 O +++ ++ ++ + 0 547 3 500 0 +++ ++ ++ - ++ 548 3 500 ++ +++ ++ + + O 586 3 500 0 +++ ++ +++ 0 ++ The day post-dosing that the bird was perfused. ** Doses are expressed as mg TPP/kg body weight. + Light degeneration ++ Moderate degeneration +++ Heavy degeneration BSC Brachium of superior colliculus ES Ectostriatum MLD Lateral mesencephalic nucleus, pars dorsalis NC Caudal neostriatum NR Nucleus rotundus OV nucleus ovoidalis 57 contained degenerating cell bodies in the form of black- impregnated cell somata in addition to degenerating axons and terminals. The degeneration in the neostriatum caudalis consisted of degenerating fibers primarily, and in some cases, degenerating cell somata. In a few cases, degeneration was noted in the deeper parts of the lateral mesencephalic nucleus. In one case, axonal degeneration was also noted in the nucleus angularis, a nucleus equivalent to the mammalian cochlear nucleus. Brain Visual System : Eleven of the 14 quail examined had degeneration in 3 principal nuclei of the visual system, namely, the ectostriatum, the nucleus rotundus, and. the brachium. of superior colliculus (Table 3 and Figure 6). Degeneration was noted in all the 3 areas in 4 birds while 5 birds had degeneration in only 2 areas. The brachium of superior colliculus was the sole site of degeneration in 1 bird. The majority of cases studied showed the nucleus rotundus with moderate to heavy degeneration. In a few cases, black silver impregnated cell bodies indicating somatic degeneration were also present. Degeneration in the ectostriatum, though inconsistent, encompassed the major portion of the nuclear region (Figures 3b and 6) . The brachium of the superior colliculus also showed fiber degeneration which was particularly evident in the portion of the brachium 58 encompassing the pretectal nucleus before terminating in the nucleus rotundus. A few degenerating fibers were also noted within the pretectal nucleus. The optic tectum did not contain any axonal or somatic degeneration. DISCUSSION The data obtained from this study indicate that the Japanese quail, which.has been reported.to be resistant to the effects of the Type I OPIDN compound TOTP (Francis et a1., 1980; Bursian et a1., 1983), is susceptible to the Type II delayed neurotoxicant TPP. This was apparent in terms of clinical signs characteristic of OPIDN, whole-brain NTE inhibition, and central nervous system degeneration. CLINICAL SIGNS Observation of clinical signs started from day 1 post- treatment as signs were evident immediately at the higher doses (Table 1). There was a positive relationship between the TPP dose and the severity of the clinical signs exhibited by the Japanese quail. Birds dosed with 62.5 mg TPP/kg body weight showed only mild ataxia. Four of the birds were able to stand upright. The birds in the 125 mg TPP/kg body weight group were more ataxic. This was evident by the fact that these birds moved primarily on their books. In the 250 mg TPP/kg body weight dose group, the birds displayed an inability to maintain balance. The 500 mg TPP/kg body weight dose group birds showed signs similar to those in the 250 dose group, but clinical signs in the former group were evident earlier. There was also a positive relationship between the TPP 59 60 dose and the time of onset of clinical signs in that clinical signs were evident earlier as the dose increased. The onset of clinical signs occurred at day 3 post-dosing for the 62.5 and 125 TPP birds and as early as day 1 post-dosing for the 250 and 500 TPP birds. The birds in 500 TPP group were unable to stand on day 1. There was also a positive relationship between TPP dose and the number of birds affected. The percentage of birds affected was 40 % in the 62.5 TPP group, 60 % in the 125 TPP group and 100 % in the 250 and 500 TPP groups. Day 1 through day 9 seems to be the time period in which Japanese quail show clinical signs as no bird started to show signs after that period. This suggests that if an individual quail is susceptible to TPP, it will show signs prior to day 10. Previous studies reported that the Japanese quail is not sensitive to Type I OPIDN compounds like TOTP (Stuart and Oehme, 1982; Francis et a1., 1980; Bursian et a1., 1983) based on the absence of clinical signs after doses as high as 1000 mg TOTP/kg body weight. In this study, none of the 5 birds dosed with 500 mg TOTP/kg body weight showed clinical signs typical of OPIDN during the 21 day period. Earlier studies have suggested that differences in absorption, metabolism, and elimination of the neurotoxicant may play an important role in species sensitivity to neurotoxic agents (Smith et a1., 1932; Holmstead et a1., 1973; Whitacre et a1., 1976; Abou-Donia, 1976; Baron, 1981; Chadwick et a1., 1982; Abou-Donia, 1983; 61 Abou-Donia and Nomeir, 1986). Abou-Donia and Nomeir (1986) concluded that the rates of clearance of the delayed neurotoxicants EPN and leptophos in insensitive species were faster than in sensitive species. Lasker et a1. (1982) studied the in vitro metabolism of the Type I OPIDN compound EPN and its oxygen-analog EPNO by rat and chicken microsomal enzymes. The formation of EPNO (active metabolite) and PNP (p-nitrophenol) (inactive metabolite) from EPN metabolism was 4.6 and 19.4 times higher in the rat than in the chicken, respectively. In another study with EPN, Abou-Donia et al. (1983a,b) concluded that the neurotoxicant remained in neural tissues for a longer time in sensitive species allowing continuous transfer of the compound and its metabolite to the site of action. A possible explanation of why the Japanese quail is resistant to TOTP is that this species may have a faster rate of clearance of TOTP and/or a greater repair capability in the insulted physiological system compared to sensitive species. Assessment of clinical signs also indicates that the Japanese quail respond with a shorter delay than the usual avian model, the domestic hen. In the present study, Japanese quail in the 2 higher dose groups displayed OPIDN clinical signs within 24 hours of dosing whereas birds in the lower 2 dose groups showed clinical signs by day 3. Previous studies have shown that chickens dosed with TPP first started showing signs between day 5 and day 14 post-dosing (Konno et a1., 1989; Katoh et a1., 1990; Tanaka et a1., 1992). Mammalian 62 models are similar to the hen in regard to the latent period. Rats treated with 1184 mg TPP/kg body weight developed hindleg ataxia within a week followed by paralysis (Veronesi et a1., 1986a;‘Veronesi and.Dvergsten, 1987). Ferrets.dosed with 500, 1000 and 2000 mg TPP/kg body weight show clinical signs of ataxia as early as day 4 and paralysis by day 8 (Tanaka et 61., 1990). Not only is the delay