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Biovolatilization of antimony and sudden infant death syndrome (SIDS).

1. The aerobic filamentous fungus S. brevicaulis IMI 17297 methylated antimony from Sb2O3 substrate, with the formation of gaseous trimethylantimony (TMA). No evidence was found for the generation of other gaseous antimony compounds by this organism. 2. Biovolatilization of inorganic antimony was greatest during cultivation of the fungus on solid media at 25 degrees C, and occurred more readily from antimony (III) substrates than from antimony (V) substrates. 3. Under simulated cot environment conditions (CO2 enriched atmosphere, 33 degrees C) the fungus exhibited an altered morphology and a reduced capability to volatilize inorganic antimony from the pure compound. 4. No evidence of antimony biovolatilization from cot mattress PVC was found, unless antimony was released from PVC by heat treatment (at 80 or 100 degrees C). 5. These data suggest that normal cot environment conditions are non-optimal for volatilization of antimony by S. brevicaulis, and that Sb2O3 in cot mattress PVC is not bioavailable. 6. Cot mattress isolates of S. brevicaulis also volatilized antimony (not encapsulated by PVC), whereas those of other filamentous fungi (Penicillium spp., Aspergillus niger, Aspergillus fumigatus, Alternaria sp.) and of bacteria (Bacillus spp.) did not. 7. The oxidation products of TMA may be the true determinants of toxicity for biogenic antimony gases produced in an aerobic environment.

Antimony↗

Resistance to antimony and treatment failure in human Leishmania (Viannia) infection.

BACKGROUND: Failure of antimonial therapy has been increasingly reported in anthroponotic visceral leishmaniasis and in cutaneous disease. The role of drug resistance in treatment failure has been difficult to ascertain because therapeutic response is multifactorial, and the efficacy of antimonial drugs depends on an effective immune response. In this study, we sought to determine whether standard treatment selects for resistant organisms and whether drug resistance contributes to treatment failure. METHODS: We evaluated the susceptibility to antimony of 19 strains isolated before treatment with meglumine antimoniate and 21 strains isolated at treatment failure from 20 patients. The 50% effective dose (ED50) of antimony in the form of additive-free meglumine antimoniate was determined for intracellular amastigotes in human promonocytic U-937 cells. RESULTS: Before treatment, 16% of strains (3/19) showed primary resistance (ED50 of >128 microg Sb/mL), whereas 84% (16/19) were susceptible (ED50 of <20 microg Sb/mL). However, 88% of susceptible strains (14/16) had ED90 values of >128 microg Sb/mL. At treatment failure, 40% of strains (8/20) were resistant. Secondary resistance was documented in 4 patients. CONCLUSIONS: Primary and secondary resistance to antimony can contribute to treatment failure in American cutaneous leishmaniasis. Selection for resistance to antimony occurs during standard treatment with antimonial drugs, and primary resistance to antimony supports the plausibility of anthroponotic transmission.

Adolescent↗

Occupational exposure to antimony compounds.

The toxicology of antimony and its compounds is known from three sources: its medicinal use over centuries, studies of process workers in more recent times, and more recent still, studies of its presence in modern city environments and in domestic environments. Gross exposure to antimony compounds over long periods, usually the sulfide (SbS3) or the oxide (Sb2O3) has occurred in antimony miners and in antimony process workers. There have been relatively few of these, and few studies of possible symptoms have been made. Antimony sulfide imported from, at different times, China, South Africa, and South America was processed in the North-East of England from about 1870 to 2003. The process workers in North-East England have been studied at different times, notably by Sir Thomas Oliver in 1933, and by the Newcastle upon Tyne University Department of Occupational Medicine on later occasions. Studies which have been made of the working environment, and in particular of the risk of lung cancer in process workers, have underlined the high levels of exposure to antimony compounds and to other toxic materials. However, the working conditions in antimony processing have improved markedly over the last 30 years, and the workforce had been much reduced in numbers following automation of the process. Prior to the cessation of the industry in the UK it had become a 'white coat' operation with relatively few people exposed to high concentrations of antimony. Antimony, which is normally present in domestic environments, has also been studied as a possible cause of cot death syndrome (SIDS) but extensive investigations have not confirmed this. The full importance of environmental antimony has still to be determined, and evidence of specific effects has not yet been presented.

