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Biomedical subjects

D G McDonald

Publications and source records attributed to D G McDonald.

At least 19 recordsLinked to original sources

The recovery of locomotory activity following exhaustive exercise in juvenile rainbow trout (Oncorhynchus mykiss).

This study investigated the recovery of locomotory activity in exhausted juvenile rainbow trout (Oncorhynchus mykiss, approximately 6-10-cm fork length) in response to two conditions: (1) direct transfer to a range of velocities (0-15 cm s(-1)) in a swim flume (forced swimming) and (2) direct transfer to a pool downstream of a swim channel where a choice of velocities was presented: 2-3 cm s(-1) in the lower half of the pool, a range of velocities from 7 to 40 cm s(-1) in the upper half the pool near the channel entrance, and a velocity of 57 cm s(-1) in a swim channel emptying into the pool (volitional swimming). Exhausted trout showed a pronounced delay in the recovery of normal locomotory activity. With forced swimming, the time required to resume swimming was inversely proportional to water velocity. At 15 cm s(-1), almost all exhausted fish recovered immediately, whereas it took about 1 h for recovery at a current of 5 cm s(-1). In contrast, nonexhausted fish responded to imposed velocity with immediate rheotactic responses (orientation and station holding) at all test velocities. In voluntary swim trials, exhausted trout showed a marked preference for holding station in current in the downstream pool (approximately 11 cm s(-1)) but took, on average, 2 h longer than nonexhausted fish to make transits in the swim channel. Moreover, their ground speed in the swim channel was significantly slower. We conclude that swimming performance is impaired for at least 6 h by exhaustive exercise. Maladaptive behaviors during this time include a preference for current near the surface over cover and a reduced capacity for burst activity, both of which would translate into greater predation risk and reduced ability to forage.

Animals↗

Gastrointestinal uptake and fate of cadmium in rainbow trout acclimated to sublethal dietary cadmium.

Adult rainbow trout were pre-exposed to a sublethal concentration of dietary Cd (500 mg/kg dry wt.) for 30 days to induce acclimation. A gastrointestinal dose of radiolabeled Cd (276 microg/kg wet wt.) was infused into the stomach of non-acclimated and Cd-acclimated trout through a stomach catheter. Repetitive blood samples over 24 h and terminal tissue samples were taken to investigate the gastrointestinal uptake, plasma clearance kinetics, and tissue distribution of Cd. Only a small fraction of the infused dose (non-acclimated: 2.4%; Cd-acclimated: 6.6%) was internalized across the gut wall, while most was bound in the gut tissues (10-24%) or remained in the lumen (16-33%) or lost from the fish (approximately 50%) over 24 h. Cadmium loading during pre-exposure produced a profound increase of total Cd in the blood plasma (approximately 28-fold) and red blood cells (RBC; approximately 20-fold). The plasma Cd-time profiles consisted of an apparent rising (uptake) phase and a declining (clearance) phase with a maximum value of uptake in 4 h, suggesting that uptake of gastrointestinally infused Cd was very rapid. Acclimation to dietary Cd did not affect plasma Cd clearance (approximately 0.5 ml/min), but enhanced new Cd levels in the plasma (but not in the RBC), and resulted in a longer half-life for plasma Cd. Tissue total and new Cd levels varied in different regions of the gastrointestinal tract, and overall levels in gut tissues were much greater than in non-gut tissues, reflecting the Cd exposure route. Dietary Cd, but not the infused Cd, greatly increased total Cd levels of all gut tissues in the order posterior-intestine (640-fold) > cecae (180-fold) > mid-intestine (94-fold) > stomach (53-fold) in Cd-acclimated fish relative to naïve fish. Among non-gut tissues in the Cd-acclimated fish, the great increases of total Cd levels were observed in the liver (73-fold), kidney (39-fold), carcass (35-fold), and gills (30-fold). The results provide some clear conclusions that may be useful for environmental risk assessment of dietary Cd exposure in fish.

Acclimatization↗

Audit of the management of convulsive status epilepticus in children: the need for a uniform treatment strategy.

