TILMICOSIN First draft prepared by Dr G. Roberts Commonwealth Department of Health and Family Services Canberra, Australia 1. Explanation 2. Biological data 2.1 Biochemical aspects 2.1.1 Excretion 2.1.2 Biotransformation 2.2 Toxicological studies 2.2.1 Acute studies 2.2.2 Short-term toxicity studies 2.2.3 Long-term toxicity/carcinogenicity studies 2.2.4 Reproductive toxicity studies 2.2.5 Special studies on embryotoxicity and teratogenicity 2.2.6 Special studies on genotoxicity 2.2.7 Special study on the immune system 2.2.8 Special studies on microbiological activity 2.2.9 Special studies on pharmacology 2.3 Observations in humans 3. Comments 4. Evaluation 5. References 1. EXPLANATION Tilmicosin is a macrolide antibiotic with the chemical name of 20-deoxo-20-(3,5-dimethyl piperidin-1-yl) desmycosin. It is structurally similar to tylosin. Tilmicosin is a mixture of one cis and two trans isomers in the approximate ratio 85:15. Tilmicosin is available as an injectable formulation for the treatment of respiratory diseases in cattle and sheep (10 mg/kg bw) and as a feed premix for the treatment and control of respiratory diseases in pigs (200 to 400 mg/kg in the feed). It had not been previously evaluated by the Committee. The molecular structure of tilmicosin is shown below.2. BIOLOGICAL DATA 2.1 Biochemical aspects 2.1.1 Excretion Pigs were administered a dose of 110 mg 14C-tilmicosin in the diet over the course of one day. The recovery of radioactivity was 15% in the urine and 80% in the faeces (Giera & Thomson, 1986). In two studies, pigs were given a dose of 154 or 400 mg 14C-tilmicosin in the diet following a similar dose given for 5 days. The recovery of radioactivity was 4 to 6% in urine and 62 to 75% in faeces. Radioactivity was detected in the bile but was not quantified (Donoho & Thomson, 1988; Donoho et al., 1993). 2.1.2 Biotransformation 2.1.2.1 Rats Tilmicosin, labelled with 14C in both the desmycosin macrolide ring and the piperidine ring, was given orally to 15 male and 15 female Fischer-344 rats. The dosage was 20 mg/kg bw per day for 3 days. In the liver, radiolabel corresponded to tilmicosin and a desmethyl derivative, T1(demethylated in the mycaminose ring). The single radioactive substance identified in urine was unchanged tilmicosin, while in faeces the major peak was parent compound with lesser amounts of desmethyl tilmicosin and a high molecular weight compound known to be present as an impurity in the administered substance, T2 (consisting of two macrolide rings and one piperidine ring) (Donoho, 1988). Fischer-344 rats (10 males and 10 females) were given gavage doses of 50 mg/kg bw per day 14C-tilmicosin for 5 days. An analysis of faecal radioactivity for the presence of the sulfate metabolite that was found in the faeces of pigs revealed the presence of a similar compound, but quantification was not undertaken (Donoho & Kennington, 1993). 2.1.2.2 Sheep Beulah cross lambs were administered a single subcutaneous dose of 20 mg/kg bw per day 14C-tilmicosin. The major radioactive component in the liver, kidneys and urine was the parent drug, together with lesser amounts of T1 and T2, and minor amounts of other unidentified substances (Hawkins et al., 1993). 2.1.2.3 Pigs Pigs were fed diets containing 14C-tilmicosin, which resulted in daily doses of 400 mg, for 5 days. Of the radiolabel in liver and kidney, approximately 60 to 70% was in the form of the parent drug and there were small amounts of T1. Similarly in urine and faeces, there were high levels of tilmicosin and low levels of T1. A further metabolite was detected that comprised 14% of faecal and 25% of urinary radioactivity and that was consistent with reduction of one double bond in the macrolide ring followed by sulfation (Donoho et al., 1993). 2.1.2.4 Cattle In a summary of results obtained in cattle injected with 14C-tilmicosin, it was reported that the radioactivity profile in the liver of treated rats was similar to that in the faeces. In animals treated with a highly purified sample of tilmicosin, metabolite T2 was not detected in the liver, suggesting that its presence was a result of direct administration as a component of the drug substance. Radioactivity in the kidneys was essentially in the form of unchanged tilmicosin (Donoho, 1988). 2.2 Toxicological studies 2.2.1 Acute studies Major signs of toxicity in mice and rats were leg weakness, hypoactivity, lethargy, ataxia, poor grooming and coma. Monkeys given 20 mg/kg vomited during the first day but were subsequently normal. The single monkey given 30 mg/kg vomited, exhibited hypoactivity, laboured respiration, vocalization and ataxia, and died within 2 hours. New Zealand white rabbits (five males and five females) received 5000 mg/kg bw tilmicosin onto clipped skin for a period of 24 hours, under a non-occlusive dressing. There were no deaths and no signs of skin irritation (Jordan et al., 1987). A volume of 0.1 ml (17 mg) of tilmicosin was instilled into one eye of three male and three female New Zealand White rabbits. Conjunctival hyperaemia and chemosis were noted for several days, clearing by the end of one week (Jordan et al., 1987). Hartley albino guinea-pigs (6 to 12 females) were given 10 intracutaneous induction doses of tilmicosin (0.05 to 0.1 ml of a 50 mg/ml solution). Fourteen days after the induction phase each animal was injected intracutaneously with 0.05 ml tilmicosin. This challenge dose did not result in an enhancement of skin reactions, suggesting that a skin sensitization response had not been elicited (Jordan et al., 1989b). 