The human bladder is one of the primary target organs for arsenic-induced carcinogenicity, and arsenic metabolites in urine have been suspected to be directly involved in carcinogenesis. Thioarsenicals are commonly found in human and animal urine and are also considered to be highly toxic arsenic metabolites. The present study was performed to gain insight into the toxicity and accumulation of arsenic species found in urine, including arsenate (iAs(V)), arsenite (iAs(III)), monomethylarsonic acid (MMA(V)), monomethylmonothioarsonic acid (MMMTA(V)), dimethylarsinic acid (DMA(V)), dimethylarsinous acid (DMA(III)), dimethylmonothioarsinic acid, (DMMTA(V)), and dimethyldithioarsinic acid (DMDTA(V)) in human bladder cancer EJ-1 cells. The order of cytotoxicity of these arsenic compounds in EJ-1 human bladder cancer cells was DMA(III), DMMTA(V) > iAs(III) ≫ iAs(V) > MMMTA(V) > MMA(V), DMA(V), and DMDTA(V), indicating that the sulfur-containing DMMTA(V) was among the most toxic arsenic compounds similar to trivalent DMA(III). We further characterized the DNA damage, generation of highly reactive oxygen species (hROS), and expression of proteins p21 and p53 in cells after exposure to iAs(III), DMA(III), and DMMTA(V). Cellular exposure to DMMTA(V) resulted in reduced protein expression of p53 and p21, increased DNA damage, and increased intracellular hROS (hydroxyl radical). In contrast, iAs(III) significantly increased the protein expression of p21 and p53 and did not increase the hROS at the IC(50). Intracellular glutathione (GSH) was reduced by 60% after exposure to DMA(III) or DMMTA(V), suggesting that DMMTA(V) causes cell death through oxidative stress. In contrast, GSH levels increased in cells exposed to iAs(III), and hROS only increased after a long exposure to iAs(III). Our findings demonstrate that DMMTA(V) may be one of the most toxicologically potent arsenic species, relevant to arsenic-induced carcinogenicity in the urinary bladder.

Hundreds of millions of people worldwide are exposed to unacceptable levels of arsenic in drinking water. This is a public health crisis because arsenic is a Group I (proven) human carcinogen. Human cells methylate arsenic to monomethylarsonous acid (MMA . Although the liver is the predominant site for arsenic methylation, elimination occurs mostly in urine. The protein(s) responsible for transport of arsenic from the liver (into blood), ultimately for urinary elimination, are unknown. Human multidrug resistance protein 1 (MRP1/ABCC1) and MRP2 (ABCC2) are established arsenic efflux pumps, but unlike the related MRP4 (ABCC4) are not present at the basolateral membrane of hepatocytes. MRP4 is also found at the apical membrane of renal proximal tubule cells, making it an ideal candidate for urinary arsenic elimination. V were the transported species. MMA(GS) 2 and DMA V transport was osmotically sensitive, allosteric (Hill coefficients of 1.4 6 0.2 and 2.9 6 1.2, respectively), and high affinity (K 0.5 of 0.70 6 0.16 and 0.22 6 0.15 mM, respectively). DMA V transport was pH-dependent, with highest affinity and capacity at pH 5.5. These results suggest that human MRP4 could be a major player in the elimination of arsenic.

ABSTRACT:The ATP-binding cassette (ABC) transporter protein multidrug resistance protein 1 (MRP1; ABCC1) plays an important role in the cellular efflux of the high-priority environmental carcinogen arsenic as a triglutathione

Simultaneous exposure of lab animals to toxic doses of the human carcinogen arsenic (As) and the essential trace element selenium (Se) results in a remarkable mutual detoxification. A likely basis for this is the in vivo formation and biliary excretion of seleno-bis(S-glutathionyl) arsinium ion [(GS)(2)AsSe](-); however, the transport protein responsible for the biliary efflux of [(GS)(2)AsSe](-) has not been identified. The multidrug resistance protein 2 (MRP2/ABCC2) is an adenosine triphosphate (ATP)-binding cassette transporter expressed at the canalicular membrane of hepatocytes. Rat Mrp2 is known to excrete the As glutathione (GSH/GS-) conjugates arsenic triglutathione [As(GS)(3)] and monomethyl arsenic diglutathione [CH(3)As(GS)(2)] into bile, and in vitro studies have established As(GS)(3) as a substrate for human MRP2. In the present study, membrane vesicles prepared from human embryonic kidney (HEK293T) cells transfected with human MRP2 were used to demonstrate that MRP2 transports [(GS)(2)AsSe](-). In addition, the characteristics of MRP2 transport of As(GS)(3) and [(GS)(2)AsSe](-) were investigated. As(GS)(3) and [(GS)(2)AsSe](-) are chemically labile and have the potential to dissociate. However, arsenite (As(III)) +/- selenite (Se(IV)) transport was not detected in the absence of GSH or in the presence of the non-reducing GSH analog, ophthalmic acid, suggesting that the conjugates are the transported forms. The apparent K(m) values for [(GS)(2)AsSe](-) and As(GS)(3) were 1.7 and 4.2 microM, respectively, signifying high relative affinities. Membrane vesicles prepared from human erythrocytes, which express the MRP2-related MRP1/ABCC1, MRP4/ABCC4 and MRP5/ABCC5, transported As(GS)(3) in an MRP1- and ATP-dependent manner but did not transport [(GS)(2)AsSe](-). These results have important implications for the Se-dependent and -independent disposition of As.

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