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PubMedDate not supplied

African sharptooth catfish Clarias gariepinus does not detoxify ammonia to urea or amino acids but actively excretes ammonia during exposure to environmental ammonia.

The African sharptooth catfish Clarias gariepinus lives in freshwater, is an obligatory air breather, and exhibits high tolerance of environmental ammonia. This study aimed at elucidating the strategies adopted by C. gariepinus to defend against ammonia toxicity during ammonia exposure. No carbamoyl phosphate synthetase (CPS) I or III activities were detected in the liver or muscle of the adult C. gariepinus. In addition, activities of other ornithine-urea cycle (OUC) enzymes, especially ornithine transcarbamylase, were low in the liver, indicating that adult C. gariepinus does not have a "functional" hepatic OUC. After being exposed to 50 or 100 mM NH4Cl for 5 d, there was no induction of hepatic OUC enzymes and no accumulation of urea in tissues of the experimental animals. In addition, the rate of urea excretion remained low and unchanged. Hence, ammonia exposure did not induce ureogenesis or ureotely in C. gariepinus as suggested elsewhere for another obligatory air-breathing catfish of the same genus, Clarias batrachus, from India. Surprisingly, the local C. batrachus did not possess any detectable CPS I or III activities in the liver or muscle as had been reported for the Indian counterpart. There were no changes in levels of alanine in the muscle, liver, and plasma of C. gariepinus exposed to 50 or 100 mM NH4Cl for 5 d; neither were there any changes in the glutamine levels in these tissues. Yet even after being exposed to 100 mM NH4Cl for 5 d, there was no significant increase in the level of ammonia in the muscle, which constitutes the bulk of the specimen. In addition, the level of ammonia accumulated in the plasma was relatively low compared to other tropical air-breathing fishes. More importantly, for all NH4Cl concentrations tested (10, 50, or 100 mM), the plasma ammonia level was maintained relatively constant (2.2-2.4 mM). These results suggest that C. gariepinus was able to excrete endogenous ammonia and infiltrated exogenous ammonia against a very steep ammonia gradient. When exposed to freshwater (pH 7.0) with or without 10 mM NH4Cl, C. gariepinus was able to excrete ammonia continuously to the external medium for at least 72 h. This was achieved while the plasma NH4+ and NH3 concentrations were significantly lower than those of the external medium. Diffusion trapping of NH3 through boundary layer acidification can be eliminated as the pH of the external medium became more alkaline instead. These results represent the first report on a freshwater fish (C. gariepinus) adopting active excretion of ammonia (probably NH4+) as a major strategy to defend against ammonia toxicity when exposed to environmental ammonia.

Alanine↗

PubMed2002

Swimming and ammonia toxicity in salmonids: the effect of sub lethal ammonia exposure on the swimming performance of coho salmon and the acute toxicity of ammonia in swimming and resting rainbow trout.

This study tested the hypothesis that swimming exacerbates ammonia toxicity in fish. Both sub-lethal and acute toxicity testing was conducted in a swim tunnel on swimming and resting coho salmon and rainbow trout, respectively. The sub lethal tests on coho salmon also considered the compartmentalization of ammonia within the fish. Coho salmon showed a significant linear decrease in U(crit) both with increasing water ammonia (0, 0.02, 0.04 and 0.08 mg per l NH3) and increasing plasma ammonia. Data collected included plasma pH and ammonia, muscle pH and ammonia and muscle membrane potential. Based on results found in these experiments it was concluded that the reduction in swimming performance was due to both metabolic challenges as well as depolarization of white muscle. Acute toxicity testing on swimming and resting rainbow trout revealed that swimming at (60% U(crit) or approximately 2.2 body lengths/s) decreased the LC50 level from 207+/-21.99 mg N per l in resting fish to 32.38+/-10.81. The LC50 for resting fish was significantly higher than that for swimming fish. The acute value set forth by the US EPA at the same pH is 36.1 mg N per l and may not protect swimming fish. In addition the effect of water hardness on ammonia toxicity was considered. It was found that increased water calcium ameliorates ammonia toxicity in fish living in high pH water.