2.2.2 Short-term toxicity studies 2.2.2.1 Rats Groups of 20 male and 20 female Fischer-344 rats were given gavage doses of 0, 50, 175 or 600 mg/kg bw per day tilmicosin (purity 88%) in an aqueous vehicle. Drug administration was continued for 2 weeks, during which there was no mortality or clinical signs of toxicity. Food consumption was lower in males and females at 600 mg/kg and body weight gain was depressed in males throughout the study and in females during the first few days only. Table 1. Results of acute toxicity studies with tilmicosin Species Route Vehicle Sex LD503 Reference (strain) (mg/kg bw) Mouse sc aqueous M 97 Jordan (ICR) F 109 et al., 1986a Rat1 oral aqueous M 850 Jordan (Sprague- F 800 et al., 1986b Dawley) Rat2 oral aqueous M & F > 2000 Piroozi (Fischer-344) et al., 1993 Rat sc aqueous M 185 Jordan (Fischer-344) F 440 et al., 1986c Rat inhalation aerosol M & F > 494 (0/20) Jordan (Fischer-344) < 4053 (14/20) et al., 1987 Rabbit dermal - M & F > 5000 Jordan (NZ White) et al., 1987 Monkey im aqueous ? > 20 (0/2) Jordan & (Rhesus) 30 (1/1) Shoufler, 1990 Sheep sc aqueous ? > 150 (0/5) Cochrane & iv aqueous ? > 7.5 (1/5) Thomson, 1990 1 Animals were fasted 2 Animals were non-fasted 3 Figures in brackets represent the incidence of deaths In the 600 mg/kg bw per day groups, there were increases in haematocrit owing to an increase in corpuscular volume and in serum levels of alanine aminotransferase and hepatic p-nitroanisole O-demethylase activity. Thrombocyte counts were slightly decreased at this dose. Urinalysis was unaffected. At the highest dose, there were slight decreases in the weights of kidneys, spleen and ovaries, increased adrenal weight and multifocal inflammation in the liver of some animals. All treated animals exhibited caecal distension, which is a typical response to high doses of an antibiotic compound (Jordan, 1986). Groups of 20 male and 20 female Sprague Dawley (Crl:CD) rats received 0, 50, 250 or 1000 mg/kg bw per day tilmicosin (purity 88%) in an aqueous vehicle, by gavage for 3 months. Signs of overt toxicity were noted at 1000 mg/kg and included thinness, ventral soiling, chromorhinorrhea, chromodacryorrhea, alopecia and poor grooming. Mortality was increased at this highest dose and in females given 250 mg/kg bw per day. Although food consumption was depressed in the 1000 mg/kg bw per day group (males only), body weight gain was lower in males and females at 1000 mg/kg bw per day and females at 250 mg/kg bw per day. At 1000 mg/kg bw per day, serum alanine aminotransferase was increased in males, blood urea nitrogen (BUN) was increased in males and females, urinary pH was slightly lower in females and the presence of occult blood was greater in males and females. There were no effects on ophthalmology, haematology or hepatic p-nitroanisole O-demethylase activity. The weights of kidneys, liver and heart were increased in females at 1000 mg/kg bw per day and adrenal weight was increased at 250 mg/kg bw per day (females only) and 1000 mg/kg bw per day (males and females). Gross pathology revealed caecal enlargement or distension at 250 mg/kg bw per day or more and small spleens in a few rats at 1000 mg/kg bw per day. Slight nephrosis was noted in two males in each of the 250 and 1000 mg/kg bw per day groups. Other pathological alterations were seen only in males and females of the 1000 mg/kg bw per day group, i.e. hypertrophy of the zona fasciculata of the adrenal cortex in most rats, necrosis of individual skeletal muscle fibres in some rats; myocardial degeneration was increased and lymphoid depletion was evident in the spleen and thymus of some animals. The NOEL was 50 mg/kg bw per day (Jordan, 1988). 2.2.2.2 Dogs Beagle dogs (two males and two females per group) were exposed by inhalation to aerosols of 0, 12, 47 or 251 mg/m3 tilmicosin (purity 83%). The treatment was administered for 4 hours per day on 12 days out of a 16-day period (excluding weekends). Particle median equivalent aerodynamic diameters were between 1.2 and 1.5 µm. The mean serum concentrations of tilmicosin were 0.23 to 0.33 and 1.67 to 2.46 µg/ml at 47 and 251 mg/m3 respectively. Drug levels at 12 mg/m3 were below the detection limit of 0.1 µg/ml. One male given 251 mg/m3 died on the final day of exposure but no other overt signs of toxicity were observed. Heart rates were increased in dogs at 251 mg/m3. Food intake, body weight, haematology and blood chemistry were unaffected. At autopsy, lung weight was increased in females given 251 mg/m3 and inflammation was noted in the respiratory tract at 47 mg/m3 (females only) and 251 mg/m3 (males and females) (Jordan et al., 1991). Groups of four male and four female beagle dogs were given 0, 6, 20 or 70 mg/kg bw per day tilmicosin (purity 88%) in capsules for 3 months. The daily dose was administered in two equal amounts, 6 hours apart. Serum concentrations of tilmicosin were measured 3 hours and 24 hours after the first of the two daily doses in weeks 2, 3, 5, 9 and 13. At increasing doses, the mean concentrations were 0.1 to 0.2, 0.74 to 1.49 and 3.24 to 6.05 µg/ml at 3 hours and 0, 0.26 to 0.59 and 1.72 to 3.96 µg/ml at 24 hours. Half the 70 mg/kg bw per day males and females died during the first month. Clinical signs prior to death were pale mucous membranes in two dogs and ataxia in one dog. Food intake, body weight, haemato- logy and urinalysis were unaffected. Serum alanine aminotransferase activity was progressively increased at 70 mg/kg bw per day, while hepatic p-nitroanisole O-demethylase activity was increased in females at this level. Two of the four surviving dogs at 70 mg/kg bw per day showed bilateral multifocal areas of subretinal fluid concentrated along arterioles in the tapetal region of the eye. The changes were claimed to be consistent with those associated with systemic hypertension. One of these dogs also had retinal degeneration and the other showed miosis with normal pupillary light