White snakeroot poisoning in goats: Variations in toxicity with different plant chemotypes.

Tremetone and possibly other benzofuran ketones are believed to be the toxic compounds in white snakeroot. However, disease has not been reproduced with purified toxins and the concentrations of the benzofuran ketones in white snakeroot populations that cause toxicosis have not been documented. The objectives of this study were to compare the toxicity of seven plant populations, better characterize the clinical and pathologic changes of poisoning, and correlate intoxication with benzofuran ketone content. Four of the seven white snakeroot collections were toxic at the dose and duration used in the study. Affected goats became exercise intolerant, had significant serum enzyme changes and histological lesions in the large appendicular muscles. The incidence and severity of poisoning was not correlated with total doses of tremetone or total benzofuran ketone concentrations suggesting they may not be closely involved in producing toxicity and the possible involvement of an unidentified toxin. The results also demonstrate that white snakeroot populations vary chemically and toxicologically.

Rumen Microorganisms Decrease Bioavailability of Inorganic Selenium Supplements.

Despite the availability of selenium (Se)-enriched trace mineral supplements, we have observed low Se status in cattle and sheep offered traditional inorganic Se supplements. Reasons for this may include inadequate intake or low bioavailability of inorganic Se sources. The objective of this study was to determine whether rumen microorganisms (RMO) alter the bioavailability of Se sources commonly used in Se supplements. Rumen microorganisms were isolated from ewes (n = 4) and incubated ex vivo with no Se (control), with inorganic Na selenite or Na selenate, or with organic selenomethionine (SeMet). Total Se incorporated into RMO and the amount of elemental Se formed were determined under equivalent conditions. Incorporation of Se from Na selenite, Na selenate, or SeMet into RMO was measured as fold change compared with control (no added Se). Incorporation of Se into microbial mass was greater for SeMet (13.2-fold greater than no-Se control) compared with inorganic Se supplements (P = 0.02); no differences were observed between inorganic Na selenate (3.3-fold greater than no-Se control) and Na selenite (3.5-fold greater than no-Se control; P = 0.97). Formation of non-bioavailable, elemental Se was less for RMO incubated with SeMet compared with inorganic Se sources (P = 0.01); no differences were observed between Na selenate and Na selenite (P = 0.09). The clinical importance of these results is that the oral bioavailability of organic SeMet should be greater compared with inorganic Se sources because of greater RMO incorporation of Se and decreased formation of elemental Se by RMO.

Elk (Cervus Canadensis) preference for feeds varying in selenium concentration.

Selenium-accumulator plants are reputed to be unpalatable to large ungulates. Elk (Cervus canadensis) populations in southeastern Idaho overlap with populations of Se-rich plants, but there is no information on the influence of plant Se concentration on elk dietary preferences. The objective of this study was to determine, under controlled conditions, the preference of elk for feeds varying in Se concentrations. Seven yearling female elk (128 ± 5 kg) were purchased from a commercial elk farm in southeastern Idaho and adapted to low-Se alfalfa pellets. Three feeding trials using pellets with predetermined Se concentrations were conducted. Alfalfa pellets were commercially made with the addition of Symphyotrichum ascendens (western aster) so that the pellets contained 0.4, 5, 20, 50, or 100 mg/kg (DM basis) Se. In trial 1, 5 Se-containing alfalfa pellets (0.4, 5, 20, 50, and 100 mg/kg Se) were offered for 10 d; trial 2 used 4 Se-containing alfalfa pellet choices (0.4, 20, 50, and 100 mg/kg), and trial 3 used 3 pellet choices (0.4, 50, and 100 mg/kg) for 6 d. In trial 1, consumption of the control pellets by elk was greater than each of the other pellet choices (P < 0.001). Similarly, consumption of the 5-mg/kg Se pellet differed from control pellet and all other Se-containing pellets (P < 0.0001). There were no differences (P > 0.50) in consumption of the 20-, 50-, or 100-mg/kg Se pellets. In trial 2, elk consumed more (P < 0.0001) of the control pellet than the 20-, 50-, and 100-mg/kg Se pellets. Similarly, elk consumed more (P < 0.0001) of the 20-mg/kg Se pellet than the 50- and 100-mg/kg Se pellets. There were no differences (P > 0.99) in elk consumption of the 50- and 100-mg/kg Se pellets. In trial 3, elk consumption of the control and 50- and 100-mg/kg Se pellets differed (P ≤ 0.03) from one another each day except that on d 1 and 2, where elk consumption of the 50- and 100-mg/kg Se pellets did not differ (P ≥ 0.32). Elk clearly discriminated against pellets with the highest Se concentrations when they were given pellets with differing Se concentrations. These results suggest that elk are not likely to select forages with high Se concentrations, particularly when high-Se plants are present in a rangeland situation with numerous other forage choices.