period shorter in Japanese quail, but the transition from mild ataxia to severe paralysis occurs more rapidly in Japanese quail than in chickens. Quail treated with 250 and 500 mg TPP/kg body weight deteriorated within 2 days after initial signs were observed. Hens treated with 1000 mg TPP/kg body weight took 7 days to deteriorate after the onset of clinical signs (Konno et a1., 1989; Tanaka et 81., 1992). The types of clinical signs noted in the Japanese quail are different from those noted in the hen. Once affected by OPIDN, the hen can stand for a longer period of time whereas the quail tend to sit. Mortality in the hen is usually noted much later than in Japanese quail, if at all. Three hens dosed with 140 mg TPP/kg body weight died at days 16 - 22 post-dosing (Konno et a1. , 1989) , whereas in this study, Japanese quail died as early as day 6 and 7 post-dosing and some probably would have died sooner than day 6 or 7 post- dosing if they weren't taken for neuropathological assessment. Comparison of TPP-induced neuropathological damage in avian species have shown differences in the location of lesions in 63 the brains of chickens and Japanese quail. The present study has indicated lesions in the neostriatum of the Japanese quail forebrain. Salzen and Parker (1975) have suggested that damage to the neostriatum causes impairment of fine movements such as are involved in feeding and visual discrimination. Thus, TPP-exposed Japanese quail may have trouble locating feed and eating. Since the metabolism of the Japanese quail is relatively high, it is possible that any impairment that affects the bird's ability to eat is going to be more detrimental to the quail than to the chicken. Thus, neostriatal damage in the Japanese quail may be contributing to its early mortality when compared to the chicken. Another possible explanation may be that the higher metabolic rate of the Japanese quail might somehow enhance the rapid distribution of the toxicant to the nervous system. The development of TPP-induced OPIDN in the Japanese quail occurs at much lower doses when compared to other species. A study by Konno et a1. (1989) showed that leg paralysis could not be produced in adult chickens by a single dose of 100 or 500 mg TPP/kg body weight which agreed with earlier study by Smith et a1. (1933). Ferrets were administered 500 mg TPP/kg body weight in order to produce clinical signs (Tanaka et a1., 1990). Rats showed clinical signs after a dose of 1184 mg TPP/kg body weight (Veronesi et a1., 1986a; Veronesi and Dvergsten, 1987) . However, in Japanese quail, a single dose of 62.5 mg TPP/kg body weight caused mild ataxia in 2 of the 5 birds. 64 NTE ASSAY TPP’ doses as low' as 125 mg/kg‘ body' weight caused significant inhibition of whole-brain NTE activity in the Japanese quail (Table 2). These results agree with previous studies done in the hen and rat (Veronesi et a1., 1986a; Padilla et a1., 1987; Tanaka et a1., 1992; Knoth-Anderson and Abou-Donia, 1993) in that TPP inhibits whole-brain NTE activity. However, the threshold NTE inhibition required to cause clinical signs may vary among species. The percent inhibition of NTE is related to the dose of TPP administered in that higher doses result in greater inhibition. The percent inhibition is also related to the severity of clinical signs noted. An 11 % NTE inhibition by 62.5 mg TPP/kg body weight resulted in mild ataxia whereas an 87 % NTE inhibition by 500 mg TPP/kg body weight was related to severe paralysis which developed very quickly after dosing. For Type I compounds, it is generally assumed that NTE must be inhibited by at least 70 % for clinical signs and neuropathy to develop. In this study, OPIDN developed when NTE inhibition was only 11 %. Similar effects in rats have been reported in that TPP caused NTE inhibition of approximately 40 %, yet clinical signs and neuropathy developed (Veronesi et al., 1986a; Padilla et a1., 1987). Conversely, TOTP caused threshold inhibition of NTE in Japanese quail yet did not cause OPIDN. The latter agrees with a previous study by Bursian et a1. (1983). In that 65 study, Japanese quail were administered TOTP at doses of 125, 250, 500 and 1000 mg/kg body weight, doses sufficient.totcause threshold inhibition of whole-brain NTE, yet clinical signs did not develop. The reason why TOTP causes significant NTE inhibition yet doesn't cause clinical signs is unknown. Johnson (1976) stated that the NTE assay can be used as a tool to determine the neurotoxic potential of OPIDN compounds in that there is a relationship between NTE inhibition in excess of 70 % and the development of clinical signs. The present study indicates that these rules do not apply to Japanese quail. NEUROPATHOLOGICAL STUDIES TPP doses as low as 62.5 mg/kg body weight caused histopathological changes in the CNS of Japanese quail. The fact that.TPP induces CNS damage in.quail agrees with.previous studies on the effects of TPP on the CNS of chickens, rats, and ferrets (Veronesi et al., 1986a; Padilla et a1., 1987; Veronesi and Dvergsten, 1987; Carrington et a1., 1988; Tanaka et a1. , 1990, 1992) , although the minimum dose needed to cause degeneration varied among species. The present study shows that the Japanese quail is very sensitive to TPP which is indicated by the presence of widespread lesions in the cerebellum, medulla, midbrain and forebrain (Figures 5 and 6) . The spinocerebellar tract, spinal lemniscus, reticular formation, ventral part of the 66 medial longitudinal fasciculus and fascicles of cranial nerves IX and X had axonal and terminal degeneration. Moderate to severe degeneration was noted in the gracile-cuneate, lateral cervical, external cuneate and lateral paragigantocellular reticular nuclei. Parvocellular and gigantocellular reticular nuclei had light and scattered degeneration. The nucleus cerebellaris internus in the cerebellum showed. moderate degeneration. Degenerating fibers were noted in the forebrain and midbrain, in the paleostriatum primitivum, lateral forebrain bundle, ansa lenticularis, dorso-intermediate posterior thalamic nucleus, pedunculopontine tegmental nucleus, and lateral spiriform nucleus. The brain auditory and visual systems in the Japanese quail were also affected. Lesions were noted in the lateral mesencephalic nucleus, pars dorsalis, thalamic nucleus ovoidalis, neostriatum caudalis, thalamic nucleus rotundus and ectostriatum. The distribution of neuropathy in hens dosed with TPP (Figures 8 and 9) is similar to that noted in TPP-dosed Japanese quail. Slight to moderate degeneration was noted in hens dosed with 1000 mg TPP/kg body weight (Carrington.et a1., 1988a; Tanaka et a1., 1992). Moderate degeneration was noted in the medulla in the lateral