Ammonia↗

PubMed2002

Accumulation of ammonia in the body and NH(3) volatilization from alkaline regions of the body surface during ammonia loading and exposure to air in the weather loach Misgurnus anguillicaudatus.

The weather loach Misgurnus anguillicaudatus inhabits rice fields that experience drought in summer and ammonia loading during agricultural fertilisation. Exposure of specimens to ammonia led to the accumulation of ammonia in muscle, liver and blood. The level of ammonia reached in the plasma was the highest reported among fishes. Ammonia was not detoxified to urea, and urea excretion rate was unaffected by ammonia exposure. Fish acidified the water to reduce ammonia loading. Ammonia loading, unlike aerial exposure, did not induce glutamine synthesis, and there was no accumulation of glutamine. This is a unique observation different from those reported for other fishes in the literature. An initial switch to partial amino acid catabolism led to the accumulation of alanine and was probably associated with a decreased rate of ammonia production. Aerial exposure led to decreases in rates of ammonia and urea excretion, as well as the accumulation of tissue ammonia. As the internal ammonia levels increased, M. anguillicaudatus was able to excrete some ammonia in the gaseous form (NH(3)). The percentage of ammonia excreted as NH(3) increased with time of exposure and with increasing temperature. It appears that air-breathing through the gut is involved, with the anterior portion of the digestive tract playing a central role: it became significantly more alkaline in fish exposed to air or to environmental ammonia. The skin, which also became more alkaline during air exposure, may also be involved in ammonia volatilization in air-exposed fish. This represents the first report of a fish using volatilization of NH(3) as part of a defence against ammonia toxicity. It can be concluded that the main strategy adopted by M. anguillicaudatus confronted with ammonia loading or air exposure is to tolerate high ammonia levels in the tissues. During periods of elevated tissue ammonia levels, some ammonia is lost by volatilization via air-breathing using the gut. In addition, some ammonia may be lost across the skin during air exposure.

Air↗

PubMed1997

The effects of exposure to ammonia on ammonia and taurine pools of the symbiotic clam

The nutrition of the gutless clam Solemyareidi is supported by the activity of intracellular chemoautotrophic bacteria housed in its gill filaments. Ammonia (the sum of NH3 and NH4+) is utilized as a nitrogen source by the association and is abundant in the clam's environment. In the present study, clams were exposed to 0.011.3mmoll-1 ammonia for 2223h in the presence of thiosulfate as a sulfur substrate. Ammonia exposure increased the ammonia concentration in the tissue pools of the gill, foot and visceral mass from 0.5 to 2µmolg-1wetmass, without added ammonia, to as much as 12µmolg-1wetmass in the presence of 0.7 and 1.3mmoll-1 external ammonia. Gill tissue ammonia concentrations were consistently higher than those in the foot and visceral mass. The elevation of tissue ammonia concentration compared with the medium may be due in part to an ammonia trapping mechanism resulting from a lower intracellular pH compared with sea water and greater permeability to NH3 compared with NH4+. Rates of ammonia incorporation into organic matter (assimilation) were determined using 15N as a tracer. 15N-labeled ammonia assimilation was higher in gill than in foot and increased as a function of 15N-labeled ammonia concentration in the medium. The size of the free amino acid (FAA) pool in the gill also increased as a function of ammonia concentration in the medium. This entire increase was accounted for by a single amino acid, taurine, which was the predominant FAA in both gill and foot tissue. Aspartate, glutamate, arginine and alanine were also abundant but their levels were not influenced by external ammonia concentration. Ammonia assimilation appeared to occur at rates sufficient to account for the observed increase in taurine level. These findings suggest that taurine is a major product of ammonia assimilation.

Journal Article↗

PubMed2003

The swamp eel Monopterus albus reduces endogenous ammonia production and detoxifies ammonia to glutamine during 144 h of aerial exposure.