responses. Heart rate increases were dose related, being marked at 70 mg/kg bw per day and moderate to severe at 20 mg/kg bw per day. The increase in males given 6 mg/kg bw per day was not significant. At the highest dose, examination of the electrocardiogram revealed depression of the ST segment. At 70 mg/kg bw per day, heart weight was increased in males and females, and liver and kidney weights were increased in females. Gross necropsy showed small spleens in the females that died during the study and an enlarged heart in a surviving male at 70 mg/kg bw per day. Slight diffuse mucosal oedema was seen in the gall bladders of two dogs at 70 mg/kg bw per day. Despite the physiological changes in the eyes and heart, there were no associated pathological alterations. The NOEL was 6 mg/kg bw per day (Jordan, 1987). Groups of four male and four female beagle dogs were given 0, 4, 12 or 36 mg/kg bw per day tilmicosin (purity 86%) in capsules for 12 months. The daily dose was administered in two equal amounts, 6 hours apart. There were no deaths. Peripheral redness was seen sporadically in some animals of all groups, in particular at 12 and 36 mg/kg bw per day. Body weight gains were lower at > 12 mg/kg bw per day. There were no effects on ophthalmology, haematology, blood chemistry and urinalysis. Heart rates were markedly increased at 36 mg/kg bw per day with sporadic depression of the ST segment in some dogs. Heart weight was increased at 36 mg/kg bw per day and four males and one female at this dose showed enlarged hearts. Mild chronic dermatitis was noted in the external ears of dogs from all treated groups. The findings included minimal thickening of the epidermis, foci of acantholysis and inflammatory cell infiltration in the dermis. These changes were only slight and non-dose-related, and therefore of questionable relationship to treatment. The NOEL was 4 mg/kg bw per day (Jordan & Bernhard, 1989). 2.2.3 Long-term toxicity/carcinogenicity studies Tilmicosin has not been tested in toxicological studies longer than 12 months in duration and hence the carcinogenic potential of this drug has not been directly determined. There are a number of observations which are relevant in assessing the carcinogenicity of tilmicosin: a) The results of available toxicological studies with tilmicosin have not identified lesions or proliferative changes which could be considered suggestive of potential neoplasia. b) Tilmicosin has been tested in a wide range of genotoxicity assays. All results were negative and it was concluded that the compound has no genotoxic activity. c) Tilmicosin is a macrolide antibiotic. This class of chemical has been in widespread usage in humans for many years but there is no evidence of carcinogenicity. Tylosin is the closest structural analogue and this chemical was reviewed by the thirty-eighth meeting of JECFA (Annex 1, reference 97). 2.2.3.1 Reconsideration of tylosin tumorigenicity Tylosin was tested in 2-year feeding studies in rats. The findings revealed an association between drug administration at doses of 150 and 300 mg/kg bw per day in the diet and an increased incidence of pituitary adenomas in males. While it was claimed that the increase in the incidence of tumours was an indirect result of the ability of tylosin to increase survival and weight gain, supporting data were not available to the Committee and an ADI was not established. New information, not considered at the thirty-eighth meeting, indicates that spontaneous pituitary tumours occur in male rats at variable rates with increased rates occurring in animals with higher body weights (Gries & Young, 1982). In the tylosin studies, 12-month body weights were somewhat higher in treated males rats and mortality was increased in control animals due to respiratory infection. The highest observed incidence of tumours in tylosin-treated groups was comparable to the upper limit of the historical control range (23%) in the test facility. 2.2.4 Reproductive toxicity studies 2.2.4.1 Rats A dose-ranging study was carried out in groups of 10 female Sprague-Dawley (Crl:COBS CD) rats given gavage doses of 0, 50, 125, 250, 500 or 750 mg/kg bw per day tilmicosin (purity unknown). The females were treated from 14 days before mating with untreated males until the end of study on post-partum day 4. Excess salivation was dose-related at > 250 mg/kg bw per day. Chromodacryorrhea, urine-stained fur and alopecia were seen in some rats at 750 mg/kg bw per day; the three most severely affected died during the study. Prior to death, these animals exhibited reduced food intake, lost weight and were emaciated. Body weight gain was depressed in surviving rats at 750 mg/kg bw per day during the pre-mating period while food intake was reduced at > 250 mg/kg bw per day in week 1 and at 750 mg/kg bw per day in week 2. The pregnancy rate was decreased at > 500 mg/kg bw per day. Duration of gestation, litter size and weight, pup survival and weight gain to post-partum day 4 were unaffected (Dearlove et al., 1987). Groups of 30 male and 30 female Sprague Dawley (Crl: COBS CD BR) rats were administered 0, 10, 45 or 200 mg/kg bw per day tilmicosin (purity 87%) by gavage in an aqueous vehicle. Treatment commenced 70 days (males) and 14 days (females) before the first mating period and was continued through two litters per generation for two generations. F1 litters were culled to five pups per sex on post-partum day 4 and F1b pups (40 males and 40 females per group) were bred to produce the following generation. F2a and F2b pups were killed on post-partum day 4. In adult animals, salivation was noted in males and females at 200 mg/kg bw per day, but there were no other signs of toxicity. Body weight gain and food consumption were depressed in females of the 45 and 200 mg/kg bw per day groups during the pre-mating period only. During the production of the four litters in this study there were no effects on mating performance, pregnancy rates, duration of gestation, litter size and weight and the weight gain of offspring. In both F1 litters at 200 mg/kg bw per day, pup mortality was slightly increased up to post-partum day 4, but the finding was not duplicated in either F2 litter. The NOEL was 10 mg/kg bw per day in adult rats (Christian & Hoberman, 1989). 