vestibular, gracile-cuneate, external cuneate and lateral cervical nuclei. Less degeneration was noted in the solitary, inferior olivary and raphae nuclei, in the medial and dorsal vestibular nuclei, and in the lateral paragigantocellular, gigantocellular, and lateral reticular nuclei. In the cerebellum, mossy fiber 67 mfimHUDZ HMHSQHHUWOKV Hflhmflflfl 90> “CHEMQ «AHMHHSUOS HMMHOQ g ma0HUsz unflsnflum0> unfloc0om0o 90> md0a092 0900:5010Hw00uo muommaou whom 0:0Hoaz owamaona .ms0aosz H0OC0Bm0B 0cwusomloadogp0m 0mm. nowu0umom 0uoao0fiu0uswlomuoo 090aosz Hoswmmmumsm mm ms0HUsz H00H>H0U HOH0umq ms0aosz 0swusom H0H0umq gm whammwaaoo u0flu0uc4 090Hosz hum>wao u0flu0ucH Ho adaa0n0n0u asu0fluumo0z Hopooo Oz mannaoowus0q 00nd A30fi> swap0a Houuflmmmv sauna c0xowno 0:» CH c0wumu0c0m0o o0oopcwlmma .m musmflm 00 mn .HU d0 m0 Q4 68 aaumwuumo0aom adumwnumo0z Hocamo mwaumuoa whom .mfl0ausz owaonm0oc0m0: H0H0uoq aaunwhumouum A30fl> Hmu0umH Hmuuwmmmv sauna smxoflco 0gp CH cofiumu0c0m0o p0oopsfinmm9 m 02 GAS m .m 0Hsmwm 69 degeneration was noted in the granular layer of foliae I - Vb, especially in foliae IV and V. The degenerating fibers were noted as alternating parasagittal bands of heavy and light degeneration. The deep cerebellar nuclei also had small amounts of coarse fiber degeneration. unlike the Japanese quail, no lesions were found in the auditory and visual systems of the chicken (Figures 8 and 9). Despite the similarity in neuropathological changes, neuropathy in the Japanese quail was detected earlier and at lower doses than in the hen. Swollen axons are present in the brainstem of hens dosed with 1000 mg TPP/kg body weight at day 7 post-dosing (Carrington et a1. , 1988) whereas Japanese quail dosed with 250 and 500 mg TPP/kg body weight in the present study showed degeneration on day 3 post-dosing. Some birds dosed with 500 mg TPP/kg body weight showed clinical signs as early as.day'1 post-dosing; .Although birds were not taken for perfusion until day 3, it can be speculated that degeneration is present in the CNS of the Japanese quail on day 1 post- dosing. The earlier onset of TPP-induced neuropathological lesions in Japanese quail in this study may be due to a more rapid distribution of TPP in the Japanese quail. Differences in the location of degeneration may contribute to the severity of clinical signs in different species. Studies by Karten (1967, 1968) and Boord (1969) showed that the pathway of the auditory system in birds begins at the nucleus angularis and continues through the lateral mesencephalic nucleus, pars dorsalis and nucleus ovoidalis to 70 terminate in the caudal neostriatum. Studies on TPP exposure in the chicken by Tanaka et a1. (1992) showed that TPP caused limited degeneration in the forebrain, which included descending motor pathways originating in the basal ganglia and projecting to several midbrain and medullary nuclei. The midbrain lateral mesencephalic nucleus pars dorsalis contains degeneration whereas neither the nucleus ovoidalis nor the caudal neostriatum show any degeneration (Figures 8 and 9). The results of the present study in Japanese quail document for the first time that TPP exposure results in degeneration of the forebrain auditory and visual systems in an avian species. Degeneration was noted especially in the thalamic nucleus and neostriatum of the auditory pathway (Figure 6). The neostriatum is crucial for simultaneous visual discrimination learning, feeding behavior and bodily movements (Salzen and Parker, 1975). As mentioned previously, fine adjustments involved in feeding and preening, like neck, limb, and bill movements, are controlled by sensorimotor coordinating circuits in the neostriatum. Damage to the neostriatum may cause difficulty and inaccuracy in pecking. In the present study, lesions were noted in the neostriatum region of the Japanese quail forebrain whereas no such lesions were noted in TPP-exposed chickens (Tanaka et a1., 1992) . It can be suggested that lesions in the neostriatum contributed to mortality of TPP- exposed. Japanese: quail as ‘the birds face difficulty in locating and consuming feed. 71 Degeneration has been noted in the forebrain and midbrain motor nuclei and pathways of TPP-exposed mammals. Previous studies in mammals have reported extensive degeneration in the thalamus and cerebral cortex following exposure to TPP (Tanaka et a1., 1990, 1992a) and the organophosphate compound soman (McLeod et a1., 1984; Churchill et a1., 1985; Pazdernik et a1., 1985; Lallement et a1., 1993). Tanaka et a1. (1990) reported widespread degeneration in ferrets dosed with 1000 mg TPP/kg body weight. Lesions were noted in the external cuneate nucleus, pontine gray, nucleus of the reticular formation, red nucleus, superior olivary nucleus, inferior colliculus, ventral lateral nucleus and the lateral geniculate nucleus. Rats, like the Japanese quail, though resistant to TOTP- induced neuropathy, are sensitive to TPP (Lehning et a1. , 1990; Tanaka et a1., 1992b). Large amounts of CNS degeneration were noted in rats administered 1184 mg TPP/kg body weight. Degeneration was noted in the sensorimotor cerebral cortex, auditory cortex, medial geniculate thalamic nucleus, ventral medial thalamic nucleus, substantia nigra, pars compacta and the deeper layers of the superior colliculus. Though the Japanese quail is sensitive to TPP, the present study confirms the results from previous studies (Francis et a1., 1980; Bursian et a1., 1982) indicating that this species is resistant to TOTP-induced neuropathy. Widespread degeneration was absent in the brain of the 72 Japanese quail administered TOTP (Figure 7). Moderate degeneration was noted in nucleus cerebellaris internus in the cerebellum and gracile-cuneate nucleus in the medulla. Lighter amounts of lesions were noted in the medullary nucleus supraspinalis and inferior olivary nucleus. Unlike the Japanese quail, the domestic chicken is very sensitive to TOTP. Neuropathological lesions were confined to the medulla and cerebellum in hens dosed with 500 mg TOTP/kg body weight (Tanaka and Bursian, 1989). Moderate amounts of degeneration were noted in the lateral vestibular, gracile, external cuneate and lateral cervical nuclei. Lesser amounts of degeneration were noted in the solitary nucleus, inferior olivary nucleus, and.raphae nucleus, in the medial, descending and lateral 'vestibular' nuclei, and. in. ‘the lateral paragigantocellular, gigantocellular, and lateral reticular nuclei. Medullary portions of the dorsal and ventral spinocerebellar tracts and spinal lemniscus had fiber degeneration. Moderate amounts of degeneration were also noted in the deep cerebellar nuclei and granular layers of cerebellar folia I - V in the cerebellum. Rats appear