The swamp eel Monopterus albus inhabits muddy ponds, swamps, canals and rice fields, where it can burrow within the moist earth during the dry summer season, thus surviving for long periods without water. This study aimed to elucidate the strategies adopted by M. albus to defend against endogenous ammonia toxicity when kept out of water for 144 h (6 days). Like any other fish, M. albus has difficulties in excreting ammonia during aerial exposure. In fact, the rates of ammonia and urea excretions decreased significantly in specimens throughout the 144 h of aerial exposure. At 144 h, the ammonia and urea excretion rates decreased to 20% and 25%, respectively, of the corresponding control values. Consequently, ammonia accumulated to high levels in the tissues and plasma of the experimental specimens. Apparently, M. albus has developed relatively higher ammonia tolerance at the cellular and subcellular levels compared with many other teleost fish. Since the urea concentration in the tissues of specimens exposed to air remained low, urea synthesis was apparently not adopted as a strategy to detoxify endogenous ammonia during 144 h of aerial exposure. Instead, ammonia produced through amino acid catabolism was detoxified to glutamine, leading to the accumulation of glutamine in the body during the first 72 h of aerial exposure. Complementing the increased glutamine formation was a significant increase in glutamine synthetase activity in the liver of specimens exposed to air for 144 h. Formation of glutamine is energetically expensive. It is probably because M. albus remained relatively inactive on land that the reduction in energy demand for locomotory activity facilitated its exploitation of glutamine formation to detoxify endogenous ammonia. There was a slight decrease in the glutamine level in the body of the experimental animals between 72 h and 144 h of aerial exposure, which indicates that glutamine might not be the end product of nitrogen metabolism. In addition, these results suggest that suppression of endogenous ammonia production, possibly through reductions in proteolysis and amino acid catabolism, acts as the major strategy to avoid ammonia intoxication in specimens exposed to air for >/=72 h. It is concluded that glutamine formation and reduction in ammonia production together served as effective strategies to avoid the excessive accumulation of ammonia in the body of M. albus during 144 h of aerial exposure. However, these strategies might not be adequate to sustain the survival of M. albus in the mud for longer periods during drought because ammonia and glutamine concentrations had already built up to high levels in the body of specimens exposed to air for 144 h.

Air↗

PubMedDate not supplied

The African lungfish, Protopterus dolloi, detoxifies ammonia to urea during environmental ammonia exposure.

The African lungfish, Protopterus dolloi, was able to maintain a low level of blood plasma ammonia during exposure to high concentrations of environmental ammonia. After 6 d of exposure to 30 or 100 mM NH(4)Cl, the total ammonia concentrations in the blood plasma were 0.288 and 0.289 mM, respectively, which were only 1.7-fold greater than the control value of 0.163 mM. In addition, accumulation of ammonia occurred only in the muscle, but not in the liver. This was achieved in part through urea synthesis, as reflected by significant increases in urea contents in the muscle, liver, and plasma of the experimental animals. In contrast with plasma ammonia, the plasma urea concentrations of specimens exposed to 30 or 100 mM NH(4)Cl for 6 d increased 15.4-fold and 18.8-fold, respectively. Taken together, these results suggest that P. dolloi upregulated the rate of urea synthesis to detoxify ammonia during environmental ammonia exposure and that the increased rate of urea synthesis was fast enough to compensate for the rate of endogenous ammonia production plus the net influx of exogenous ammonia in these experimental animals. Simultaneously, there were increases in the rates of urea excretion in the experimental animals between day 2 and day 6 of environmental ammonia exposure. Interestingly, the rates of urea excretion in specimens exposed to 100 mM NH(4)Cl were lower than those exposed to 30 mM NH(4)Cl, despite the presumably greater load of ammonia to be detoxified to urea in the former situation. It would appear that P. dolloi was regulating the rate of urea excretion during ammonia exposure to retain urea, which might have some physiological functions under environmental stresses yet to be determined. There were decreases in the contents of glutamate, glutamine, and total free amino acids in the liver of the experimental animals, which indirectly suggest that a reduction in the rate of proteolysis and/or amino acid catabolism would have occurred that might lead to a decrease in ammonia production. Our results suggest that, unlike marine elasmobranchs and coelacanths, which synthesize and retain urea for osmoregulatory purposes, the ureogenic P. dolloi was adapted to synthesizing and excreting urea for the purpose of ammonia detoxification.