Air Pollutants, Occupational↗

Increased biliary excretion of glutathione is generated by the glutathione-dependent hepatobiliary transport of antimony and bismuth.

We have recently demonstrated that the hepatobiliary transport of arsenic is glutathione-dependent and is associated with a profound increase in biliary excretion of glutathione (GSH), hepatic GSH depletion and diminished GSH conjugation (Gyurasics A, Varga F and Gregus Z, Biochem Pharmacol 41: 937-944 and Gyurasics A, Varga F and Gregus Z, Biochem Pharmacol 42: 465-468, 1991). The present studies in rats aimed to determine whether antimony and bismuth, other metalloids in group Va of the periodic table, also possess similar properties. Antimony potassium tartrate (25-100 mumol/kg, i.v.) and bismuth ammonium citrate (50-200 mumol/kg, i.v.) increased up to 50- and 4-fold, respectively, the biliary excretion of non-protein thiols (NPSH). This resulted mainly from increased hepatobiliary transport of GSH as suggested by a close parallelism in the biliary excretion of NPSH and GSH after antimony or bismuth administration. Within 2 hr, rats excreted into bile 55 and 3% of the dose of antimony (50 mumol/kg, i.v.) and bismuth (150 mumol/kg, i.v.), respectively. The time courses of the biliary excretion of these metalloids and NPSH or GSH were strikingly similar suggesting co-ordinate hepatobiliary transport of the metalloids and GSH. However, at the peak of their excretion, each molecule of antimony or bismuth resulted in a co-transport of approximately three molecules of GSH. Diethyl maleate, indocyanine green and sulfobromophthalein (BSP), which decreased biliary excretion of GSH, significantly diminished excretion of antimony and bismuth into bile indicating that hepatobiliary transport of these metalloids is GSH-dependent. Administration of antimony, but not bismuth, decreased hepatic GSH level by 30% and reduced the GSH conjugation and biliary excretion of BSP. These studies demonstrate that the hepatobiliary transport of trivalent antimony and bismuth is GSH-dependent similarly to the hepatobiliary transport of trivalent arsenic. Proportionally to their biliary excretion rates, these metalloids generate increased biliary excretion of GSH probably because they are transported from liver to bile as unstable GSH complexes. The significant loss of hepatic GSH into bile as induced by arsenic or antimony may compromise conjugation of xenobiotics with GSH.

Animals↗

Human biomonitoring of antimony.

OBJECTIVES: The aim of the study was to test the suitability of 24-h urine, blood, and scalp-hair samples as surrogates for the determination of internal exposure to antimony in case of a strongly elevated soil contamination with antimony. METHODS: The bio-monitoring was performed using graphite-furnace atomic absorption spectrometry. Blood and scalp-hair samples were decomposed by microwave digestion. RESULTS: No elevated content of antimony could be detected in 24-h urine, blood, or scalp-hair samples from the study participants geogenically exposed to antimony. The results did not show a correlation between the antimony contents in the soil of the housing area and those in urine, blood, or hair. Surprisingly, the reference group (n = 47) showed a significantly higher median antimony excretion rate than did the exposed group (n = 89; 1.23 versus 0.60 micrograms Sb/24 h). Additionally, the scalp-hair contents of the reference group were also significantly higher than those of the exposed persons (0.045 versus 0.026 mg Sb/kg). Blood contents of the two study groups were 0.57 and 0.48 microgram Sb/l, respectively. The detection limit for urine and blood was 0.5 microgram Sb/l and that for scalp hair was 0.005 mg Sb/kg. Of all samples of urine, blood, and scalp hair analyzed, 31.2%, 49.3%, and 10.3%, respectively, were below the limit of analytical detection. CONCLUSIONS: The antimony contents recorded for both study groups in urine, blood, and scalp hair can be judged as being within the normal range. The rate of transfer of antimony from the soil to humans in the exposure case described seemed to be very low. With respect to analytical practicability and validity, urine was the surrogate which deemed most useful for determination of internal exposure to antimony.