to be somewhat more resistant to TOTP-induced neuropathy than the Japanese quail. Rats dosed with 1160 mg TOTP/kg body weight had no neuropathological lesions in the brainstem region (Veronesi and Dvergsten, 1987). However, degeneration was noted in the fasciculus gracilis at the cervical level and dorsolateral columns at the lumbar levels in the spinal cord. The rat is an example of a mammalian 73 species similar to the Japanese quail in terms of resistance to Type I OPIDN. The present histological examinations are consistent with previous studies which indicate that TPP causes OPIDN. The results indicate that TPP causes degeneration in the auditory and visual areas of the brain in addition to the forebrain, midbrain, cerebellum and medulla. The distribution of neuropathological lesions, however, indicates that the biochemical activity of TPP differs among species. CONCLUSION This study demonstrated that TPP is neurotoxic in the Japanese quail based on the development of clinical signs, whole-brain NTE inhibition and the presence of neuropathological lesions. The Japanese quail may serve as an excellent model for the study of TPP neurotoxic effects in avian species. The Japanese quail is perhaps a better model for Type II OPIDN studies than the hen as it appears to be very sensitive to TPP as indicated by the early onset of clinical signs, lower threshold dose for NTE inhibition, and the degeneration of many motor and sensory nuclei and pathways. It should also be noted that the Japanese quail is not a suitable model for Type I OPIDN as it is resistant to neurotoxic effects of TOTP indicated by the absence of clinical signs and widespread degeneration. The Japanese quail is similar to the rat in regard to sensitivity to Type I and Type II OPIDN. The distinctly different clinical, biochemical and neuropathological profiles produced by Type I and Type II OPIDN compounds in Japanese quail suggest that different mechanisms may be responsible for their neuropathological effects. The Japanese quail is an excellent avian model for studying the differences in'Type I and Type II OPIDN mechanisms. The neuropathological lesions caused by TPP in. Japanese quail are «different from those in. the hen suggesting further that the neurotoxic effects of the same chemical vary among species. 74 LIST OF REFERENCES LIST OF REFERENCES Abou-Donia, M. B. (1976) Pharmacokinetics of a neurotoxic oral dose of leptophos in hens. Arch. Toxicol. 36: 103-110 Abou-Donia, M. B. (1978) Role of acid.phosphatase inidelayed neurotoxicity induced by leptophos in hens. Biochem. Pharmacol. 27: 2055-2058 Abou-Donia, M. B. (1981) Organophosphorus ester-induced delayed neurotoxicity. .Ann. Rev. Pharmacol. Toxicol. 21:511- 548 Abou-Donia, M. B. (1983) Toxicokinetics and metabolism of delayed neurotoxic organophosphorus esters . Neurotoxicol . 4:89-105 Abou-Donia, M. B. (1984) Toxicokinetics of Organophosphorus Esters. In.Delayedeeurotoxicity, ed. J. M. Cranmer and.E. J. Hixon, Intox Press, Little Rock, AR. Abou-Donia, M. B. and Brown, H. R. (1990) Triphenyl phosphite a Type II OPIDN compound. In Proc. Spring Natl. Meet. Am. Chem. Soc. April 1990. Boston, MA. (Abstract No. 107) Abou-Donia, M. B. and Graham, D. G. (1978a) Delayed neurotoxicity of O-ethyl O-4-nitrophenyl phenylphosphonithioate: Subchronic (90 days) oral administration in.hens. Toxicol. Appl. Pharmacol. 45:685-700 Abou-Donia, M. B. and Graham, D. G. (1978b) Delayed neurotoxicity from long-term low-level topical administration of leptophos to the comb of hens. Toxicol. Appl. Pharmacol. 46:199-213 Abou-Donia, M. B. and Graham, D. G. (1979) Delayed neurotoxicity of O-ethyl O-4-nitrophenyl phenyl phosphonothioate: Toxic effects of a single oral dose on the nervous system of hens. Toxicol. Appl. Pharmacol. 48:57-66 Abou-Donia, M. B. and Lapadula, D. M. (1990) Mechanism of organophosphorus ester-induced delayed neurotoxicity Type I and Type II. Ann. Rev. of Pharmacol. and Toxicol. 30:405-440 75 76 Abou-Donia, M. B. and Nomeir, A. A. (1986) The role of pharmacokinetics and metabolism in species sensitivity to neurotoxic agents. Fundam. Appl. Toxicol. 6:190-207 Abou-Donia, M. B., Abdel-Kader, H. M. and Abou-Donia, S. A. (1983a) Tissue distribution, elimination and metabolism of O- ethyl O-4-nitrophenyl phenylphosphonithioate in hens following daily dermal doses. J. Amer. Coll. Toxicol. 2: 391-403 Abou-Donia, M. B., Kinnes, C. G., Abdo, K. M. and Bjornsson, T. D. (1983b) Physiologic disposition and metabolism of O- ethyl O-4-nitrophenyl phenylphosphonothioate in male cats following a single dermal administration. Drug Met. Dispos. 11: 31-36 Abou-Donia, M. B., Makkawy, H. M., Salama, A. E. and Graham, D. G. (1982) Effects of age on hens on their sensitivity to delayed neurotoxicity induced by a single dose of tri-o-tolyl phosphate. Toxicologist 2:178 Abou-Donia, M. B., Othman, M. A., Tantawy, G., Khalil, A. z. and Shawer, M. F. (1974) Neurotoxic effect of leptophos. Experientia 30:63-64 Abou-Donia, M. B., Reichert, B. L., Ashry, M. A. and Graham, D. G. (1983c) Toxicokinetics and metabolism of a single dose of O-ethyl O-4-nitrophenyl phenylphosphonothioate. Toxicol. Appl. Pharmacol. 70: 18-28 Abou-Donia, M. B., Trofatter, L. P., Graham, D. G. and Lapadula, D. M. (1986) Electromyographic, neuropathological and functional correlates in the cat as the result of tri-o- cresyl phosphate delayed neurotoxicity. Toxicol. Appl. Pharmacol. 83:126-141 Aird, R. B., Cohn, W. E. and Wiess, S. (1940) Convulsive action of triphenyl phosphite. Proc. Soc. Exp. Biol. Med. 45:306-309 Aldridge, W. N. and Barnes, J. M. (1961) Neurotoxic and biochemical properties of some triaryl phosphates. Biochem. Pharmacol. 6:177-188 Aldridge, W. N. and Barnes, J. M. (1966) Further observations on the neurotoxicity of organophosphorus compounds. Biochem. Pharmacol. 15:541-548 Aldridge, W.N. and Reiner, E. (1972) Enzyme inhibitors as substrates. In Interaction of Esterases with Esters of Organophosphorus and carbamic Acid, Frontiers of Biology Vol XII, ed. A. Neuberger and E.L. Tatum, North Holland Publishing, Amsterdam, Holland. pp 53-90 77 Aldridge, W. N., Barnes, J. M. and Johnson, M. K. (1969) Studies on delayed neurotoxicity produced by some organophosphorus compounds. Ann. NY Acad. Sci. 160:314-322 Anonymous, Tri-cresyl phosphate found in oil. (1988) Durham Morning Herald, Aug. 4. p. 2A Aring, C. D. (1942) The systemic nervous affinity of tri- orthocresyl phosphate (Jamaica ginger palsy). Brain 63:34-47 Baker, T., Lowndes, H. E., Johnson, M. K. and Sandberg, I. C. (1980) The effects of phenylmethanesulfonyl fluoride on delayed organophosphorus neuropathy. Arch. Toxicol. 46:305- 311 Barnes, J. M. and Denz, F. A. (1953) Experimental demyelination with organophosphorus compounds. J. Pathol. Bacteriol. 