Amino Acids↗

PubMed2002

The effect of sub-lethal ammonia exposure on fed and unfed rainbow trout: the role of glutamine in regulation of ammonia.

Many species of fishes have evolved mechanisms for coping with ammonia caused by either high ammonia environments or an inability to excrete nitrogenous wastes. Rainbow trout (Oncorhynchus mykiss), have not been known to have such a mechanism. The present study investigated whether rainbow trout can use amino acid synthesis and storage to cope with ammonia. Experiments were performed on fed and unfed rainbow trout under both control and elevated ammonia conditions (0 and 10 mgN/l (total ammonia nitrogen), pH 7.2). The results indicate that both feeding and ammonia exposure increased plasma ammonia significantly 6 h postprandial and post ammonia exposure. After 48 h the fed/ammonia exposed fish had plasma ammonia levels that were not significantly different than the fed/control fish. Plasma ammonia was reduced by more than 50%, attributable to ammonia being converted to glutamine in brain, liver and muscle tissue. Feeding alone also increased glutamine levels in brain tissue. Activity of glutamine synthetase in brain and liver was increased corresponding to an increase in glutamine concentrations when fish were exposed to ammonia. This is the first report showing that rainbow trout can detoxify endogenous and exogenous ammonia.

Ammonia↗

PubMed1995

Nitroarginine, an inhibitor of nitric oxide synthetase, attenuates ammonia toxicity and ammonia-induced alterations in brain metabolism.

We have proposed that acute ammonia toxicity is mediated by activation of the N-methyl-D-aspartate type of glutamate receptors. MK-801, a selective antagonist of these receptors, prevents death of animals induced by acute ammonia intoxication as well as ammonia-induced depletion of ATP. It seems therefore that, following activation of the N-methyl-D-aspartate receptors, the subsequent events in ammonia toxicity should be similar to those involved in glutamate neurotoxicity. As it has been shown that inhibitors of nitric oxide synthetase such as nitroarginine prevent glutamate toxicity, we have tested whether nitroarginine prevents ammonia toxicity and ammonia-induced alterations in brain energy and ammonia metabolites. It is shown that nitroarginine prevents partially (approximately 50%), but significantly death of mice induced by acute ammonia intoxication. Nitroarginine also prevents partially ammonia-induced depletion of brain ATP. It also prevents completely the rise in glucose and pyruvate and partially that in lactate. Injection of nitroarginine alone, in the absence of ammonia, induces a remarkable accumulation of glutamine and a decrease in glutamate. The results reported indicate that nitroarginine attenuates acute ammonia toxicity and ammonia-induced alterations in brain energy metabolites. The effects of MK-801 and of nitroarginine are different, suggesting that ammonia can induce nitric oxide synthetase by mechanisms other than activation of N-methyl-D-aspartate receptors.

Amino Acid Oxidoreductases↗

PubMed2004

Defences against ammonia toxicity in tropical air-breathing fishes exposed to high concentrations of environmental ammonia: a review.