We conducted a two-year prospective audit to review the paediatric management of Convulsive Status Epilepticus (CSE) in Ireland. Our audit showed that there is considerable variability in the management of CSE in this country. In order to provide optimum care for this potentially life-threatening condition a uniform management strategy is required. We propose a protocol for the treatment of CSE, which should ensure uniform management and optimum care and also provide a template for further study and audit of this important disorder.

Anticonvulsants↗

Plasma clearance of cadmium and zinc in non-acclimated and metal-acclimated trout.

Adult rainbow trout were pre-exposed to a sublethal concentration of waterborne cadmium (Cd, 26.7 nmol/l) or waterborne zinc (Zn, 2294 nmol/l) for 30 days to induce acclimation. A single dose of radiolabeled Cd (64.4 nmol/kg) or Zn (183.8 nmol/kg) was injected into the vascular system of non-acclimated and Cd- or Zn-acclimated trout through indwelling arterial catheters. Subsequently, repetitive blood samples over 10 h and terminal tissue samples (liver, heart, bile, stomach, intestine, kidney, gills, muscle, and spleen) were taken to characterize the effect of metal acclimation on clearance kinetics in vivo. Plasma clearance of Cd in Cd-acclimated fish (0.726+/-0.015 and 0.477+/-0.012 ml/min per kg for total and newly accumulated Cd, respectively), was faster than that in non-acclimated trout (0.493+/-0.013 and 0.394+/-0.009 ml/min per kg). Unlike plasma Cd, the levels of Cd in red blood cells (RBCs) were 1.2-2.2 times higher in Cd-acclimated fish than in non-acclimated fish. At 10 h post-injection, the liver accumulated the highest proportion ( approximately 22%) of the injected Cd dose in both non-acclimated and Cd-acclimated fish but did not account for the difference in plasma levels of Cd between two groups. Plasma clearance of Zn ( approximately 0.23 ml/min per kg for new Zn) was substantially lower than Cd clearance. Pre-acclimation to waterborne Zn reduced the new Zn levels in RBCs, but did not affect the clearance of Zn from blood plasma or tissue burdens of Zn in fish. Bile concentrations of both Cd and Zn were elevated in acclimated fish, but total bile burden accounted for <1% of the injected metal dose. The results suggest that the detoxification process of injected plasma Cd is stimulated by pre-acclimation to waterborne Cd, and that Zn levels are homeostatically controlled in both non-acclimated and acclimated trout.

Adaptation, Physiological↗

The effects of trace metal exposure on agonistic encounters in juvenile rainbow trout, Oncorhynchus mykiss.

The effects of five trace metals, copper, cadmium, nickel, zinc and lead (presented as soluble salts) on the ability of juvenile rainbow trout to form social relationships were investigated. Comparable concentrations of the five metals in relation to their acute 96 h LC50s (concentration at which population mortality=50% at 96 h) were used (i.e. 15% of the 96 h LC50) and water quality parameters (hardness=120 mg l(-1) as CaCO(3), pH 8; DOC=3 mg l(-1)) were kept constant throughout. In the first experiment, trout exposed to sublethal concentrations of cadmium for 24 h displayed significantly lower numbers of aggressive attacks during pair-wise agonistic encounters than fish paired in the copper, nickel, zinc, lead and control water. In a second experiment, fish were exposed to the same concentration of metal for 24 h, and then returned to normal water for 24 h. When these metal pre-exposed fish were paired with non-exposed fish only cadmium pre-exposure had a significant effect on social interaction. All of the cadmium pre-exposed fish became subordinate when paired with non-exposed fish, whereas the probability of a fish pre-exposed to copper, nickel, zinc or lead becoming subordinate did not significantly differ from random. Therefore, at around 15% of the 96 h LC50, different metals exert different effects on the social behaviour of fish, suggesting potential implications for social structure and population stability.

Aggression↗

Socially-induced changes in sodium regulation affect the uptake of water-borne copper and silver in the rainbow trout, Oncorhynchus mykiss.