65:597-605 Baron, R. (1981) Delayed neurotoxicity and other consequences of organophosphate esters. Ann. Rev. Entomol. 26:29-48 Baron, R. L. , Bennett, D. R. and Casida, J. E. (1962) Neurotoxic syndrome produced in chickens by a cyclic phosphate metabolite of tri-o-cresyl phosphate - A chemical and pathological study. Brit. J. Pharmacol. Chemother. 18:465-474 Barrett, D. S. and Oehme, F. W. (1985) A review of organophosphorus ester-induced delayed neurotoxicity. vet. Hum. Toxicol. 27:22-37 Bidstrup, P. L., Bonnell, J. A. and Beckett, A. G. (1953) Paralysis following poisoning by a new organic phosphorus insecticide (Mipafox). Brit. Med. J. 1:1068-1072 Bischof f , A . ( 197 0) Ultrastructure of tri-ortho-cresyl phosphate poisoning in the chicken. II. Studies on spinal cord alteration. Acta. Neuropathol. 15:142-155 Bleiberg, M. J. and Johnson, H. (1965) Effects of certain metabolically active drugs and oximes on tri-o-cresyl phosphate toxicity. Toxicol. Appl. Pharmacol. 7:227-235 Bond, J. S. and Butler, P. E. (1987) Intracellular proteases. Ann. Rev. Biochem. 56:333-364 Bondy, H. F., Field, E. J., Worden, A. N. and Hughese, J. P. W. (1961) A study on the acute toxicity of the triaryl phosphates used as plasticizers. Brit. J. Indust. Med. 17:190-200 Boord, R. L. (1969) The anatomy of the avian auditory 78 system. Ann. N. Y. Acad. Sci. 167: 186-198 Bouldin, T. W. and Cavanagh, J. B. (1979) A teased-fiber study of the spatiotemporal spread of axonal degeneration. Am. J. Pathol. 94:241-252 Bursian, S. J., Brewster, J. S. and Ringer, R. K. (1983) Differential sensitivity to the delayed neurotoxic tri-o-tolyl phosphate in several avian species. J. Toxicol. and Environ. Health 11:907-916 Calabrese Jr., L. F. and Bursian, S. J. (1984) The effect of hepatic mixed-function oxidase enzyme inducers on the development of tri-o-tolyl phosphate-induced delayed neurotoxicity. J. Toxicol. and Environ. Health 14:145-151 Carboni, D., Ehrich, M., Dyer, K. and Jortner, B. S. (1992) Comparitive evolution of mipafox-induced delayed neuropathy in rats and hens. Neurotoxicol. 13:723-734 Carrington, C. D. and Abou-Donia, M. B. (1984) The correlation between the recovery rate of neurotoxic esterase activity and sensitivity to organophosphorus-induced neurotoxicity. Toxicol. Appl. Pharmacol. 75:350-357 Carrington, C. D. and Abou-Donia, M. B. (1988a) Triphenyl phosphite neurotoxicity in the hen: inhibition of neurotoxic esterse and a lack of prophylaxis by phenylmethylsulfonyl fluoride. Arch. Toxicol. 62:375-380 Carrington, C. D. and Abou-Donia, M. B. (1988b) Variation between three strains of rat: inhibition of neurotoxic esterase and acetylcholinesterase by tri-ortho-cresyl phosphate. J. Toxicol. Environ. Health 25:259-268 Carrington, C. D., Brown, H. R. and Abou-Donia, M. B. (1988a) Histopathological assessment of triphenyl phosphite neurotoxicity in the hen. Neurotoxicol. 9(2):223-234 Carrington! C. D., Burt, C. T. and Abou-Donia, M. B. (1988b) In vivo lP nuclear magnetic resonance studies on the absorption of triphenyl phosphite and tri-o-cresyl phosphate following subcutaneous administration in hens. Pharmacol. and Expt. Ther. Vol 16, No 1 Caroldi, S., Lotti, M. and.Masutti, A. (1984) Intra-arterial injection of diisopropylfluorophosphate or phenylmethane sulfonyl fluoride produces unilateral neuropathy or protection, respectively, in hens. Biochem. Pharmacol. 33:3213-3217 Casida, J. (1961) Specificity of substituted phenyl phosphorus compounds for esterase inhibition in mice. 79 Biochem. Pharmacol. 5: 332-342 Casida, J. E., Eto, M. and Baron, R. L. (1961) Biological activity of a tri-o-cresyl phosphate metabolite. Nature 191:1396-1397 Cavanagh, J. B. (1954) The toxic effects of tri-ortho cresyl phosphate on the nervous system. An experimental study in hens. J. Neurol. Neurosurg. Psychiatr. 17:163-172 Cavanagh, J. B. (1964a) The significance of the "dying back" process in experimental and human neurological disease. Int. Rev. Exp. Path. 3:219-267 Cavanagh, J. B. (1964b) Peripheral nerve changes in ortho- cresyl phosphate poisoning in the cat. J. Pathol. Bacterol. 87: 365-383 Cavanagh, J. B. (1973) Peripheral neuropathy caused by chemical agents. Crit. Rev. Toxicol. 2(3):365-417 Cavanagh, J. B. and Patangia, G. N. (1965) Changes in the central nervous system in the cat as the result of tri-o- cresyl phosphate poisoning. Brain 88:165-180 Chadwick, R. W., Copeland, M. F., Soliman, S. A., Froehlich, R., Perry, J. D., Farmer, J. D. and Watts, R. R. (1982) Comaparitive disposition of leptophos in the rat and chicken 24 hours after a single dose or iv dose. Vet. Hum. Toxicol. '24:219 Cherniak, M. G. (1988) Toxicological screening for organophosphorus-induced delayed neurotoxicity: Complications in toxicity testing. Neurotoxicol. 9: 249-272 Churchill, L., Pazdernik, T. L., Jackson, J. L., Nelson, S. R., Samson, F. B., McDonough, Jr., J. and McLeod, Jr., C. G. (1985) Soman-induced brain lesions demonstrated by muscarinic receptor autoradiography, Neurotoxicol. 6: 81-90 Clothier, B. and Johnson, M. K. (1979) Rapid aging of neurotoxic esterase after inhibiton of diisopropyl phosphofluoridate. J. Biochem. 177:549-558 Cohen, J. A. and Oosterbaan, R. A. (1963) The active site of acetylcholinesterase and related esterases and its reactivity towards substrates and inhibitors. In Handbuch der Experimentsllen Pharmakologie, XV, (Cholinesterase and Anticholinesterase Agents), ed. G. B. Koelle, Springer, Berlin. pp. 299-373 Davis, C. S. and Richardson, R. J. (1980) Organophosphorus compounds. In.Experimental and Clinical Neurotoxicology, ed. 80 P. S. Spencer and H. H. Schaumburg, Williams and Wilkins, Baltimore, MD. pp. 527-544 Davis, C. S., Johnson, M. K. and Richardson, R. J. (1985) Organophosphorus compounds, In Neurotoxicity of Industrial and Commercial Chemicals Vol II, ed. J. L. O'Donoghue, CRC Press, Boca Raton, FL. pp. 1-23 De Jager, A. E. J., Van Weerdon, T. W., Houthoff, H. J. and De Monchy, J. G. R. (1981) Polyneuropathy after massive exposure to parathion. Neurol. 31:603-605 Draper, H. B., James, M. F. and Johnson, B. C. (1952) Tri-o- cresyl phosphate as a vitamin E antagonist for the rat and lamb. J. Nutr. 47:583-597 Dyer, K. R. , Jortner, B. S. , Shell, L. G. and Ehrich, M. (1992) Comparitive dose-response studies of organophosphorus ester-induced delayed neuropathy in rats and hens administered mipafox. Neurotoxicol. 13:745-756 Ecobichon, D. J. (1991) Toxic effects of pesticides. In Casarett and Doull 's Toxicology, The Basic Science of Poisons, 4th ed., ed. M. O. Amdur, J. Doull and C. D. Klaassen, Pergamon Press, New York, NY. pp. 565-622 Ehrich, M., Jortner, B. S. and Gross, W. B. (1985) Absence of a protective effect of corticosterone on O-O-diisopropyl phosphofluoridate (DFP) induced. delayed neurotoxicity in chickens. Neurotoxicol. 