2.2.5 Special studies on embryotoxicity and teratogenicity 2.2.5.1 Rats Groups of 25 presumed pregnant female Sprague Dawley (Crl: CD) rats were administered gavage doses of 0, 10, 70 or 500 mg/kg bw per day tilmicosin (purity 86%) in an aqueous vehicle. The dams were treated on gestation days 6 to 15 and were killed on gestation day 20. Increased salivation was seen at 70 and 500 mg/kg bw per day and alopecia at 500 mg/kg bw per day. There were no deaths or abortions. Body weight gain was reduced at 70 and 500 mg/kg bw per day, and food intake was reduced at 500 mg/kg bw per day, during gestation days 6 to 10. The number of resorption or live fetuses, fetal weight, sex ratio and the incidence of fetal malformations were similar between groups. The incidences of total skeletal and visceral anomalies were increased in treated groups, but there was no dose-response relationship and the findings were within the historical control values for the laboratory. The NOEL for maternotoxicity was 10 mg/kg bw per day (Jordan & Higdon, 1988). 2.2.5.2 Rabbits Groups of 15 presumed pregnant female Japanese White-NIBS rabbits were given gavage doses of 0, 8, 19 or 48 mg/kg bw per day tilmicosin (purity unknown) in an aqueous vehicle. Does were treated on gestation days 6 to 18 and were killed on gestation day 28. One female given 48 mg/kg bw per day aborted on gestation day 26 and died. Reduced faeces were seen at 19 and 48 mg/kg bw per day with only a transient effect at 8 mg/kg bw per day. During the treatment period food intake was depressed in a dose-related manner and body weight loss was observed at 19 and 48 mg/kg bw per day. Fetal and placental weight tended to decrease at 19 and 48 mg/kg bw per day but did not achieve statistical significance. There were no meaningful effects on the incidence of resorptions or fetal deaths or on sex ratio. Open eyelids were observed in 11/91 and 16/68 fetuses from the 19 and 48 mg/kg bw per day groups, respectively, and some of these fetuses showed cleft palate or club foot. The affected fetuses had low body weights and the seven litters involved were derived from does that had lost body weight during drug administration. Skeletal examination revealed retardation of fetal development at 19 and 48 mg/kg bw per day. Similar effects have been seen in this laboratory in dietary restricted rabbits, suggesting the effects on the fetus were secondary to maternal malnutrition (Noda, 1993). 2.2.6 Special studies on genotoxicity Table 2. Results of genotoxicity studies on tilmicosin Test system1 Test object Concentration Results Reference Reverse S. typhimurium 1 - 100 µg/plate negative Jordan mutation2 TA98, TA100, (± S9) et al., 1986f TA1535, TA1537, TA1538 Reverse E. coli 1 - 100 µg/plate negative Garriott mutation2 WP2uvrA (± S9) et al., 1993 Forward L5178Y mouse 100-900 µg/ml negative Jordan mutation2 lymphoma cells (- S9) et al., 1986e 200-1000 µg/ml (+ S9) Forward HGPRT+ Chinese 25-250 µg/ml negative Jordan mutation2 Hamster ovary (- S9) et al., 1989c cells 50-300/ µg/ml (+ S9) Unscheduled primary cultures 0.5-10 µg/ml negative Jordan DNA synthesis of rat hepatocytes et al., 1985 assay Sister chromatid Chinese hamster 200-1800 × 1 negative Jordan et al., exchange bone marrow mg/kg bw oral 1986d, 1989a assay Chromosome rat bone marrow 180-1800 × 1 and negative Jordan & aberrations 100-1000 × 5, Ivett, 1989 mg/kg bw per day oral 1 Positive controls used 2 Both with and without liver microsomal activation 2.2.7 Special study on the immune system Groups of eight male CD-1 mice were given gavage doses of 0, 10, 250, 500 or 1000 mg/kg bw per day tilmicosin (purity 87%) in an aqueous vehicle. Drug treatment was continued for 10 days. After the third dose mice were injected intravenously with sheep red blood cells. At the end of the study, serum from each mouse was assayed for antibodies (haemagglutinin). There was one death at 500 mg/kg bw per day and six at 1000 mg/kg bw per day, but antibody production was not affected at any level (McGrath et al., 1988a). 2.2.8 Special studies on microbiological activity 2.2.8.1 In vitro The antibacterial activity of tilmicosin was determined against a range of organisms representative of human intestinal flora. Cultures were initiated using inoculum sizes of between 3 × 105 and 1.6 × 106 cells per spot on blood agar plates and incubated anaerobically at 37°C. The median MIC values for the clinical isolates of Bifidobacterium and Peptostreptococcus, respectively, were 0.015 and 0.5 µg/ml. The above results were obtained at pH 7.7. At pH 6.6 the MIC values were one to two orders of magnitude higher (Scott et al., 1993). The antibacterial activity of tilmicosin was examined against a number of organisms used in industrial food processing and originally obtained from dairy products. Cultures were initiated in blood agar plates using three strains of Propionibacterium and four strains of Lactobacillus. Under anaerobic conditions the MICs were between 8 and 64 µg/ml and under microaerophilic conditions the values were between 4 and 32 µg/ml (McLaren, 1994). 