Evaluation of the respiratory elimination kinetics of selenate and Se-methylselenocysteine after oral administration in lambs.

Sheep can be acutely poisoned by selenium (Se) accumulating forages which often contain selenate or Se-methylselenocysteine as their predominant forms. Excess Se can be eliminated via respiration. Sheep were given a single oral dose of 0, 1, 2, 3, 4, or 6 mg Se/kg BW as sodium selenate and Se-methylselenocysteine or 6 mg Se/kg BW as sodium selenite or selenomethionine. Expired air samples were collected and analyzed for Se. The Se concentration of the expired air reflected a dose-dependent increase at individual time points for both Se-methylselenocysteine and sodium selenate, however, Se content was greater and eliminated more rapidly from sheep receiving Se-methylselenocysteine. The mean Se concentration in respired air from sheep administered 6 mg Se/kg BW of different selenocompounds was greatest in sheep dosed Se-methylselenocysteine > selenomethionine > sodium selenate > sodium selenite. The Se concentration in respired air of acutely poisoned sheep is significantly different for different chemical forms of Se.

Effect of selenium concentration on feed preferences by cattle and sheep.

Selenium-accumulator plants are reputed to be unpalatable to livestock. The objective of this study was to determine if sheep and cattle could discriminate between forages and feeds with different concentrations of Se. In the first study, cattle and sheep preferences for intermediate wheatgrass (Thinopyrum intermedium), alfalfa (Medicago sativa), and western aster (Symphyotrichum ascendens) of varying Se concentrations were assessed. The Se concentrations ranged from 0.8 to 50 mg/kg (DM) in grass, 1.4 to 275 mg/kg in alfalfa, and 4 to 4,455 mg/kg in aster. Selenium concentration had no influence (P > 0.05) on the initial or subsequent preferences of sheep or cattle for grass or alfalfa. Cattle developed an aversion to aster after consuming 95% of the plant material during the first brief exposure and subsequently refused to eat any aster. Sheep consumption of aster was variable, but their preference was not driven by Se concentration. In the next study, cattle and sheep were offered pellets at 1.5% of BW (as fed) that contained increasing concentrations of Se from aster (control and 5, 25, 45, and 110 mg/kg Se). In trial 1, all pellets were offered. In Trials 2 and 3, all pellets were offered with the exception of the 5 mg/kg Se pellet and the 5 and 25 mg/kg Se pellets, respectively. In trial 1, consumption of the control pellet by cattle was greater on all days compared with other Se pellets (P < 0.001). Cattle ate more (P < 0.001) of the 5 mg/kg Se pellet than the higher Se pellets on d 3, 4, and 5. Sheep ate greater amounts of the control and 5 and 110 mg/kg Se pellets compared with the 25 and 45 mg/kg Se pellets (P < 0.0001) on d 1, and sheep consumed primarily the control and 5 mg/kg Se pellets thereafter. In trial 2, cattle and sheep consumed more (P < 0.0001) of the control Se pellet than the 25, 45, and 110 mg/kg Se pellets. In trial 3, cattle consumption of the control and 45 and 110 mg/kg Se pellets differed on d 2 and 3 (P < 0.001), except there was no difference (P > 0.95) in cattle consumption of the control and 45 mg/kg Se pellets on d 1. Sheep consumed primarily the control and 45 mg/kg Se pellets. We conclude that high Se concentrations in fresh forages had no effect on initial consumption by cattle or sheep. When given Se pellets, initial responses were variable, but the results indicate that cattle and sheep adjusted their intake over time to avoid excessive intake of Se.

Comparative oral dose toxicokinetics of selenium compounds commonly found in selenium accumulator plants.