6:87-92 El-Fawal, H. A. N., Jortner, B. S. and Ehrich, M. (1990) Use of the biventer-cervicis nerve-muscle preparation to detect early changes following exposure to organophosphates inducing delayed neuropathy. Fundam. Appl. Toxicol. 15: 108-120 Eto, M. (1979) Organophosphorus Pesticides: Organic and Biological Chemistry, CRC Press, Boca Raton, FL. 387 pp. Eto, M., Casida, J. E. and Eto, T. (1962) Hydroxylation and cyclization reactions involved in the metabolism of tri-o- cresyl phosphate. Biochem. Pharmacol. 11:337-352 Eto, M., Oshima, Y. and Casida, J. E. (1967) Plasma albumin as a catalyst in cyclization of tri-aryl-o- (-hydroxyl) -tolyl phosphates. Biochem. Pharmacol. 16:295-308 Fisher E. B. and Van Wazer, J. R. (1961) Uses of organic phosphorus compounds. In Phosphorus and its Compounds Vol II, ed. J. R. Van Wazer, Interscience, New York, NY. pp. 1897- 1936 Francis, B. M., Hansen, L. and Metcalf, R. L. (1980) 81 Response of Japanese quail (CoturniX' coturnix) to organophosphorus ester-induced delayed neurotoxicity relative to domestic hens (Gallus gallus domesticus). Bull. Environ. Contam. Toxicol. 25:537-540 Fukuhara, N., Hoshi, M. and Mori, S. (1977) Core/targetoid fibers and multiple cycloplasmatic bodies in organophosphate neuropathy. Acta. Neuropathol. 40:137-144 Gill, J. L. (1978) Design and.Analysis of.Experiments in the Animal and Medical Sciences Vol. I, Iowa State University Press, Ames, IA. 410 pp. Goldstein, D. A., McGuigan, M. A. and Ripley, B. D. (1988) Acute tricresylphosphate intoxication in childhood. Human Toxicol. 7:179-182 Herin, R. A, Komeil, A. A., Graham, D. G., Curley, A. and Abou-Donia, M. B. (1978) Delayed neurotoxicity induced by organophosphorus compounds in the wild mallard duckling: Effect of leptophos. J. Environ. Pathol. Toxicol. 1:233-240 Hess, R., Thomann, P. and.Rinke, G. (1978) The assessment of neurotoxicity in laboratory animalsu In.Rroc. 1st Int. Congr. Toxicol., ed. G. L. Plaa and W. A. M. Duncan, Academic Press, New York, NY. pp. 245-268 Hierons, R. and Johnson, M. K. (1978) Clinical and toxicological investigations of a case of delayed neuropathy in man after acute poisoning by an organophosphorus pesticide. Arch. Toxicol. 40:279-284 Holmstead, R. L., Fukuto, T. R. and March, R. B. (1973) The metabolism of O-(4-bromo-2, 5,-dichlorophenyl) O-methyl phenyl phosphonothioate (leptophos) in white mice and on cotton plants. Arch. Environ. Contam. Toxicol. 1:133-147 Hopkins, A. P. (1975) Toxic Neuropathy due to Industrial Agents. In Peripheral Neuropathy, ed. P. J. Dyck, P. K. Thomas, and E. H. Lambert, W. B. Saunders, Philadelphia, PA. pp. 1207-1226 Hunter, D., Perry, K. M. A. and Evans, R. B. (1944) Toxic poly neuritis arising during the manufacture of tricresyl phosphate. Brit. J. of Indust. Med. 1:227 Hussain, M. D. and Olaffa, P. C. (1979) Neurotoxic effects of leptophos (Phosvel) in chickens and rats following chronic low-level feeding. J. Environ. Sci. Health B 14(4):367-382 Inui, K. , Mitsumori, K. , Harada, T. and Maita, K. (1993) Quantitative analysis of neuronal damage induced by tri-ortho- cresyl phosphate in Wistar rats. Fundam. Appl. Toxicol. 82 20:111-119 Itoh, H., Kishida, H., Tadokoro, M. and Oikawa, K. (1984) Studies on the delayed neurotoxicity of organophosphorus compounds-(II). J. Toxicol. Sci. 9:37-50 Itoh, H., Tadokoro, M. and Oikawa, K. (1981) Studies on the delayed neurotoxicity of organophosphorus compounds-(I). J. Toxicol. Sci. 6:287-300 Jedrzejowski, H., Rowinska-Marcinska, K. and Hoppe, B. (1980) Neuropathy due to phytosol (agritox) . Acta. Neuropathol. (Berl.) 49:163-168 Johnson, M. K. (1969a) Delayed neurotoxic action of some organophosphorus compounds. Brit. Med. Bull. 25:231-235 Johnson, M. K. (1969b) The delayed neurotoxic effect of some organophosphorus compounds. Identification of the phosphorylation site as an esterase. J. Biochem. 114:711-717 Johnson, M. K. (1969c) A phosphorylation site in brain and the delayed neurotoxic effect of some organophosphorus compounds. J. Biochem. 111:487-495 Johnson, M. K. (1970) Organophosphorus and other inhibitors of brain ”neurotoxic esterase" and the development of delayed neurotoxicity in hens. J. Biochem. 120:523-531 Johnson, M; K. (1974) The primary biochemical lesion leading to the delayed neurotoxic effects of some organophosphorus esters. J. Neurochem. 23:785-789 Johnson, M. K. (1975a) Organophosphorus esters causing delayed neurotoxic effects. Arch. Toxicol. 34:259-288 Johnson, M. K. (1975b) The delayed neuropathy caused by some organophosphorus esters: mechanism and challenge. Crit. Rev. Toxicol. 3:289-316 Johnson, M. K. (1976a) Mechanism of protection against the delayed nerotoxic effects of organophosphorus esters. Fed. Proc. 35:73-74 Johnson, M. K. (1976b) Structure-activity relationships among organophosphorus esters with respect to delayed neuropathy. In Pesticide Induced Delayed Neurotoxicity, ed. R. L. Baron, U.S. Environmental Protection Agency, Research Triangle Park, NC. pp. 70-83 Johnson, M. K. (1977) Improved assay of neurotoxic esterase for screening organophosphates for delayed neurotoxicity potential. Arch. Toxicol. 37:113-115 83 Johnson, M. K. (1982) The target site for the initiation of delayed neurotoxicity by organophosphorous esters: biochemical studies and toxicological applications. Rev. Biochem. Toxicol. 4:141-212 Johnson, M. K. and Barnes, J. M. (1970) Age and the sensitivity of chicks to the delayed neurotoxic effects of some organophosphorus compounds. Biochem. Pharmacol. 19:3045- 3047 Jortner , B . S . and Ehrich , M. (1987) Neuropathological effects of phenyl saligenin jphosphate in chickens. Neurotoxicol. 8:97-108 Jortner, B. S., Shell, L., El-Fawal, H. and Ehrich, M. (1989) Myelinated nerve fiber regeneration following oraganophosphorus ester-induced delayed neuropathy. Neurotoxicol. 10:717-726 Karten, H. J. (1967) The organization of the ascending auditory pathway in the pigeon (Columbia livia). I. Diencephalic projections of the inferior colliculus (nucleus mesencephali lateralis, pars dorsalis). Brain Research 6: 409-427 Karten, H. J. (1968) The ascending auditory pathway in the pigeon (Columbia livia) . II. Telencephalic projections of the nucleus ovoidalis thalami. Brain Research 11: 134-153 Karten, H. J. (1969) The organization of the avian telencephalon and some speculation on the phylogeny of the amniote telencephalon. Ann. N. Y. Acad. Sci. 167: 164-179 Katoh, K., Konno, N., Yamauchi, T. and Fukushima, M. (1990) Effects of age of susceptibility of chickens to delayed neurotoxicity due to triphenyl phosphite. Pharmacol. Toxicol. 