Subordinate fish take up more copper during water-borne exposure than dominant fish and consequently display higher tissue burdens. The present study demonstrated a similar effect of social status on water-borne silver uptake. We evaluated whether differences in copper and silver accumulation between individuals could be due to differences in metabolic rate, internal concentrations of cortisol or sodium uptake rates. In the absence of social interaction, experimentally increased metabolic rates (via moderate exercise) and elevated whole body cortisol concentrations (via feeding of a cortisol-spiked diet) did not result in increased metal uptake. However, elimination of the difference in sodium uptake rates between dominant and subordinate fish by exposing them to a saturating level of water-borne sodium (50 mM) resulted in an elimination of copper uptake differences. No significant differences in sodium and silver uptake rates were seen between dominant and subordinate fish exposed to elevated silver concentrations. Therefore, it appears that socially-mediated differences in copper and silver accumulation are a result of differences in sodium uptake rates as both silver and copper are known to cross the gill epithelia via sodium transport pathways.

Animal Feed↗

Dietary sodium inhibits aqueous copper uptake in rainbow trout (Oncorhynchus mykiss).

Ours is the first study to demonstrate an influence of dietary sodium on waterborne copper uptake in fish. We examined possible interactions between dietary sodium and the response of freshwater rainbow trout (Oncorhynchus mykiss) to waterborne copper in light of recent evidence of interactions between sodium and copper metabolism in the gills. Trout were maintained for 6 days on one of four diets of increasing sodium concentration (0.25 mmol g(-1), 0.51 mmol g(-1), 0.76 mmol g(-1) and 1.27 mmol g(-1), which corresponds to 0.6%, 1.2%, 1.8% and 3% sodium by mass, respectively). At the end of 7 days, fish were exposed for 6 h to waterborne copper spiked with (64)Cu to determine if the dietary sodium affected responses to a subsequent short-term waterborne copper exposure. The radiotracer allowed us to distinguish between Cu occurring in fish tissues before the experiment and 'newly accumulated' Cu arising from the experimental exposure. Dietary sodium concentrations of 1.8% or 3% reduced newly accumulated copper concentrations in gill (from 93.9 ng g(-1) in control to 38.9 ng g(-1) and 20.0 ng g(-1) in fish fed 1.8% or 3% Na(+)-supplemented diets, respectively), liver (from 64.3 ng g(-1) to 23.1 ng g(-1) and 7.5 ng g(-1), respectively), kidney (from 29.3 ng g(-1) to 11.7 ng g(-1) and 7.8 ng g(-1), respectively), plasma (from 64.7 ng g(-1) to 21.5 ng g(-1) and 10.7 ng g(-1), respectively) and gut (from 6.8 ng g(-1) to 3.4 ng g(-1) and 2.2 ng g(-1), respectively) by 50.0-88.2%. The 3% Na(+)-supplemented diets also increased plasma and gut sodium concentrations by 38.1% (from 137.1 micromol g(-1) to 189.3 micromol g(-1)) and 104.3% (from 56.5 micromol g(-1) to 115.4 micromol g(-1)), respectively, relative to fish maintained on untreated diets. Whole body uptake rates of both sodium and copper were significantly reduced, and highly correlated (r=0.97) with one another, in fish fed high-sodium diets relative to controls. Moreover, sodium efflux was 12% and 38% higher in fish fed 1.8% and 3% sodium-enriched diets, respectively. Fish fed high-sodium diets also drank more water, but the contribution of drinking to waterborne copper uptake was negligible. From these results, we speculate that, at least in part, aqueous sodium and copper share a common branchial uptake route, probably through an apical sodium channel. According to this hypothesis, as the channel is downregulated with increasing internal sodium concentrations, both sodium and copper uptake from the water are inhibited.

Algorithms↗

The further development of ionoregulatory measures as biomarkers of sensitivity and effect in fish species.

Extensive season-by-season sampling was used to establish the normal range of whole-body Na+ and Cl- and Na+ uptake in healthy populations of two fish species, rainbow trout, Oncorhynchus mykiss, and fathead minnow, Pimephales promelas, of known differences in sensitivity to ionoregulatory toxicants (low pH, trace metals). These data together with responses of both species to six different ionoregulatory challenge tests of increasing severity (mild handling, exposure to low Ca2+ water, epinephrine injection, net-confinement stress, exposure to copper, and osmotic shock) were evaluated for their potential as biomarkers of sensitivity and of effect of ionoregulatory toxicants. There were no obvious biomarkers of sensitivity in the ion measures themselves, but four of the six challenges (exposure to low Ca2+ water, epinephrine injection, exposure to copper, and osmotic shock) produced a significantly greater effect in the more sensitive of the two species, fathead minnow. Based on the responses of both species, this article makes a number of recommendations for the application of ion measures alone and in combination with challenge tests to the assessment of chronic effects in populations experiencing sublethal ionoregulatory stress.