2.2.8.2 Rats In two separate studies, female germ-free rats were orally dosed with 1 ml of 10% (w/v) pooled human faecal suspension. Three weeks later groups of two males and two females were given gavage doses of 0, 0.12 or 0.4 mg/kg bw per day tilmicosin (purity 87%) for 5 days. Rat faecal samples were collected before treatment, daily during treatment and once during each of the 2 weeks following cessation of dosing. Body weight gain remained unaffected. The animals in each study received faecal suspensions obtained from different donors. Results from different studies varied widely, possibly reflecting differences between the bacterial populations used. Total anaerobes were not reduced by tilmicosin treatment. Total enterobacterial counts and the proportion of enterobacteria with respect to total anaerobe counts were transiently increased at 0.4 mg/kg bw per day in one study only. Tilmicosin-resistant enterobacteria were not significantly increased in either study. Spiramycin, at a dose of 0.5 mg/kg bw per day, increased total enterobacterial counts and the number of spiramycin-resistant enterobacteria; the latter appeared to remain high after the cessation of treatment. The NOEL for tilmicosin was 0.4 mg/kg bw per day (Rumney, 1993). 2.2.9 Special studies on pharmacology Table 3. Results of pharmacological assays with tilmicosin Test system Doses Results Reference Isolated 0.0009 to No effect on non-stimulated organ. Williams guinea-pig 90 µg/ml 90 µg/ml slightly inhibited acetylcholine- et al., ileum and angiotensin-induced contraction 1988 and significantly inhibited electrically stimulated contraction Isolated 0.0009 to No effect on non-stimulated tissue and Williams rat uterus 90 µg/ml no change to oxytocin-induced et al., (estrogen contractions 1988 primed) Isolated rat 0.0009 to No effect on non-stimulated tissue and Williams vas deferens 90 µg/ml no change to noradrenaline-induced et al., contractions 1988 Isolated 0.0009 to In spontaneously beating tissue, > 90 Williams guinea-pig 900 µg/ml µg/ml decreased force of contraction; et al., atria and 900 µg/ml increased rate of 1988; contraction. 90 µg/ml inhibited Jordan isoprenaline-, noradrenaline- and Bay et al., K8644 (calcium agonist)-induced force 1990 and rate of contraction, and histamine-induced rate of contraction. Table 3. Results of pharmacological assays with tilmicosin (cont'd). Test system Doses Results Reference Conscious 0.25, 1, 2.5 Heart rate increased at > 1 mg/kg. Left Jordan & dogs or 5 mg/kg ventricular function decreased at > 0.25 Sarazan, iv mg/kg. Aortic pulse pressure decreased 1991; at > 1 mg/kg. ECG revealed "Ventricular Sarazan Alternans" (ventricular contraction fails et al., to achieve adequate pressure to open 1993 aortic valve and cause an arterial pulse). Anaesthetised 0.5, 1 or 5 Heart rate increased, stroke volume, Jordan dogs mg/kg iv stroke work index and cardiac output et al., decreased at > 1 mg/kg. At 5 mg/kg 2/3 1988 dogs developed second degree heart block CD-1 mice 10, 100, Piloerection and grasping loss at > 500 Jordan 500 or mg/kg. Ptosis at 1000 mg/kg. No effect et al., 1000 mg/kg on electroshock- or pentylenetetrazol- 1989d oral induced seizures or on body temperature. Hexobarbital-induced sleep time prolonged by 500 (x1) and 1000 (x3) mg/kg Sprague- 10, 30, 90 Urine volume and creatinine reduced McGrath Dawley or 270 at 270 mg/kg with increases in osmolality et al., rats mg/kg oral and electrolytes. 1988b 2.3 Observations in humans A total of 241 human exposures to tilmicosin (Micotil) were reported to the Rocky Mountain Poison Center from May 1992 to May 1993. Needlesticks and scrapes (n=112) and accidental injection (n=43) caused either no effect or local reactions including soreness, numbness, stinging, swelling, redness, burning and stiffness. Some injected subjects experienced anxiety, sweating, headache and lightheadedness. Skin exposures (n=50) resulted in redness and tingling of the skin, and eye exposures (n=11) resulted in stinging and swelling. Persons accidentally ingesting the drug (n=39) reported either no symptoms or bitter taste, nausea, numbness of lips and tongue, vomiting, thirst and headache (Montanio & Dart, 1993). Over a 30-month period, 36 cases of accidental exposure to tilmicosin (Micotil) were reported to the Ontario Regional Poison Information Centre. Percutaneous injection (n=26) always resulted in pain at the site and seven subjects mentioned a variety of local reactions consistent with an irritant action. One person showed "peaked T waves" 30 minutes following the injection of 1 ml into his arm, but ECG changes were not noted in other subjects. The remaining subjects received splashes into the mouth or eyes or onto the skin. Unpleasant taste, a burning sensation on the hard palate and ocular irritation were each recorded in one person (McGuigan, 1994). 3. COMMENTS The Committee considered toxicological data on tilmicosin, including the results of studies on acute and short-term toxicity, pharmacokinetics, metabolism, reproductive toxicity, teratogenicity, genotoxicity, antimicrobial activity and pharmacology. The Committee also considered observations in humans accidentally exposed to tilmicosin. Tilmicosin is absorbed from the gastrointestinal tract as shown by the recovery of radiolabelled compound in urine and/or bile of orally dosed pigs (110 to 400 mg per animal), and the presence of dose-related serum concentrations of tilmicosin dosed orally in dogs for 3 months. However, the results from available studies did not allow any conclusion to be reached concerning the extent of absorption. The metabolites detected in a range of farm animals were also found in rats, which suggests that the rat is a suitable model for determining the potential toxicological hazards posed by tilmicosin. The LD50 in fasted rats was 800 to 850 mg/kg bw, but toxicity was substantially lower in non-fasted