Monophthalates promote IL-6 and IL-8 production in the human epithelial cell line A549.

The dramatically increasing prevalence of allergic respiratory diseases may in part be due to the presence of certain immunotoxic xenobiotics in the environment. Recent studies have suggested that some plasticizers belonging to the phthalate family, and metabolites thereof, play a role in the development of allergic respiratory diseases. This is probably due to an adjuvant effect, which in some cases may be combined with an inflammatory process. The scope of the present study was to investigate the inflammatory potential of monophthalates, which are degradation products of phthalate plasticizers. The human epithelial cell line A549 was exposed to 15.6-2000 microg/ml, in two-fold dilutions, to either mono-n-butyl phthalate, monobenzyl phthalate, mono-n-octyl phthalate, mono-2-ethylhexyl phthalate, mono-iso-nonyl phthalate or mono-iso-decyl phthalate. Concentrations of the proinflammatory cytokines IL-6 and IL-8 were measured in the cell culture supernatant by ELISA. The study showed that some, but not all, monophthalates could induce a concentration-dependent increase in cytokine production, whereas, at higher concentrations, all phthalates suppressed cytokine production. Both the stimulatory and the suppressive properties were highly dependent on the length of the alkyl side chain of the monophthalate - a structure-activity relationship that is supported by recent observations in mice.

[Acute arsenic poisoning]. / Akut arsenforgiftning.

We report three cases of arsenic poisoning in a chemical factory. Three workers were exposed to vinyzene 10,10'-oxydephenarsine and developed mild symptoms of acute poisoning. All patients were treated with dimercaprol, and recovered after a few days. Urine analysis did not show increased arsenic excretion, but this could be due to the large urine samples taken. It is recommended that a urine sample is taken right after admission to hospital and new samples after eight and 16 hours.

Studies of serum protein complexes with nickel using crossed immunoelectrophoresis.

Crossed immunoelectrophoresis of human serum spiked with nickel in the range 0.85-24 mmol Ni/L was used to study nickel-protein complexes. These high concentrations, which are far higher than the physiological level (approximately 7.8 nmol/L), were used to saturate both high and low affinity binding sites. Addition of increasing amounts of nickel resulted in dose-dependent changes of the electrophoretic patterns of prealbumin, alpha-1-lipoprotein, alpha-1-antitrypsin and alpha-2-macroglobulin. Radioactive 63Ni was used for crossed immunoelectrophoresis autoradiography experiments for further identification of nickel-protein complexes. When a 63Ni pulse of 740 kBq/application was used, many human serum proteins were labeled. When using a 63Ni pulse of 185 kBq/application only albumin and alpha-1-antitrypsin were visualized clearly. The binding of large amounts of nickel to albumin, visualized by autoradiography, may reflect the high abundance of albumin in human serum as compared to other serum proteins. Addition of nickel to serum proteins resulted in liquid phase precipitation of serum proteins, and rocket immunoelectrophoresis was used to demonstrate that IgG in particular is precipitated. This precipitation of serum proteins may disturb the elution profile when chromatographic techniques are used to analyze nickel-protein complexes. Consequently, immunoelectrophoretic methods may also be attractive alternatives to column chromatographic techniques. The present study demonstrated that, besides the nickel-binding of albumin and alpha-2-macroglobulin, several other serum proteins have nickel-binding affinity.

Estimation of the method evaluation function for the determination of hydride-generating arsenic compounds in urine by flow-injection atomic-absorption spectrometry.

A direct flow-injection atomic-absorption spectrometric (FIA-AAS) method for the assessment of inorganic arsenic compounds and their metabolites was developed and statistically evaluated by the estimation of the method evaluation function (MEF), which provides detailed information on the analytical performance of the method, i.e., the average combined uncertainty and the magnitude of potential systematic errors. The method evaluation study demonstrated that the use of standard addition was a necessity to obtain an acceptable method performance at low concentrations typical for low dose exposure. In contrast the use of calibration curves resulted in a method with reduced sensitivity and high systematic error. The developed method, using standard addition, had a limit of detection (2.9 microg/l.) sufficiently low for the determination of hydride-generating arsenic species in urine from non-exposed and low exposed persons. Organoarsenicals such as arsenobetaine and arsenocholine are not detected by this method. Hence, the contribution of these compounds derived from a diet containing seafood does not affect the monitoring of inorganic arsenic compounds after occupational or environmental exposure. The high capacity of the FIA-AAS system (three minutes per sample measured by standard addition) together with the low limit of detection makes this method suitable for biological monitoring of inorganic arsenic exposure even though standard addition is required.

Effect of seafood consumption on the urinary level of total hydride-generating arsenic compounds. Instability of arsenobetaine and arsenocholine.

Arsenobetaine and arsenocholine are considered to be non-toxic and are present as a relatively large proportion of total arsenic in seafoods, and they do not respond to hydride generation. The present study describes the effect of seafood consumption on the urinary concentration of hydride-generating arsenic compounds measured by a newly developed flow injection atomic absorption spectrometric (FI-AAS) method. Consumption of plaice, pighvar and tunny resulted in a 2-fold increase, and consumption of mussels produced a 6-fold increase in the urinary level of hydride-generating arsenic compounds. Hence, a person who has consumed mussels may be suspected of being occupationally or environmentally exposed, if the level of consumption of this seafood is unknown. As the FI-AAS method cannot be used to detect arsenobetaine and arsenocholine, the observed increase in urinary concentration of hydride-generating arsenic compounds after consumption of seafood must originate either from hydride-generating arsenic compounds in the seafood or from degraded arsenobetaine or arsenocholine. The present study has demonstrated that both arsenobetaine and arsenocholine are unstable when incubated in daylight in the presence of hydrogen peroxide, i.e., an oxidizing environment. Hence, it is tempting to speculate that arsenobetaine could be converted into hydride-generating arsenic compounds during storage or cooking of seafood. The feasibility of speciation methods based on high-performance liquid chromatographic (HPLC) separation and on-line analysis by inductively coupled plasma atomic emission spectrometry (ICP-AES) and FI-AAS was also investigated. The FI-AAS system is approximately 35 times more sensitive to the hydride-generating arsenic species than the ICP-AES system.(ABSTRACT TRUNCATED AT 250 WORDS)