Adult↗

Cross-resistance between cisplatin and antimony in a human ovarian carcinoma cell line.

The metal compound cisplatin (DDP) is a widely used anticancer agent but naturally occurring and acquired resistance to DDP limits its effectiveness. Resistance is associated with a decreased accumulation of DDP and increased levels of glutathione and metallothioneins. Such changes also serve as protective and detoxification mechanisms for other metal salts in prokaryotes and lower eukaryotes. The aim of this study was to find metal salts for which the cross-resistance profile was the same as for DDP in sublines of the parental 2008 human ovarian carcinoma cells selected with either DDP (2008/C13*5.25) or CdCl2 and ZnCl2 (2008/MT). Among the metal salts tested the resistance profile of trivalent antimony most closely resembled that of DDP. DDP-selected cells were 15-fold resistant to DDP and 4.4-fold cross-resistant to antimony potassium tartrate, whereas of the cations tested (Cd2+, Zn2+, Ni2+ and Co2+) cross-resistance was observed only for Cd2+ (2.4-fold). When 2008 cells were selected for resistance to antimony (6.6-fold) they were found to be 16-fold cross-resistant to DDP. Accumulation of the DDP analogue cis-[3H]dichloro(ethylenediamine)platinum(II) was 59% lower in the DDP-selected subline and 48% lower in the antimony-selected variant than in the parental cell line. We conclude from the mutual cross-resistance to DDP and antimony potassium tartrate and from the impaired uptake of [3H]DEP in both the DDP and antimony-selected variants that DDP and antimony share a common mechanism of resistance. The significance of this observation lies in the fact that several evolutionarily conserved mechanisms for antimony detoxification are already known in lower organisms which may point the way to identification of additional DDP resistance mechanisms in mammalian cells.

Antimony↗

Syntheses, crystal structures and antimicrobial activities of 6-coordinate antimony(III) complexes with tridentate 2-acetylpyridine thiosemicarbazone, bis(thiosemicarbazone) and semicarbazone ligands.

Five novel antimony(III) complexes with the mono- and bis(thiosemicarbazone) ligands of 2N1S or 4N2S donor atoms, N'-[1-(2-pyridyl)ethylidene]morpholine-4-carbothiohydrazide (Hmtsc, L1) and bis[N'-[1-(2-pyridyl)ethylidene]]-1,4-piperazinedicarbothiohydrazide (H(2)ptsc, L7), and the tridentate semicarbazone ligand of 2N1O donor atoms, 2-acetylpyridine semicarbazone (Hasc, L2b), were prepared by reactions of SbCl(3) or SbBr(3), and characterized by elemental analysis, TG/DTA, FT-IR and (1)H NMR spectroscopy. The crystal and molecular structures of five antimony(III) complexes were determined by single-crystal X-ray structure analysis. The neutral, 6-coordinate antimony(III) complexes ([Sb(mtsc)Cl(2)] 1, [Sb(mtsc)Br(2)] 2, [Sb(asc)Cl(2)] 3 and [Sb(asc)Br(2)] 4) are depicted with one electron pair (5s(2)) of the antimony(III) atom, deprotonated forms of multidentate thiosemicarbazone or semicarbazone ligands, and two monodentate halogen ligands, respectively. In the dimer complex 5 ([Sb(2)(ptsc)Cl(4)]) with the ligand in which two tridentate thiosemicarbazone moieties are connected by the piperazine moiety, each antimony(III) was also described as a neutral 6-coordinate structure. These antimony(III) complexes were thermally stable around 200 degrees C. Water-soluble antimony(III) complexes 1 and 2 showed moderate antimicrobial activities against Gram-positive (Bacillus subtilis and Staphylococcus aureus) and -negative bacteria (Escherichia coli and Pseudomonas aeruginosa), yeasts (Candida albicans and Saccharomyces cerevisiae) and molds (Aspergillus niger and Penicillium citrinum). Complex 5 showed moderate antimicrobial activities against four bacteria, and two molds, while the ligand itself showed only modest antimicrobial activities against selected bacteria (B. subtilis, E. coli and S. aureus). The molecular structures and antimicrobial activities of antimony(III) complexes were compared with those of bismuth(III) complexes in the same 15 group in the periodic table.