In the tropics, air-breathing fishes can be exposed to environmental ammonia when stranded in puddles of water during the dry season, during a stay inside a burrow, or after agricultural fertilization. At low concentrations of environmental ammonia, NH(3) excretion is impeded, as in aerial exposure, leading to the accumulation of endogenous ammonia. At high concentrations of environmental ammonia, which results in a reversed NH(3) partial pressure gradient (DeltaP(NH3)), there is retention of endogenous ammonia and uptake of exogenous ammonia. In this review, several tropical air-breathing fishes (giant mudskipper, African catfish, oriental weatherloach, swamp eel, four-eyed sleeper, abehaze and slender African lungfish), which can tolerate high environmental ammonia exposure, are used as examples to demonstrate how eight different adaptations can be involved in defence against ammonia toxicity. Four of these adaptations deal with ammonia toxicity at branchial and/or epithelial surfaces: (1) active excretion of NH(4)(+); (2) lowering of environmental pH; (3) low NH(3) permeability of epithelial surfaces; and (4) volatilization of NH(3), while another four adaptations ameliorate ammonia toxicity at the cellular and subcellular levels: (5) high tolerance of ammonia at the cellular and subcellular levels; (6) reduction in ammonia production; (7) glutamine synthesis; and (8) urea synthesis. The responses of tropical air-breathing fishes to high environmental ammonia are determined apparently by behavioural adaptations and the nature of their natural environments.

Air↗

PubMed1999

Respiratory ammonia output and blood ammonia concentration during incremental exercise.

The aim of this study was to investigate whether the increase of ammonia concentration and lactate concentration in blood was accompanied by an increased expiration of ammonia during graded exercise. Eleven healthy subjects performed an incremental cycle ergometer test. Blood ammonia, blood lactate and the amount of expired ammonia were measured until 30 minutes post exercise. The expired air was guided through a flow chamber filled with a sulphuric acid solution to trap the expired ammonia. Blood ammonia, blood lactate increased more than proportionally and the amount of expired ammonia (in micromol/min) increased exponentially with the workload. Post-exercise the amount of expired ammonia decreased within a few minutes back to pre-exercise levels while the concentrations of lactate and ammonia in blood decreased much more slowly and were still elevated after 30 minutes of recovery. We conclude that the more than proportional increase of ammonia and lactate during graded exercise, is accompanied with an exponential increase of expired ammonia output. Faster and more accurate ammonia gas detection techniques are necessary to quantify more precisely the respiratory ammonia output during graded exercise.

Adult↗

PubMedDate not supplied

Alkaline environmental pH has no effect on ammonia excretion in the mudskipper Periophthalmodon schlosseri but inhibits ammonia excretion in the related species Boleophthalmus boddaerti.

Experiments were performed to evaluate the effects of alkaline environmental pH on urea and ammonia excretion rates and on tissue urea, ammonia, and free amino acid concentrations in two mudskippers, Periophthalmodon schlosseri and Boleophthalmus boddaerti. Periophthalomodon schlosseri is known to be capable of actively excreting ammonia. The rate of ammonia excretion in B. boddaerti exposed to 50% seawater (brackish water, BW) at pH 9 decreased significantly during the first 2 d of exposure when compared with that of specimens exposed to pH 7 or 8. This suggested that B. boddaerti was dependent on NH(3) diffusion for ammonia excretion, as in most fishes. It was incapable of detoxifying the accumulating endogenous ammonia to urea but could store and tolerate high concentrations of ammonia in the muscle, liver, and plasma. It did not undergo reductions in proteolysis and/or amino acid catabolism in alkaline water, probably because the buildup of endogenous ammonia was essential for the recovery of the normal rate of ammonia excretion by the third day of exposure to a pH 9 medium. Unlike B. boddaerti, P. schlosseri did not accumulate ammonia in the body at an alkaline pH (i.e., pH 9) because it was capable of actively excreting ammonia. Periophthalmodon schlosseri did not undergo partial amino acid catabolism (no accumulation of alanine) either, although there might be a slight reduction in amino acid catabolism in general. The significant decrease in blood pCO(2) in B. boddaerti at pH 9 might lead to respiratory alkalosis in the blood. In contrast, P. schlosseri was able to maintain its blood pH in BW at pH 9 despite a decrease in pCO(2) in the blood. With 8 mM NH(4)Cl in BW at pH 7, both mudskippers could actively excrete ammonia, although not to the same extent. Only P. schlosseri could sustain ammonia excretion against 8 mM NH(4)Cl in BW at pH 8. In BW containing 8 mM NH(4)Cl at pH 9, both mudskippers died within a short period of time. Boleophthalmus boddaerti consistently died faster than did P. schlosseri. This indicates that the body surfaces of these mudskippers were permeable to NH(3), but the skin of P. schlosseri might be less permeable to NH(3) than that of B. boddaerti. Both mudskippers excreted acid (H(+)) to alter the pH of the alkaline external medium. Such a capability, together with modifications in gill morphology and morphometry as in P. schlosseri, might be essential to the development of an effective mechanism for the active excretion of NH+4.