animals, among which there were no deaths following administration of a single dose of 2000 mg tilmicosin/kg bw. Studies in a range of pharmacological models identified depression of cardiac muscle contractility and reduced heart function as the main adverse effects. Rats were administered oral doses of 50, 250 or 1000 mg/kg bw per day for 3 months. At 1000 mg/kg bw per day, animals exhibited chromorhinorrhea, chromodacryorrhea, alopecia, poor grooming, reduced food consumption and they appeared thin. Body-weight gain was reduced and mortality was increased in females at 250 mg/kg bw per day and in both sexes at 1000 mg/kg bw per day. Toxic effects on the kidney and liver were indicated by increased organ weights, increased serum levels of alanine aminotransferase and blood urea nitrogen, and the presence of blood in the urine. However, pathological examination of these organs showed only slight nephrosis in two males in each of the groups given 250 or 1000 mg/kg bw per day. At the highest dose, hypertrophy of the zona fasciculata of the adrenal cortex was noted in most rats, and myocardial degeneration, necrosis of individual skeletal muscle fibres and lymphoid depletion in the spleen and thymus were seen in some rats. The NOEL was 50 mg/kg bw per day. Dogs were given oral doses of 6, 20 or 70 mg/kg bw per day for three months. Half of the animals given 70 mg/kg bw per day died during the first month. Heart rate was increased at 20 and 70 mg/kg bw per day and at the higher dose there was depression of the ST segment of the electrocardiogram. Ophthalmoscopic examination of the eyes showed bilateral areas of subretinal fluid concentrated along arterioles in the tapetal region of two of the four surviving dogs at 70 mg/kg bw per day. The NOEL was 6 mg/kg bw per day. Dogs were given oral doses of 4, 12 or 36 mg/kg bw per day for twelve months. Body weight gain was depressed at 12 and 36 mg/kg bw per day. Heart rate was markedly increased at 36 mg/kg bw per day, with occasional depression of the ST segment of the electrocardiogram. Hearts were enlarged at 36 mg/kg bw per day, but there were no associated pathological changes. The NOEL was 4 mg/kg bw per day. In a two-generation reproductive toxicity study, rats were administered oral doses of 10, 45 or 200 mg tilmicosin/kg bw per day. Body weight gain and food consumption were depressed in females given 45 or 200 mg/kg bw per day, but only during the pre-mating period. Fertility and reproduction parameters were unaffected at any dose level. At 200 mg/kg bw per day, mortality in pups was slightly increased in both first-generation litters up to post-partum day 4, but not in either second-generation litter. The NOEL was 10 mg/kg bw per day. Developmental toxicity studies were reported in rats and rabbits. Rats were dosed with 10, 70 or 500 mg tilmicosin/kg bw per day by gavage. Growth and development in rat fetuses were not affected by treatment, but increased salivation and reduced body weight gain of dams were observed at 70 and 500 mg/kg bw per day. The NOEL for maternal toxicity in rats was 10 mg/kg bw per day. In the study in rabbits, there were dose-related signs of toxicity in the does at all doses (8, 19 and 48 mg/kg bw per day). Severely affected members of the groups given 19 or 48 mg/kg bw per day produced offspring that had open eyelids and low incidences of cleft palate or club foot. These fetuses had low body weights and were clearly retarded in development. The effects were attributed to treatment-related malnutrition in maternal animals, which is commonly observed in rabbits dosed with antibiotics, confirming that this species is an inappropriate model for studying the teratogenic potential of antibiotics. Tilmicosin has been tested for reverse mutation in bacteria, forward mutation in cultured mammalian cells, unscheduled DNA synthesis in primary cultures of rat hepatocytes, and in in vivo cytogenetic assays. All results were negative, and the Committee concluded that tilmicosin has no genotoxic potential. The carcinogenic potential of tilmicosin has not been tested. However, a number of factors are relevant in assessing the carcinogenicity of this drug. Toxicity studies with tilmicosin have not resulted in lesions or proliferative changes suggestive of neoplasia, and tilmicosin was uniformly negative in a wide range of genotoxicity assays. Tilmicosin is a macrolide antibiotic, and this class of chemicals is not known to induce neoplasia despite widespread use in humans over many years. The closest structural analogue, tylosin, was reviewed at the thirty-eighth meeting of the Committee (Annex 1, reference 97). In a 2-year feeding study in rats, tylosin administration was associated with an increased incidence of pituitary adenomas in male animals when compared to concurrent controls. New evidence, not considered at the thirty-eighth meeting, indicates that spontaneous pituitary neoplasms occur in male rats at variable rates. Additionally, increased rates occur in animals with higher body weights. In tylosin-treated groups of male rats, the 12-month body weights were somewhat higher than in the control groups and the incidences of pituitary adenomas were comparable to the upper limit of the historical control range. The lower incidence of pituitary neoplasms in the control animals may have been due to the earlier mortality in this group caused by respiratory disease. In light of this information the Committee considered that the concerns of the thirty-eighth meeting over the potential tumorigenicity of tylosin had been satisfactorily addressed and that there was no concern for the carcinogenic potential of tylosin. For the above reasons, the Committee considered that carcinogenicity studies would not be required for tilmicosin. In assessing the microbiological activity of tilmicosin, the results of a study using germ-free rats colonized with human intestinal microflora was considered the most relevant. At the highest dose administered (0.4 mg/kg bw per day for 5 days) there were no significant alterations in numbers of total anaerobes or enterobacteria in rat faeces. Reports of accidental human exposure to tilmicosin have identified local reactions indicative of an irritant action following dermal and ocular exposure. Humans accidentally injected with tilmicosin have reported anxiety, sweating, headache and lightheadedness. Changes in the electrocardiogram pattern were observed in only one person. Contact with the buccal mucosa or ingestion has resulted in a range of symptoms including nausea, vomiting, thirst, numbness or burning sensation in the mouth, and headache. 