Anti-Infective Agents↗

Antimony speciation by inductively coupled plasma mass spectrometry using solid phase extraction cartridges.

A novel and simple method for inorganic antimony speciation is described based on selective solid phase extraction (SPE) separation of antimony(III) and highly sensitive inductively coupled plasma mass spectrometric (ICP-MS) detection of total antimony and antimony(V) in the aqueous phase of the sample. Non-polar SPE cartridges, such as the Isolute silica-based octyl (C8) sorbent-containing cartridge, selectively retained the Sb(III) complex with ammonium pyrrolidine dithiocarbamate (APDC), while the uncomplexed Sb(V) remained as a free species in the solution and passed through the cartridge. The Sb(III) concentration was calculated as the difference between total antimony and Sb(V) concentrations. The detection limit was 1 ng L(-1) antimony. Factors affecting the separation and detection of antimony species were investigated. Acidification of samples led to partial or complete retention of Sb(V) on C8 cartridge. Foreign ions tending to complex with Sb(III) or APDC did not interfere with the retention behavior of the Sb(III)-APDC complex. This method has been successfully applied to antimony speciation of various types of water samples.

Antimony↗

Characterization of the antimonial antileishmanial agent meglumine antimonate (glucantime).

Meglumine antimonate (Glucantime), a drug of choice for the treatment of leishmaniasis, is produced by the reaction of pentavalent antimony with N-methyl-D-glucamine, a carbohydrate derivative. We investigated the structure and composition of meglumine antimonate, which remain poorly understood, despite 50 years of use. Measurement of the antimony content of meglumine antimonate powder indicated a 1:1.37 molar ratio of antimony to N-methyl-D-glucamine. Osmolality measurements performed with meglumine antimonate solutions demonstrated an average of 1.43 antimony atoms per molecule of meglumine antimonate. The osmolality of a 1:10 dilution of stock meglumine antimonate increased by 45% over 8 days, suggesting hydrolysis to less complex species. A comparison of the proton nuclear magnetic resonance spectra of N-methyl-D-glucamine and meglumine antimonate revealed an increase in complexity in the latter but with all of the resonances of the former still being evident, consistent with the presence of coordination complexes between antimony and each of the N-methyl-D-glucamine hydroxyls. Fast atom bombardment and electrospray ionization mass spectrometry coupled with several derivatization procedures provided evidence that up to four N-methyl-D-glucamine hydroxyls are coordinated with each antimony. A series of oligomers were observed. The major moiety has a molecular mass of 507 atomic mass units and consists of NMG-Sb-NMG, where Sb represents antimony and NMG represents N-methyl-D-glucamine. Additional species containing up to four antimony atoms and five N-methyl-D-glucamine moieties and corresponding to the general form (NMG-Sb)n-NMG are also present. These results suggest that this agent is a complex mixture that exists in equilibrium in aqueous solution.

Antiprotozoal Agents↗

Urinary antimony in infancy.