Animals↗

Creatine supplementation affects sprint endurance in juvenile rainbow trout.

Fingerling rainbow trout were supplemented with equal amounts of creatine (Cr) by two routes: dietary (12.5 mg Cr per g food); or intraperitoneal injection (0.5 mg Cr per g fish). Endurance in a fixed velocity sprint test (at a speed of 7 BL s(-1)), and resting levels of white muscle metabolites (total creatine [a measure of free creatine plus phosphocreatine (PCr), ATP, lactate and glycogen] were assessed following 7 days of supplementation and compared to controls. None of the treatments had a significant effect on growth, muscle total creatine, percent phosphorylation of creatine, ATP or lactate. However, resting muscle glycogen was elevated in creatine-supplemented fish. Higher muscle glycogen corresponded to significantly greater endurance in creatine-supplemented fish. Although fish do not actively transport additional creatine into the muscle, a mechanism whereby circulating creatine acts to enhance muscle glycogen is present. These results suggest that the improved endurance may be due to an insulin-dependent mechanism (similar to that elucidated in mammalian studies) that allows fish to supercompensate muscle glycogen stores, thus extending endurance through enhanced glycolytic flux.

Adenosine Triphosphate↗

Effects of chronic Cd exposure via the diet or water on internal organ-specific distribution and subsequent gill Cd uptake kinetics in juvenile rainbow trout (Oncorhynchus mykiss).

New regulatory approaches to metal toxicity (e.g., biotic ligand model [BLM]) focus on gill metal binding and tissue-specific accumulation of waterborne metals; the dietary route of exposure and dietary/waterborne interactions are not considered, nor are the consequences of chronic exposure by either route. Therefore, we studied the effect of the same gill Cd load (approximately 2.5 microg/g), achieved by a chronic, 30-d exposure to Cd either via the diet (1,500 mg/kg) or the water (2 microg/L), on tissue-specific Cd distribution and subsequent uptake of waterborne Cd in juvenile rainbow trout (Oncorhynchus mykiss). These two exposure regimes resulted in a branchial Cd load that had been taken up across either apical gill membranes (waterborne Cd) or basolateral gill membranes (through the bloodstream for dietary Cd). The BLM characteristics of the gills (i.e., short-term Cd uptake kinetics) were altered: affinity (log K(Cd Gill) [95% confidence level]) decreased from 7.05 (6.75-8.76) for control to 6.54 (6.32-7.03) for waterborne Cd and 5.92 (5.83-6.51) for dietary Cd, whereas binding capacity (Bmax) increased from 3.12 (2.14-4.09) to 4.80 (3.16-6.43) and 5.50 (2.86-8.17) nmol x g(-1) for control, waterborne, and dietary Cd, respectively. Fish exposed to dietary Cd accumulated a much greater overall chronic Cd body burden relative to fish exposed to waterborne Cd or control fish. The carcass accumulated the greatest percentage of total body Cd in control and waterborne-exposed fish, whereas the intestinal tissue accumulated the greatest percentage in dietary-exposed fish. Tissue-specific Cd burdens were highest in the kidney in both dietary and waterborne treatments. We conclude that chronic Cd exposure alters Cd uptake dynamics, and that the route of Cd exposure, whether waterborne or dietary, results in differences of internal Cd accumulation and branchial Cd uptake characteristics. These factors should be considered in future BLM development.

Administration, Oral↗

Calcium homeostasis in larval and adult Drosophila melanogaster.