4. EVALUATION The NOEL from toxicological studies was 4 mg/kg bw per day in a 12-month study in dogs. Treatment of rats colonized with human intestinal microflora with 0.4 mg tilmicosin/kg bw per day produced no significant microbiological effect. The Committee established an ADI of 0-40 µg/kg bw, based on the toxicological NOEL of 4 mg/kg bw per day and a safety factor of 100. An identical ADI would have been established using the data from the study on rats colonized with human intestinal microflora and a safety factor of 10 to account for variability among humans. 5. REFERENCE Christian, M.S. & Hoberman, A.M. (1989). Reproductive effects of EL-870 administered orally via gavage to Crl:COBS CD(SD) BR rats for two generations, with two litters per generation. Unpublished study No. 112-001 from Argus Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Cochrane, R.L. & Thomson, T.D. (1990). Toxicology and pharmacology of tilmicosin following administration of subcutaneous and intravenous injections to sheep. Unpublished study No. T5C768908 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Dearlove, G.H., Hoberman, A.M., & Christian, M.S. (1987). Dosage-range study of EL-870 administered orally via gavage to Crl:COBS CD(SD) BR rats (Pilot study). Unpublished study No. 112-001P from Argus Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Donoho, A.L. (1988). Comparative metabolism of 14C-tilmicosin in cattle and rats. Unpublished study No. ABC-0395 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Donoho, A.L. & Kennington, A.S. (1993). Tilmicosin metabolite study with rat excreta. Unpublished study No. T5C759302 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Donoho, A.L. & Thomson, T.D. (1988). 14C-Tilmicosin balance- excretion study in swine. Unpublished study No. ABC-0409 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Donoho, A.L., Darby, J.M., Helton, S.L., Sweeney, D.J., Occolowitz, J.L., & Dorman, D.E. (1993). Tilmicosin metabolism study in tissues and excreta of pigs fed 400 ppm 14C-tilmicosin. Unpublished study No. T5C759201 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Garriott, M.L., Rexroat, M.A., & Jordan, W.H. (1993). The effect of tilmicosin on the induction of reverse mutations in Escherichia coli using the Ames test. Unpublished study No. 920825AMS2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Giera, D.D. & Thomson, T.D. (1986). Preliminary 14C EL-870 balance excretion and tissue residue in swine. Unpublished study No. ABC-0305 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Gries, C.L. & Young, S.S. (1982). Positive correlation of body weight with pituitary tumor incidence in rats. Fundam. Appl. Toxicol., 2, 145-148. Hawkins, D.R., Elsom, L.F., Dighton, M.H., Kaur, A,. & Cameron, D.M. (1993). The metabolism and residues of 14C-tilm- icosin following subcutaneous administration to sheep. Unpublished study No. HRC/LLY 36/930447 from Huntingdon Research Centre. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. (1986). The toxicity of compound 177370 (EL-870) given by oral gavage to Fischer 344 rats for two weeks. Unpublished study No. RI5585 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. (1987). The toxicity of EL-870 given orally to Beagle dogs for three months. Unpublished study No. DO8286 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. (1988). The toxicity of tilmicosin given orally to Crl:CD(SD) rats for three months. Unpublished study No. RO9886 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. & Bernhard, N.R. (1989). A one year chronic toxicity study in Beagle dogs given oral doses of tilmicosin. Unpublished study No. DO7187 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. & Higdon, G.L. (1988). A teratology study of tilmicosin (EL-870, compound 177370) administered orally to CD rats. Unpublished study No. RI3387 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. & Ivett, J.L. (1989). Mutagenicity test on tilmicosin in the rat bone marrow cytogenetic assay. Unpublished study No. 10646-0-452 from Hazleton Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. & Sarazan, R.D. (1991). An acute study of the cardiovascular effects of intravenous Micotil 300 in conscious dogs. Unpublished study No. DV0890 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H. & Shoufler, J.R. (1990). The acute toxicity of Micotil 300 administered intramuscularly to Rhesus monkeys. Unpublished studies Nos. PO4089 and PO7689 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Hill, L.E., & Probst, G.S. (1985). The effect of compound 177370 (EL-870) on the induction of DNA repair synthesis in primary cultures of adult rat hepatocytes. Unpublished studies Nos. 851008UDS2449 and 851015UDS2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., McKinley, E.R., Brown, G.E., & Hawkins, D.R. (1986a). The acute toxicity of compound 177370 (EL-870) administered subcutaneously