OBJECTIVE: To determine whether antimony may be detected in the urine during infancy and early childhood and its association with passive exposure to tobacco smoke, as assessed by urinary cotinine. DESIGN: Analysis of spare aliquots of urine collected from infants participating in studies of respiratory function and passive smoking. Urinary antimony was assayed using inductively coupled plasma mass spectroscopy in 201 urine specimens collected at different ages throughout the first two years of life from 122 term and 26 preterm infants. Urinary cotinine was measured using gas liquid chromatography. MAIN OUTCOME MEASURE: Urinary antimony concentrations. RESULTS: Absolute antimony concentrations varied widely between infants, being below the laboratory detection limit of 0.02 microgram/l in 7% of samples, below 0.5 microgram/l in 90.5%, and above the reference value of 1 microgram/l reported for non-occupationally exposed UK populations in 4%. Creatinine standardised antimony values were unrelated to postnatal age or urinary cotinine concentrations and were highest in urine collected from preterm infants within 24 hours of birth (geometric mean (95% confidence interval): 2.3 ng/mg (1.5 to 3.4)). CONCLUSIONS: Although antimony is present at very low concentrations in urine during infancy and early childhood, the relevance to health is uncertain. The higher levels found in preterm infants may reflect prematurity or fetal assimilation of antimony. Tobacco is unlikely to be an important source of environmental exposure to antimony during infancy and early childhood.

Aging↗

Concentrations of antimony in infants dying from SIDS and infants dying from other causes.

OBJECTIVES: Raised concentrations of antimony have been found in infants dying of sudden infant death syndrome (SIDS). The presumed source of this antimony is toxic gases generated from fire retardants that are present in cot mattresses. The aim of this study was to determine the role of antimony in SIDS. DESIGN: Samples of liver, brain, serum, and urine were collected from all patients dying from SIDS and a group of aged matched control infants who had died of other causes. SETTING: Nationwide study in Ireland. SUBJECTS: 52 infants dying from SIDS and 19 control infants aged > 7 days and < 1 year. RESULTS: The median concentration of antimony in the liver and brain of infants dying of SIDS was < 1 ng/g, with no difference detected between the infants dying from SIDS and the control infants. The range of antimony in the serum of infants dying of SIDS was 0.09-0.71 microg/litre (median, 0.26). Although no difference was found between infants dying from SIDS and control infants, SIDS infants were found to have higher concentrations when compared with healthy infants in the 1st year of life, probably as a result of release of antimony into serum after death. Urine antimony concentrations in infants dying from SIDS were < 3.91 ng/mg (corrected for creatinine) and similar to values found both in control infants and healthy infants. CONCLUSION: There is no evidence to support a causal role for antimony in SIDS.

Antimony↗

Antimony leaching from cot mattresses and sudden infant death syndrome (SIDS).

1. Polyvinyl chloride (PVC) cot mattress covers from SIDS cases were investigated as potential sources of soluble (potentially ingestable) antimony in the cot environment. 2. Body fluids (urine, saliva) and proprietary domestic detergents/sterilizing fluids markedly enhanced leaching of antimony from PVC. Release of antimony was also enhanced at both low and high pH and by elevated temperature. The extent of antimony leaching did not correlate well with PVC content of this element. 3. These data do not support the assumption that postmortem analysis of antimony content proves exposure to gaseous antimony trihydride from mattress PVC. 4. Ingestion of antimony released from PVC could account for the high variability associated with reported detectable levels of antimony in liver from both SIDS and other infants. It could also explain suspected additional postnatal exposure to this element, which gives rise to elevated levels of Sb in the hair of some healthy infants.

Antimony↗

[Antimony accumulation in agricultural food crops].