66:387-392 Kidd, J. G. and Langworthy, O. R. (1933) Jake Paralysis - Paralysis following the ingestion of Jamaican ginger extract adulterated with tri-ortho-cresyl phosphate. Bull. Johns Hopkins Hosp. 7:39 Kinebuchi, H., Konno, N., Yamauchi, T., Kaneda, N. and Sasaki, K. (1977) Delayed neurotoxicity caused by divided administration of critical doses of an organophosphorus insecticide Phosvel (leptophos). Igaku No Ayumi (Prog. Med.) 101(12):837-838 Knoth-Anderson, J. and Abou-Donia, M. B. (1993) Differential effects of triphenyl phosphite and diisopropyl phosphorofluoridate on catecholamine sectretion from bovine adrenomedullary chromaffin cells. J. Toxicol. Environ. Health 84 38:103-114 Konno, N. and Kinebuchi, H. (1978) Residues of phosvel in plasma and in adipose tissue in hens after single oral administration. Toxicol. Appl. Pharmacol. 45:541-547 Konno, N. K., Katoh, K., Yamauchi, T. and Fukushima, M. (1989) Delayed neurotoxicity of triphenyl phosphite in hens: Pharmacokinetics and biochemical studies. Toxicol. Appl. Pharmacol. 100:440-450 Kruckenberg, S. M., Stafuss, A, C., Marsland, W. P., Blauch, B. S., March, R. T., Vestwebr, J. G. E. and Winter, W. G. (1973) Posterior paresis in swine due toidermal absorption of the neurotoxic organophosphate tri-o-tolyl phosphate. Am. J. Vet. Res. 34:403-404 Lallement, G., Delamanche, I. S., Pernot-Marino, I., Baubichon, D., Denoyer, M., Carpenter, P. and Blanchet, G. (1993) Neuroprotective activity of glutamate receptor antagonists against soman-induced hippocampal damage: quantification with an omega 3 site ligand. Brain Research 618: 227-237 Larsen, C., Jortner, B. S. and Ehrich, M. (1986) Effect of neurotoxic organophosphorus compounds in turkeys. J. Toxicol. Environ. Health 17:365-374 Lasker, J. M., Graham, D. G. and Abou-Donia, M. B. (1982) Differential metabolism of O-ethyl O-4-nitrophenyl phenylphosphonothioate by rat and chicken liver microsomes: A factor in species selectivity to delayed neurotoxicity. Biochem. Pharmacol. 31: 1961-1967 Lehning, E., Tanaka, Jr., D. and Bursian, S. J. (1990) Widespread axonal and terminal degeneration in the forebrain of the rat after exposure to triphenyl phosphite (TPP). The Toxicologist 10:341 Lillie, R. D. and Smith, M. I. (1932) The histopathology of some neurotoxic phenol esters. Natl. Inst. Health. Bull. 160:54-69 Lotti, M. and Johnson, M. K. (1978) Neurotoxicity of organophosphorus pesticides: Predictions can be based on in vitro studies with hen and human enzyme. Arch. Toxicol. 41:215-221 Lotti, M. and Morretto, A. (1986) Inhibition of lymphocyte neuropathy target esterase predicts the development of organophosphate polyneuropathy in man. Hum. Toxicol. 5:114 Majno, G. and Karnovsky, M. L. (1961) A biochemical and 85 morphologic study of myelination and demyelination. III. Effect. of an. organophosphorus compound. (mipafox) on ‘the biosynthesis of lipid by nervous tissue of rats and hens. J. Neurochem. 8:1-16 Malone, J. C. (1964) Toxicity of Haloxon. Res. Vet. Sci. 5:17-31 McLeod, Jr., C. G., Singer, A. W. and Harrington, D. G. (1984) Acute neuropathology in soman poisoned rats. Neurotoxicol. 5: 53-58 Metcalf, R. In (1982) Historical perspective of organophosphorus ester-induced delayed neurotoxicity. Neurotoxicol. 3:269-284 Metcalf, R. L. (1984) Historical perspective of organophosphorus ester-induced delayed neurotoxicity. In Delayed Neurotoxicity, ed. J. M. Cranmer and E. J. Hixson, Intox Press, Little Rock, AR. Metcalf, R. L., Branch, C. E., Swift, T. R., Sikes, R. K. (1985) Neurologic findings among workers exposed to Fenthion in a veterinary hospital-Georgia. Morbid. Mortal. Week. Rep. 34:402-403 Murphy, S. C. (1975) Pesticides in Toxicology. In.The Basic Science in Pbisons, ed. J. Doull, C. D. Klaassen and M. O. Amdur, Macmillan.Publishing Co. Inc, New‘York. NY; pp 519-581 Nomeir, A. A. and Abou-Donia, M. B. (1984) Disposition of 14C tri-o-cresyl phosphate and its metabolites in various tissues of the male cat following a single dermal application. Drug Metab. Dispos. 12:705-711 Nomeir, A. A. and Abou-Donia, M. B. (1986) Studies on the metabolism of the neurotoxic tri-o-cresyl phosphate. Distribution, excretion and metabolism in male cats after a single, dermal application. Toxicol. 38:15-33 Olson, B. A. and Bursian, S. J. (1988) Effect of route of administration on the development of organophosphate-induced delayed neurotoxicity in 4-week-old chicks. J. Toxicol. and Environ. Health, 23:499-505 Padilla, S. and Veronesi, B. (1985) 'The relationship between neurological damage and neurotoxic esterase inhibition in rats acutely exposed to tri-ortho-cresyl phosphate. Toxicol. Appl. Pharmacol. 78:78-87 Padilla, S. and ‘Veronesi, B. (1988) Biochemical and morphological validation of a rodent model of organophosphorus-induced delayed neuropathy. Toxicol. Indust. 86 Health. 4:361-371 Padilla, S., Grizzle, T. B. and Lyerly, D. (1987) Triphenyl phsophite; in vivo and in vitro inhibition of rat neurotoxic esterase. Toxicol. Appl. Pharmacol. 87:249-256 Pazdernik, T. L., Cross, R. L., Giesler, M., Nelson, S., Samson, F. and McDonough, Jr., J. (1985) Delayed effects of soman: brain glucose use and.pathology. Neurotoxicol. 6: 61- 70 Peraica, M., Capodicasa, E., Moretto, A. and.Lotti, M. (1993) Organophosphate polyneuropathy in chicks. Biochem. Pharmacol. 45:131-135 Pope, C. N. and Padilla, S. (1990) Potentiation of organophosphorus-induced delayed neurotoxicity by phenylmethylsulfonyl fluoride. J. Toxicol. Environ. Health 31:261-273 Pope, C. N., Chapman, M. L., Tanaka, D. Jr. and Padilla, S. (1992) Phenylmethyl sulfonyl fluoride alters sensitivity to organophosphorus-induced delayed neurotoxicity in developing animals. Neurotoxicol. 13:355-364 Prentice, D. E. and Roberts, N. L. (1983) Acute delayed neurotoxicity in hens dosed with tri-ortho-cresyl phosphate (TOCP): Correlation between clinical ataxia and neuropathological findings. Neurotoxicol. 4: 271-283 Prineas, J. (1969) The pathogenesis of dying-back polyneuropathies: An ultrastructural study of experimental tri-ortho-cresyl phosphate intoxication in the cat. J. Neuropath. Expt. Neurol. 28:571-597 Richardson, R. J. (1984) Neurotoxic esterase: Normal and pathogenic roles. In Cellular and.Molecular'Neurotoxicology, ed. T. Narahasi, Raven Press, New York, NY. pp. 285-295 Roberts, N. L. , Prentice, D. E. and Cooke, L. (1982) Screening test for neurotoxicity of triphenyl phosphite in the chicken following oral exposure. Huntingdon.Research Center, Huntingdon, Cambridgeshire, England Salzen, E. A. and. Parker, D. M. (1975) .Arousal and orientation functions of the avian telencephalon in Neural and Endocrine Aspects of Behavior in Birds, ed. P. Wright, P. Caryl and D. Vowles, Elsevier Scientific Publishing Co., Oxford, UK. pp 205-242 Senanayake, N. (1981) Tri-cresyl phosphate neuropathy in Sri Lanka: A clinical and neurophysiological study with a three follow-up. J. Neurol. Neurosurg. Psychiatr. 