Calcium homeostasis in Drosophila melanogaster was examined in response to the challenges imposed by growth, reproduction and variations in dietary calcium content. Turnover time for calcium, calculated as the time for (45)Ca(2+)to accumulate to half the steady state value of 3.46 nmol/fly, was 3.3 days. Although larvae weighed 2x as much as adults, they contained 3-4x as much calcium. Anterior Malpighian tubules (Mts) contain much more calcium than posterior Mts, accounting for 25-30% of the calcium content of the whole fly. In response to a 6.2-fold increase in dietary calcium level, calcium content of whole flies increased only 10%. Hemolymph calcium concentration ( approximately 0.5 mM) was similar in males and females and in animals raised on diets differing in calcium content. Fluid secretion rate, secreted fluid calcium concentration, and transepithelial calcium flux in tubules isolated from flies raised on high and low calcium diets did not differ significantly. Malpighian tubules secrete calcium at rates sufficient to eliminate whole body calcium content in 0.5 and 3 days for tubules secreting fluid at basal and maximal rates, respectively. It is suggested that flies absorb high quantities of calcium from the diet and maintain homeostasis through the combined effects of elimination of calcium in fluid secreted by the Malpighian tubules and the sequestration of calcium in granules, especially within the distal segment of the anterior pair of Malpighian tubules.

Animals↗

Effects of long term sublethal Cd exposure in rainbow trout during soft water exposure: implications for biotic ligand modelling.

The objectives of the study were to determine the physiological and toxicological effects of chronic cadmium exposure on juvenile rainbow trout in soft water. Particular attention focused on acclimation, on comparison to an earlier hard water study, and on whether a gill surface binding model, originally developed in dilute soft water, could be applied in this water quality to fish chronically exposed to Cd. Juvenile rainbow trout, on 3% of body weight daily ration, were exposed to 0 (control), 0.07, and 0.11 microg l(-1) Cd [as Cd(NO(3))(2).4H(2)O] in synthetic soft water (hardness=20 mg l(-1) as CaCO(3), alkalinity=15 mg l(-1) as CaCO(3), pH 7.2) for 30 days. Mortality was minimal for all treatments (up to 14% for 0.11 microg l(-1) Cd). No significant effects of chronic Cd exposure were seen in growth rate, swimming performance (stamina), routine O(2) consumption, or whole body/plasma ion levels. In contrast to the hard water study, no acclimation occurred in either exposure group in soft water, with no significant increases in 96-h LC(50) values. Cadmium accumulated in a time-dependent fashion to twice the control levels in the gills and only marginally in the liver by 30 days. No significant Cd accumulation occurred in the gall bladder or whole body. Cadmium uptake/turnover tests were run using radioactive 109Cd for acute (3 h) exposures. Saturation of the gills occurred for control fish but not for Cd-exposed fish when exposed to up to 36 microg l(-1) Cd for 3 h. Cd-exposed trout accumulated less 'new' Cd in their gills compared to controls and they internalized less 109Cd than control fish. This effect of lowered Cd uptake by the gills of acclimated trout was earlier seen for the fish acclimated to 10 microg l(-1) Cd in hard water. The affinity of the gill for Cd was greater in hard water (logK(Cd-gill)=7.6) than in soft water (logK(Cd-gill)=7.3) but the number of binding sites (B(max)=0.20 microg g(-1) gill) was similar in both media. In addition, there was a shift in affinity of the gill for Cd (i.e. lowered logK(Cd-gill)) and increased B(max) with chronic Cd exposure in both soft water and hard water. We conclude that the present gill modelling approach (i.e. acute gill surface binding model or Biotic Ligand Model) does work for soft and hard water exposures but there are complications when applying the model to fish chronically exposed to cadmium.

Animals↗

Focal upper limb neuropathy in a child.

A 9-year-old girl presented with a 4-week history of right upper limb weakness. Clinical assessment and neurophysiological studies suggested an atypical brachial plexitis. She re-presented 3 1/2 years later with progressive muscle weakness involving both legs and left arm and hand. There had been no interval improvement in her right upper limb. Clinical, neurophysiological and pathological findings were consistent with chronic inflammatory demyelinating polyneuropathy. She responded to a single course of intravenous immunoglobulin--and review more than 6 years after treatment confirms that she remains functionally normal. Focal upper limb neuropathy preceding a diffuse demyelinating process by several years has not been previously described in a child. Long-term follow-up of this patient allows us to comment on the natural history of her condition and the apparent long-term efficacy of intravenous immunoglobulin in this case.

Arm↗

Gastrointestinal uptake and distribution of copper in rainbow trout.