A study was made of the antimony content in some farm products of plant and animal origin in the zones of wastes of antimony factories and those having nothing to do with antimony processing. The content of antimony was discovered to be elevated in all foods obtained in the zone where antimony factories are located, especially in vegetables with ground fruit. A high antimony content was detected in milk. The content of antimony in a "standard" diet calculated on the basis of maximally allowable concentrations of the metal in foods and in analogous diets containing products of plant and animal origin grown in the Fergana and Chuisk valleys was 0.405, 8.585 and 1.702, respectively. The high proportion of vegetables and fruit in the local diets makes them, apart from milk and dairy products, the main sources of antimony supply to the human body.

Animals↗

Glass and antimony electrodes for long-term pH monitoring: a dynamic in vitro comparison.

OBJECTIVE: To compare the performance of combined glass microelectrodes with monocrystalline and polycrystalline antimony electrodes with external reference in a 24-h dynamic in vitro study. DESIGN AND METHODS: In an artificial stomach, the pH of the contents titrated from pH1-7 and back by NaOH and HCI was simultaneously measured at 37 degrees C with antimony and glass probes connected to three recording devices. The recorded data were compared with data monitored continuously by a laboratory pH measurement system. The sensitivity and drift of glass microelectrodes were also analysed in intensive-care unit patients during intragastric pH monitoring for up to 96 h. RESULTS: The sensitivities of antimony polycrystalline, monocrystalline and of glass electrodes were 54.6, 55.3, and 61.8 mV/pH, respectively. The hysteresis was 6.4, 7.2 and 2.75 mV for antimony polycrystalline, monocrystalline and for glass electrodes, respectively. The drift in 24 h was -0.1 pH for glass over the pH range 1-7, and +0.3 pH over pH 1-2.5, and +0.15 pH over pH 2.5-7 for both of the antimony electrodes. The response times of both antimony and glass electrodes were similar over the pH range 2.5-7. The difference in the percentages of time below pH 1.5 was significant: 28.2% for glass, 17.3% for antimony polycrystalline and 18.1% for monocrystalline electrodes, respectively (P < 0.05). However, the difference in the percentages of time below pH 4 was not significant. After 96 h intragastric pH monitoring in six intensive-care unit patients, the mean drift of glass electrodes was 0.15 pH (range, pH 0.1-0.2) and the mean change in sensitivity 1.2%. CONCLUSIONS: (1) Antimony electrodes may be acceptable for intra-oesophageal pH monitoring but are not suitable for intragastric use. (2) The use of glass microelectrodes is recommended for intragastric pH monitoring, particularly when extended monitoring over periods longer than 24 h is required.

Aged↗

Fate of antimony in municipal solid waste incineration.

The average antimony concentration in municipal solid waste is estimated to be about 10-60 ppm. Thermodynamical models predict a volatile behavior for antimony compounds, yet literature mass balances show that about 50% of the antimony input remains in the grate ashes. This fact can be explained by the formation of thermally stable antimonates in the fuel bed due to interactions with alkali or earth-alkali metals. Thermogravimetric experiments revealed an increased thermal stability for antimony oxide in presence of oxygen and calcium oxide. Spiking experiments on the test incinerator TAMARA showed that chlorination processes have a strong effect on antimony volatilization whereas high fuel-bed temperatures and addition of antimony oxide only have a moderate effect. In the grate ashes, antimony shows a pH-depending leaching property, which is typical for anionic species. This fact supports the thesis that antimony is present in the grate ashes in an anionic speciation.

Journal Article↗

Epidemiological, clinical & pharmacological study of antimony-resistant visceral leishmaniasis in Bihar, India.