44:775-780 87 Senanayake , N . and Johnson , M . K . ( 19 8 2 ) Acute polyneuropathy after poisoning by a new organophosphate insecticide. New England J. Med. 306:155-157 Smith, H. V. and Spalding, J. M. K. (1959) Outbreak of paralysis in Morocco due to ortho-cresyl phospate poisoning. Lancet, 1019-1021 Smith, M. I. and Elvove, E. (1930) Pharmacological and chemical studies of the cause of so-called ginger paralysis. Prelim. Rept. Public. Health. Rep. 45:1703 Smith, M. I. and Lillie, R. D. (1931) The histopathology of tri-ortho-cresyl phosphate poisoning . Arch . Neurol . Psychiatr. 26:976-992 Smith, M. I., Elvove, E., and Frazier, W. H. (1930a) The pharmacological action of certain.phenols esters with special reference to the etiology of so-called ginger paralysis. U.S. Public Health Rept. 45:2509 Smith, M. I., Elvove, E., Valer, P. J., Frazier, W. H. and Mallory, G. E. (1930b) Pharmacological and chemical studies of the cause of so-called ginger paralysis. U.S. Public Health Rept. 45:1703-1716 Smith, M. I., Engle, E. W. and Stohlman, E. F. (1932) Further studies on the pharmacology of certain phenol esters with special reference to the relation of chemical constitution and physiologic action. Natl. Inst. Health. Bull. 160:1-53 Smith, M. I., Lillie, R. D., Elvove, E. and Stohlman, E. F. (1933) The pharmacologic action of the phosphorus acid esters of the phenols. J. Pharmacol. Exp. Ther. 49:78-99 Somkuti, S. G., Tison, H. A., Brown, H. R., Campbell, G. A., Lapadula, D. M. and Abou-Donia, M. B. (1988) Lack of delayed neurotoxic effect after tri-o-cresyl phosphate treatment in male Fischer 344 rats: Biochemical, neurobehavioral and neuropathological studies. Fundam. Appl. Toxicol. 10:199-205 Sorokin, N. (1969) Orthocresyl phosphate neuropathy: Report of an outbreak in Fiji. Med. J. Aust. 21:506-508 Stuart, L. D. and Oehme, F. W. (1982) Organophosphorus delayed neurotoxicity: A neuromyelopathy of animals and man. Vet. Hum. Toxicol. 24 (2): 107-118 Stumpf, A. M., Tanaka, D., Aulerich, R. J. and Bursian, S. J. (1989) Delayed neurotoxic effects of tri-o-tolyl phosphate in the European ferret. J. Toxicol. and Environ. Health 26:61-73 88 Susser, M. and Stein, z. (1957) An outbreak of tri-ortho- cresyl phosphate (TOCP) poisoning in Durban. Brit. J. of Indust. Med. 14:111-120 Tanaka Jr., D. and Bursian, S. J. (1989) Degeneration patterns in the chicken central nervous system induced by ingestion of the organophosphorus delayed neurotoxic tri- ortho-tolyl phosphate. A silver impregnation study. Brain Res. 484:240-256 Tanaka Jr., D., Bursian, S. J. and Lehning, E. J. (1990a) Selective axonal and terminal degeneration in the chicken brainstem and cerebellum following exposure to bis(1-methyl ethyl) phosphorofluoridate (DFP). Brain Res. 519:200-208 Tanaka Jr., D., Bursian, S. J. and Lehning, E. J. (1992a) Neuropathological effects of triphenyl phosphite on the central nervous system of the hen (Callus domesticus). Fundam. and Appl. Toxicol. 18:72-78 Tanaka Jr., D., Bursian, S. J. and Lehning, E. J. (1992b) Silver impregnation of organophosphorus-induced delayed neuropathy in the central nervous system. In The Vulnerable Brain and Environmental Risks, Vol 2: Toxins in Food, ed. R. L. Isaacson and.K. F. Jensen, Plenum Press, New York, NY. pp. 215-234 Tanaka Jr., D., Bursian, S. J., Lehning, E. J. and Aulerich, R.J. (1990b) Exposure to triphenyl phosphite results in widespread degeneration in the mammalian central nervous system. Brain Res. 531:294-298 Tanaka Jr., D., Bursian, S. J., Lehning, E. J. and Aulerich, R.J. (1991) Delayed neurotoxic effects of bis(1-methyl ethyl) phosphorofluoridate (DFP) in the European ferret: A possible mammalian model for organophosphorus-induced.delayed neurotoxicity. Neurotoxicol. 12:209-224 Taylor, J. D. (1967) A neurotoxic syndrome produced in cats by a cyclic phosphate metabolite of tri-o-cresyl phosphate. Toxicol. Appl. Pharmacol. 11:538-545 U.S. Environmental Protection Agency (1985) Chemical hazard information profile. Triphenyl Phosphite. Draft Rept. Washington, DC: EPA Vasilescu, C. and Florescu, A. (1980) Clinical and electrophysiological study’ of neuropathy after organophosphorus compound poisoning. Arch. Toxicol. 43:305- 315 Vasilescu, C., Alexianu, M. and Dan, A. (1984) Delayed neuropathy after organophosphorus insecticide (Dipterex) 89 poisoning: A clinical, electrophysiological and nerve biopsy study. J. Neurol. Neurosurg. Psychiatr. 47:543-548 Veronesi, B. (1984) A rodent model of organophosphorus- induced delayed neuropathy: Distribution of central (spinal cord) and peripheral nerve damage. Neuropathol. Appl. Neurobiol. 10:357-368 Veronesi, B. and Abou-Donia, M. B. (1982) Central and peripheral neuropathology induced in rats by tri-o-cresyl phosphate (TOCP). Vet. Hum. Toxicol. 24:222 Veronesi, B. and Dvergsten, C. (1987) Triphenyl phosphite neuropathy differs from organophosphorus-induced delayed neuropathy in rats. Neuropathol. Appl. Neurobiol. 13:193-208 Veronesi, B. and Padilla, S. (1985) Phenylmethylsulfonyl fluoride protects rats from mipafox-induced delayed neurpathy. Toxicol. Appl. Pharmacol. 81:258-264 Veronesi, B., Padilla, S. S. and Newland, D. (1986a) Biochemical and neuropathological assessment of tr iphenyl phosphite in rats. Toxicol. Appl. Pharmacol. 83:203-210 Veronesi, B., Padilla, S. and Lyerly, D. (1986b) The correlation between neurotoxic esterase inhibition and mipafox-induced neuropathic damage in rats. Neurotoxicol. 7:207-216 Vora, D. D., Dasutr, D. K., Braganca, B. M., Parihar, L. M., Iyer, C. G. S., Fondekar, R. B. and Prabhakaran, K. (1962) Toxic polyneuritis in Bombay due to ortho-cresyl phosphate poisoning. J. Neurol. Neurosurg. Psychiatr. 25:234-242 Whitacre, D. M., Badie, M., Schwemmer, B. A. and Diaz, L. I. (1976) Metabolism of 14C-leptophos and 14C-4-bromo-2,5- dichlorophenol in rats: A multiple dosing study. Bull. Environ. Contam. Toxicol. 16:689-696 William, D. G. and Johnson, M. K. (1981) Gel-electrophoretic identification of hen brain neurotoxic esterase, labeled with tritiated di-isopropyl phosphorofluoridate. Biochem. J. 199:323-333 Wilson, B. W., Henderson, J. D., Kellner, T. P., Goldman, M., Higgins, J. and Dacre, J. C. (1988) Toxicity of repeated doses of organophosphorus esters in the chicken. J. Toxicol. Environ. Health 23:115-126 Xintaras, C., Burg, J. R., Tanaka, S., Lee, S. T., Johnson, B. L., et a1. (1978) NIOSH health survey of velsicol pesticide workers. Occupational exposure to leptophos and other chemicals. Washington, DC. US Govt. Print. Off. "lllllllllllllllllllli