Consumption of Se accumulator plants by livestock can result in Se intoxication. Recent research indicates that the Se forms most common in Se accumulator plants are selenate and Se-methylselenocysteine (MeSeCys). In this study the absorption, distribution, and elimination kinetics of Se in serum and whole blood of lambs dosed with a single oral dose of (1, 2, 3, or 4 mg Se/kg BW) of sodium selenate or MeSeCys were determined. The Se concentrations in serum and whole blood for both chemical forms of Se followed simple dose-dependent relationships. Se-methylselenocysteine was absorbed more quickly and to a greater extent in whole blood than sodium selenate, as observed by a greater peak Se concentration (Cmax; P < 0.0001), and faster time to peak concentration (Tmax; P < 0.0001) and rate of absorption (P < 0.0001). The rate of absorption and Tmax were also faster (P < 0.0001) in serum of lambs dosed with MeSeCys compared with those dosed sodium selenate at equimolar doses; however, Cmax in serum was greater (P < 0.0001) in lambs dosed with sodium selenate compared with those dosed MeSeCys at equimolar doses. The MeSeCys was absorbed 4 to 5 times faster into serum and 9 to 14 times faster into whole blood at equimolar Se doses. There were dose-dependent increases in the area under the curve (AUC) for Se in serum and whole blood of lambs dosed with both sodium selenate and MeSeCys. In whole blood the MeSeCys was approximately twice as bioavailable as sodium selenate at equimolar doses as observed by the AUC, whereas in serum there were no differences (P > 0.05) in AUC at the same doses. At 168 h postdosing the Se concentration in whole blood remained much greater (P < 0.0001) in lambs dosed with MeSeCys as compared with lambs dosed with sodium selenate; however, the serum Se concentrations were not different between treatments at the same time point. The results presented in this study demonstrate that there are differences between the kinetics of different selenocompounds when orally dosed to sheep. Therefore, in cases of acute selenosis, it is important to understand the chemical form to which an intoxicated animal was exposed when determining the importance and meaning of Se concentration in serum or whole blood obtained at various times postexposure.

Experimental rayless goldenrod (Isocoma pluriflora) toxicosis in horses.

Rayless goldenrod (Isocoma pluriflora) sporadically poisons horses and other livestock in the southwestern United States. Similar to livestock poisoning by white snakeroot (Ageratina altissima) in the midwestern United States, previous research suggests that benzofuran ketones (BFK: tremetone, dehydrotremetone, 6-hydroxytremetone, and 3-oxyangeloyl-tremetone) are responsible for the toxicity of rayless goldenrod. However, experimental reproduction of rayless goldenrod-induced disease and detailed descriptions of poisoning in horses with known concentrations of tremetone and other BFK has not been documented. In this study four horses were fed increasing amounts of rayless goldenrod to obtain doses of approximately 0, 10, 30, and 60 mg BFK/kg BW for 14 days. After seven days of dosing the horse dosed with 60 mg BFK/kg BW horse developed depression, reluctance to eat, dehydration, trembling, and muscle fatigue. Biochemical alterations including increases in the serum enzyme activities of CK, AST, ALT, and LDH, and increased cardiac troponin I concentration, were also identified. Physiologically the clinically poisoned horse had decreased endurance seen as reluctance to perform on the treadmill with increased resting heart rate and a prolonged recovery of heart rate following treadmill exercise. The condition of the horse continued to decline and it was euthanized and necropsied on day 10. At necropsy the myocardium was pale and soft and many of the appendicular and large apical muscles were pale and moist. Histologically, the myocardium had extensive myocardial degeneration and necrosis with extensive fibrosis and multifocal mineralization. Several of the large appendicular muscles in this horse also had small foci of skeletal muscle degeneration and necrosis. Less severe myocardial changes were also identified in the horse dosed with 30 mg BFK/kg BW after 14 days of dosing. No clinical, biochemical or histologic changes were identified in the control horse and the horse dosed with 10 mg BFK/kg BW. These results suggest that doses of 60 mg BFK/kg BW for seven days produce extensive myocardial lesions in horses. The horse dosed with 30 mg BFK/kg BW developed less severe, but similar myocardial lesions over a longer duration, this suggests that poisoning may be cumulative and lower doses of longer duration are also toxic. Horses seem to be uniquely sensitive to rayless goldenrod-induced myocardial disease, therefore cardiac troponin I may be a useful marker of rayless goldenrod poisoning in horses. More work is needed to determine which BFK produce myocardial toxicity and better determine the effects of dose and duration on poisoning in horses.