Acid-Base Equilibrium↗

PubMed1981

Ammonia toxicity in cattle. V. Ammonia concentration of lymph and portal, carotid and jugular blood after the ingestion of urea.

Four rumen-fistulated Holstein steers were fitted with cannulas for the collection of portal, jugular and carotid blood. In addition, the thoracic duct of one steer was cannulated for the collection of lymph. Steers were given .125, .25 or .5 g urea/kg body weight 16 hr after a previous feeding. Within 5 min after the administration of the .5-g dose, rumen ammonia increased from 9.7 to 32.0 mg/100 ml, rumen pH from 6.47 to 7.87; portal blood ammonia from 1.02 to 8.01 mg/100 ml, carotid blood ammonia from .18 to 1.17 mg/100 ml and jugular blood ammonia from .13 to .36 mg/100 ml. Lymph ammonia increased from .22 to .32 mg/100 ml within 15 minutes. The .125- and .25-g doses or urea produced proportionate changes. In a second experiment, three Jersey cows were given .5 g urea/kg body weight, and the rates at which urea appeared in carotid and jugular blood were determined. Only small amounts of urea appeared in carotid and jugular blood during the first 5 min after dosing, but the concentrations then increased slowly but progressively. We concluded that because carotid blood ammonia concentration increased so rapidly after dosing with urea, ammonia must leak past the liver, and it is therefore unlikely, that there is a liver threshold for ammonia which must be exceeded before ammonia will reach the carotid artery. The marked difference in ammonia concentrations in carotid and jugular blood suggests that the brain takes up ammonia rapidly. While some ammonia is absorbed via the lymph, and thus bypasses the liver, the lymph does not appear to be a major contributor of ammonia to carotid blood.

Ammonia↗

PubMed1963

[STUDY OF AMMONIA METABOLISM AND HEPATIC CIRCULATION IN THE DOG. III. ARTERIO-VENOUS DIFFERENCES OF BLOOD AMMONIA. ELECTROENCEPHALOGRAPHIC CHANGES. DISTRIBUTION AND RATE OF DISAPPEARANCE OF AMMONIA].

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Ammonia↗

PubMed1992

Oxygen consumption and ammonia-N excretion of Penaeus chinensis juveniles exposed to ambient ammonia at different salinity levels.

1. Oxygen consumption rate (O2 mg/g/hr) and ammonia-N (un-ionized plus ionized ammonia as nitrogen) excretion rate (microgram/g/hr) of Penaeus chinensis juveniles (0.54 +/- 0.11 g) decreased with increase of salinity among 10, 20 and 30 ppt. 2. Oxygen consumption rate increased with increase of ambient ammonia-N at three salinity levels. 3. Ammonia-N excretion rate was highest (204 micrograms/g/hr) in P. chinensis exposed to 0.985 mg/l ammonia-N at 10 ppt, and lowest (-416 micrograms/g/hr) in that exposed to 9.897 mg/l ammonia-N at 30 ppt. 4. In the prawns exposed to 9.921 mg/l ammonia-N at 20 ppt, and to 5.087 and 9.897 mg/l ammonia-N at 30 ppt, ammonia-N excretion was heavily depressed and ammonia-N influx occurred (ammonia-N uptake was much higher than ammonia-N excretion).