to the ICR mouse. Unpublished studies Nos. M-C-41-85 and M-C-40-85 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., McKinley, E.R., Brown, G.E., & Hawkins, D.R. (1986b). The acute toxicity of compound 177370 (EL-870) administered orally to the Sprague-Dawley rat. Unpublished studies Nos. R-O-40-86 and R-O-39-86 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., McKinley, E.R., Brown, G.E., & Hawkins, D.R. (1986c). The acute toxicity of compound 177370 (EL-870) administered subcutaneously to the Fischer 344 rat. Unpublished studies Nos. R-C-02-86 and R-C-01-86 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Neal, S.B., & Probst, G.S. (1986d). The effect of compound 177370 (EL-870) on the in vivo induction of sister chromatid exchange in bone marrow of Chinese hamsters. Unpublished study No. 851014SCE2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Oberly, T.J., Bewsey, B.J., & Probst, G.S. (1986e). The effect of compound 177370 (EL-870) on the induction of forward mutation at the thymidine kinase locus of L5178Y mouse lymphoma cells. Unpublished studies Nos. 851106MLA2449 and 851113MLA2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Rexroat, M.A., & Probst,G.S. (1986f). The effect of compound 177370 (EL-870) on the induction of reverse mutations in Salmonella typhimurium using the Ames test. Unpublished studies Nos. 850930AMS2449, 851028AMS2449 and 851111AMS2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Markey, T.F., Oakley, L.M., & Torrence, T.L. (1987). The acute dermal and inhalation toxicity and ocular and dermal irritation of tilmicosin technical. Unpublished studies Nos. B-D-45-86, B-E-39-86 and R-H-037-86 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Williams, P.D., & Turk, J.A. (1988). Cardiovascular effects of tilmicosin administered intravenously in anaesthetised beagle dogs. Unpublished study No. PC8806 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Brunny, J.D., & Garriott, M.L. (1989a). The effect of tilmicosin on the in vivo induction of sister chromatid exchange in bone marrow of Chinese hamsters. Unpublished study No. 881114SCE2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Gardner, J.B., & Weaver, D.E. (1989b). An intracutaneous sensitisation study in albino guinea pigs with tilmicosin. Unpublished study No. GO1888 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Richardson, K.K., & Oberly, T.J. (1989c). The effect of tilmicosin on the induction of forward mutation at the HGPRT+ locus of Chinese hamster ovary cells. Unpublished studies Nos. 881130CHT2449 and 890111CHO2449 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Williams, P.D., & Helton, D.R. (1989d). CNS behavioural effects of tilmicosin administered orally in the male CD-1 mouse. Unpublished study No. PN8805 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Williams, P.D., & Colbert, W.E. (1990). In vitro studies of tilmicosin in the cardiac muscle of Hartley Albino guinea pigs. Unpublished study No. PM8946 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Jordan, W.H., Wolff, R.K., & Carlson, K.H. (1991). A subchronic inhalation toxicity study of tilmicosin in Beagle dogs. Unpublished study No. DO5589 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. McGrath, J.P., Hamelink, J.L., & Lochmueller, C.A. (1988a). A study of the immune response in CD-1 mice treated orally with tilmicosin. Unpublished study No. MI4288 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. McGrath, J.P., Hamelink, J.L,. & Stephenson, R.O. (1988b). A study of the acute effects of urine and electrolyte excretion of tilmicosin administered orally to female Crl:CD(SD) rats. Unpublished study No. RI8688 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. McGuigan, M.A. (1994). Human exposures to tilmicosin (Micotil). Vet. Hum. Toxicol., 36(4), 306-308. McLaren, I.M. (1994). Determination of the minimum inhibitory concentration of tilmicosin for Lactobacillus and Propionibacterium Sp. Unpublished study from Central Veterinary Laboratory, UK. Submitted to WHO by Lilly, Basingstoke, UK. Montanio, C.D. & Dart, R.C. (1993). Micotil 300. Human exposures May 1992-May 1993. Unpublished report. Submitted to WHO by Lilly, Basingstoke, UK. Noda, A. (1993). Teratogenicity study of EL-870 (tilmicosin aqueous) in rabbits by gavage. Unpublished study No. 91-001 from Research Institute for Animal Science in Biochemistry and Toxicology, Japan. Submitted to WHO by Lilly, Basingstoke, UK. Piroozi, K.S., Keaton, M.J., & Jordan, W.H. (1993). The acute toxicity of tilmicosin administered orally to Fischer 344 rats. Unpublished study No. R21493 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Rumney, C.J. (1993). Microbiological end-point determination for two antibiotics. Unpublished study No. 1164/3/93 from Bibra Toxicology International, UK. Submitted to WHO by Lilly, Basingstoke, UK. Sarazan, R.D., Main, B.W., & Jordan, W.H. (1993). Cardiovascular effects of tilmicosin alone, or in combination with propranolol or dobutamine, in conscious unrestrained dogs. Unpublished study No. DV1591 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK. Scott, R.J.D., Morgan, J.M., Pether, J.V.S., & Gosling, P. (1993). Determination of the minimum inhibitory concentrations of tilmicosin for human isolates of Bifidobacterium and Pepto- streptococcus. Unpublished study No. SMS/9301 from Southern Microbiological Services, UK. Submitted to WHO by Lilly, Basingstoke, UK. Williams, P.D., Jordan, W.H., & Colbert, W.E. (1988). In vitro studies of tilmicosin (EL-870, Compound 177370) in smooth and cardiac muscle. Unpublished study No. PM8808 from Lilly Research Laboratories. Submitted to WHO by Lilly, Basingstoke, UK.
See Also: Toxicological Abbreviations TILMICOSIN (JECFA Evaluation)