A single dose of radioactive copper ((64)Cu or new Cu) was infused into the stomach of rainbow trout (Oncorhynchus mykiss) to model dietary copper (Cu) uptake under conditions of a normal nutritional dose and optimum environmental temperature (16 degrees C, 0.117 microg Cu g(-)(1 )body mass). The distribution of new Cu to the gut and internal organs occurred in two phases: rapid uptake by the gut tissues (almost complete by 24 h post-infusion) followed by slower uptake by the internal organs. By 72 h, 60 % of the dose had been excreted, 19 % was still retained in the gut tissue, 10 % remained in the lumen and 12 % had been absorbed across the gut and partitioned amongst the internal organs. A reduction in water temperature of 10 degrees C (to 6 degrees C) significantly retarded components of new Cu distribution (movement of the bolus along the gut and excretion); nonetheless, by 72 h, the fraction absorbed by all the internal organs was similar to that at 16 degrees C. An increase in water temperature of 3 degrees C (to 19 degrees C) caused a pronounced increase in internal organ uptake by 24 h to approximately double the uptake occurring at 16 degrees C. The uptake of new Cu by the gut tissue had a low temperature coefficient (Q(10)<1) consistent with simple diffusion, while the temperature coefficient for transfer of new Cu from gut tissue to the internal organs was high (Q(10)>2), consistent with facilitated transport. Internally, the liver and gall bladder (including bile) were the target organs for dietary Cu partitioning since they were the only organs that concentrated new Cu from the plasma. Individual tissues differed in terms of the exchange of their background Cu pools with new Cu. The background Cu in the walls of the gastrointestinal tract (excluding stomach) exchanged 45-94 % with new Cu from the gut lumen, while tissues such as the stomach, gills, kidney, carcass and fat had 5-7 % exchangeable background Cu. The liver, heart, spleen, ovary, bile and plasma had only 0.2-0.8 % exchangeable background Cu. The gastrointestinal tissues appear to act as a homeostatic organ, regulating the absorption of nutritional (non-toxic) doses of Cu (0. 117 microg g(-)(1 )body mass day(-)(1)) by the internal organs. Within the dose range we used and at optimal temperature (16 degrees C), the new Cu content of the gut tissues fluctuated, but absorption of new Cu by the internal organs remained relatively constant. For example, predosing the fish with non-radioactive Cu caused new Cu absorption by the gut tissues to double and decreased new Cu excretion from 38 to 1.5 %, but had no effect on new Cu uptake by the internal organs. Feeding fish after application of the normal liquid dose of new Cu also had no effect on new Cu uptake by the internal organs, even though the presence of food in the digestive tract reduced the binding of new Cu to the gut tissues and assisted with the excretion of new Cu. The gut was therefore able to regulate new Cu internalization at this dosage. Higher new Cu doses (10, 100 and 1000 times the normal dose), however, evoked regurgitation and increased new Cu excretion within 4 h of application but did not elevate new Cu levels in gut tissue beyond a threshold of approximately 40 microg of new Cu. Only at the highest dose (1000 times the normal dose, 192 microg g(-)(1 )body mass), equivalent to toxic concentrations in the daily diet (7000 microg Cu g(-)(1 )dry mass food), was the buffering capacity of the gut overwhelmed, resulting in an increase in internal new Cu uptake.

Animals↗

Training success in U.S. Navy special forces.

Several aspects of success in an intensive military training experience on a select group of military trainees were studied. The primary dependent variables were differences in questionnaire scores between graduates and those who drop, and questionnaire score changes from pretest to posttest in graduates. A total of 336 trainees at the U.S. Navy 's Basic Underwater Demolition/SEALS (BUD/S) training school were tested at the beginning of their training period; 6 months later, all successful trainees were retested on graduation. The total sample was divided into two groups for replication. Results indicated that graduates differed consistently from drops on the Estimation scale of the Physical Estimation and Attraction Scale (PEAS), and four scales on the Hogan Personality Inventory (HPI); graduates showed consistent posttest changes in the Estimation scale, three out of six scales on the Profile of Mood States (POMS), plus four scales on the HPI. Differences between graduates and drops suggested that some aspects of the PEAS and HPI could be used as a screening device in order to reduce attrition. Posttest changes on the PEAS, POMS, and HPI in Graduates were in part consistent with previous work and in part somewhat new, indicating both general and unique features of the BUD/S training experience.

Achievement↗