BACKGROUND & OBJECTIVES: Sodium antimony gluconate (SAG) is reported to be losing its efficacy in Bihar as a first line drug for treatment of visceral leishmaniasis (VL). Concerned with the increasing incidence of antimony-resistant VL patients in Bihar, we undertook an epidemiological, clinical and pharmacological study to formulate a scientific basis for choosing a suitable first line drug for VL. METHODS: Consecutive, fresh and parasitologically confirmed patients of VL from different geographical areas of Bihar were considered for inclusion in the study. Parasites isolated from patients were tested in vitro to assess their response to sodium antimony gluconate (SAG) to 20 microg/ml, response to 20 mg/kg of SAG for 5 days in experimentally induced VL in BALB/c mice from those isolates, and response to SAG in patients treated with SAG for 28 days. Similarly response in culture (1 microg/ml) to amphotericin B (AMB) of all 282 isolates, (1 mg/kg body wt for 20 days) in patients and infected BALB/c mice (1 mg/kg body wt for 5 days) was determined. Antimony levels of plasma were determined at 2, 8 and 24 h after intramuscular injection of SAG. Patients unwilling for SAG treatment or relapsed after SAG treatment and withdrawn from SAG group because of toxicity were treated with AMB. Plasma antimony levels were estimated by atomic absorption spectrometer. RESULTS: Though antimony sensitive and resistant patient were distributed in all 14 districts of Bihar studied, there was a significant variation from district to district. Of the 123 patients included in the SAG treatment group, 19 were withdrawn due to development of toxicity and 2 died; 178 patients were treated with AMB. No patient in AMB group developed any toxicity or died. Only 47 (46%) of 102 patients, 106 (37.6%) of 282 infected macrophages, 90 (52.9%) of 170 experimental infections were cured with SAG. Mc Nemar's test on paired comparisons showed statistical significance difference (P<0.01) between infected macrophage and experimental infection. AMB cured all patients, infected mice and cleared parasites from all isolates. INTERPRETATION & CONCLUSION: Antimony resistant strains of L. donovani were wide spread over different geographical areas in Bihar. SAG cured lesser percentage of VL cases clinically compared to AMB and should be replaced by AMB as a first line drug.

Adult↗

Prenatal and postnatal antimony exposure in rats: effect on vasomotor reactivity development of pups.

Pregnant female rats were exposed to antimony trichloride (0.1 and 1 mg/dl in their drinking water ad libitum) from the first day of pregnancy until weaning (22nd day after delivery). Pups were exposed to antimony trichloride (0.1 and 1 mg/dl in their drinking water ad libitum) from 22nd until 60th day of age. Antimony exposure did not significantly affect maternal and pup systolic arterial blood pressure, length of gestation, and number of newborn per litter. Antimony exposure decreased maternal and pup body weight. No macroscopic teratogenic effects have been observed. Whether or not pups were exposed to antimony trichloride, pressor responses to carotid occlusion and 1-noradrenaline and hypotensive responses to 1-isoprenaline and acetylcholine were significantly higher on the 60th than on the 30th day of age. In pups, prenatal and postnatal antimony exposure did not affect pressor response to carotidal occlusion, while it decreased pressor response to 1-noradrenaline and hypotensive response to 1-isoprenaline on the 60th day after birth. At last, antimony exposure at higher concentration decreased pup hypotensive response to acetylcholine on the 60th day.

Animals↗

Antimony distribution and mobility in topsoils and plants (Cytisus striatus, Cistus ladanifer and Dittrichia viscosa) from polluted Sb-mining areas in Extremadura (Spain).

A study about topsoil antimony distribution and mobility from the soils to the biomass has been afforded in three abandoned Sb mining areas located at Extremadura. Physico-chemical characteristics of the soils and total antimony levels were measured in soils and autochthonous plant species (Cytisus striatus, Cistus ladanifer and Dittrichia viscosa). Comparison with corresponding values in reference areas isolated from the mining activities is discussed. Antimony mobility in the soils was estimated by measuring the water extractable fraction; low results were obtained for the three soil areas, with no statistical differences. Plant ability to accumulate antimony was estimated by use of plant accumulation coefficients (PAC). Seasonal (spring vs. autumn) effects on the antimony content in the plant species. Cytisus striatus from Mari Rosa mine presented antimony excluder characteristics, whereas Dittrichia viscosa specimens growing in San Antonio mine showed a significant antimony bioaccumulation.

Antimony↗