Ammonia↗

PubMed2000

Plasma concentration of urea, ammonia, glutamine around calving, and the relation of hepatic triglyceride, to plasma ammonia removal and blood acid-base balance.

Two experiments were conducted to test the following two hypotheses: 1) fatty liver could hamper hepatic conversion of ammonia to urea and increase circulating ammonia or Gln% [Gln% = Gln x 100/(Gln + Glu)] in cows around parturition; 2) decreased ureagenesis might cause alkalosis and in turn reduce blood Ca. In the first experiment, 14 Holstein cows were monitored from 27 d prepartum to 35 d postpartum. There was a rise in circulating ammonia and Gln% at calving, suggesting an increase in ammonia passing to and through the liver. Stepwise regression analysis revealed the following relationship for plasma samples at 22 h and liver triglyceride at 2 d postpartum: ammonia (microM) = 32.1+/-0.89 triglyceride (% DM), Gln% = 71.2 + 0.23 triglyceride (% DM) + 1.31 urea (mM). The positive correlation between liver triglyceride and plasma ammonia and Gln% suggests that hepatic triglyceride accumulation might inhibit ureagenesis, thereby increasing ammonia concentration at the perivenous hepatocytes where Gln synthesis occurs and increasing ammonia concentration in blood leaving the liver. In the second experiment, 28 rats were used to determine whether hepatic triglyceride accumulation, induced by choline deficiency, affects urinary ammonia N and blood pH homeostasis. There was a trend for a positive correlation between urinary ammonia N and liver triglyceride. No correlation between liver triglyceride and blood pH, bicarbonate, pCO2 or plasma Ca was found. In conclusion, hepatic triglyceride accumulation may inhibit ureagenesis and result in increased circulating ammonia, Gln% and urinary ammonia N in vivo. Hepatic triglyceride accumulation did not affect blood pH homeostasis.

Acid-Base Equilibrium↗

PubMed2005

Chronic and acute ammonia toxicity in mudskippers, Periophthalmodon schlosseri and Boleophthalmus boddaerti: brain ammonia and glutamine contents, and effects of methionine sulfoximine and MK801.

The objective of this study was to elucidate if chronic and acute ammonia intoxication in mudskippers, Periophthalmodon schlosseri and Boleophthalmus boddaerti, were associated with high levels of ammonia and/or glutamine in their brains, and if acute ammonia intoxication could be prevented by the administration of methionine sulfoximine [MSO; an inhibitor of glutamine synthetase (GS)] or MK801 [an antagonist of N-methyl D-aspartate type glutamate (NMDA) receptors]. For P. schlosseri and B. boddaerti exposed to sublethal concentrations (100 and 8 mmol l(-1) NH4Cl, respectively, at pH 7.0) of environmental ammonia for 4 days, brain ammonia contents increased drastically during the first 24 h, and they reached 18 and 14.5 micromol g(-1), respectively, at hour 96. Simultaneously, there were increases in brain glutamine contents, but brain glutamate contents were unchanged. Because glutamine accumulated to exceptionally high levels in brains of P. schlosseri (29.8 micromol g(-1)) and B. boddaerti (12.1 micromol g(-1)) without causing death, it can be concluded that these two mudskippers could ameliorate those problems associated with glutamine synthesis and accumulation as observed in patients suffering from hyperammonemia. P. schlosseri and B. boddaerti could tolerate high doses of ammonium acetate (CH3COONH4) injected into their peritoneal cavities, with 24 h LC50 of 15.6 and 12.3 micromol g(-1) fish, respectively. After the injection with a sublethal dose of CH3COONH4 (8 micromol g(-1) fish), there were significant increases in ammonia (5.11 and 8.36 micromol g(-1), respectively) and glutamine (4.22 and 3.54 micromol g(-1), respectively) levels in their brains at hour 0.5, but these levels returned to normal at hour 24. By contrast, for P. schlosseri and B. boddaerti that succumbed within 15-50 min to a dose of CH3COONH4 (15 and 12 micromol g(-1) fish, respectively) close to the LC50 values, the ammonia contents in the brains reached much higher levels (12.8 and 14.9 micromol g(-1), respectively), while the glutamine level remained relatively low (3.93 and 2.67 micromol g(-1), respectively). Thus, glutamine synthesis and accumulation in the brain was not the major cause of death in these two mudskippers confronted with acute ammonia toxicity. Indeed, MSO, at a dosage (100 microg g(-1) fish) protective for rats, did not protect B. boddaerti against acute ammonia toxicity, although it was an inhibitor of GS activities from the brains of both mudskippers. In the case of P. schlosseri, MSO only prolonged the time to death but did not reduce the mortality rate (100%). In addition, MK801 (2 microg g(-1) fish) had no protective effect on P. schlosseri and B. boddaerti injected with a lethal dose of CH3COONH4, indicating that activation of NMDA receptors was not the major cause of death during acute ammonia intoxication. Thus, it can be concluded that there are major differences in mechanisms of chronic and acute ammonia toxicity between brains of these two mudskippers and mammalian brains.

Acetates↗

PubMed1988

Ammonia can stimulate or inhibit aggregate density in Dictyostelium mucoroides: a quantitative test of the hypothesis that ammonia is the aggregation-suppressing gas.

Ammonia, at moderate concentrations, stimulates aggregate density of Dictyostelium mucoroides. The range of stimulatory concentrations includes ammonia concentrations established by populations of amebae. At higher concentrations, ammonia inhibits aggregate density. A quantitative test of the hypothesis that ammonia is the aggregation-suppressing gas has been carried out. The concentration of ammonia established over defined populations of amebae is one or two orders of magnitude lower than the concentration of ammonia required to exert the same degree of inhibitory effect as the populations of amebae exert. An additional difference between ammonia and the aggregation-suppressing gas is the fact that increasing concentrations of the aggregation-suppressing gas cause progressively larger aggregation streams, while increasing concentrations of ammonia have no such effect. The stimulatory effect of ammonia at concentrations established by ameba populations indicates that ammonia must be included in the variables affecting the aggregation process and that this ammonia effect must be taken into account in any quantitative modelling of the aggregation process.

Ammonia↗

PubMed2004

Use of zeolite for removing ammonia and ammonia-caused toxicity in marine toxicity identification evaluations.

Ammonia occurs in marine waters including effluents, receiving waters, and sediment interstitial waters. At sufficiently high concentrations, ammonia can be toxic to aquatic species. Toxicity identification evaluation (TIE) methods provide researchers with tools for identifying aquatic toxicants. For identifying ammonia toxicity, there are several possible methods including pH alteration and volatilization, Ulva lactuca addition, microbial degradation, and zeolite addition. Zeolite addition has been used successfully in freshwater systems to decrease ammonia concentrations and toxicity for several decades. However, zeolite in marine systems has been used less because ions in the seawater interfere with zeolite's ability to adsorb ammonia. The objective of this study was to develop a zeolite method for removing ammonia from marine waters. To accomplish this objective, we performed a series of zeolite slurry and column chromatography studies to determine uptake rate and capacity and to evaluate the effects of salinity and pH on ammonia removal. We also assessed the interaction of zeolite with several toxic metals. Success of the methods was also evaluated by measuring toxicity to two marine species: the mysid Americamysis bahia and the amphipod Ampelisca abdita. Column chromatography proved to be effective at removing a wide range of ammonia concentrations under several experimental conditions. Conversely, the slurry method was inconsistent and variable in its overall performance in removing ammonia and cannot be recommended. The metals copper, lead, and zinc were removed by zeolite in both the slurry and column treatments. The zeolite column was successful in removing ammonia toxicity for both the mysid and the amphipod, whereas the slurry was less effective. This study demonstrated that zeolite column chromatography is a useful tool for conducting marine water TIEs to decrease ammonia concentrations and characterize toxicity.

Adsorption↗