A C?As lyase for degradation of environmental organoarsenical herbicides and animal husbandry growth promoters

Arsenic is the most widespread environmental toxin. Substantial amounts of pentavalent organoarsenicals have been used as herbicides, such as monosodium methylarsonic acid (MSMA), and as growth enhancers for animal husbandry, such as roxarsone (4-hydroxy-3-nitrophenylarsonic acid) [Rox(V)]. These undergo environmental degradation to more toxic inorganic arsenite [As(III)]. We previously demonstrated a two-step pathway of degradation of MSMA to As(III) by microbial communities involving sequential reduction to methylarsonous acid [MAs(III)] by one bacterial species and demethylation from MAs(III) to As(III) by another. In this study, the gene responsible for MAs(III) demethylation was identified from an environmental MAs(III)-demethylating isolate, Bacillus sp. MD1. This gene, termed arsenic inducible gene (arsI), is in an arsenic resistance (ars) operon and encodes a nonheme iron-dependent dioxygenase with C⋅As lyase activity. Heterologous expression of ArsI conferred MAs(III)-demethylating activity and MAs(III) resistance to an arsenic-hypersensitive strain of Escherichia coli, demonstrating that MAs(III) demethylation is a detoxification process. Purified ArsI catalyzes Fe²⁺-dependent MAs(III) demethylation. In addition, ArsI cleaves the C⋅As bond in trivalent roxarsone and other aromatic arsenicals. ArsI homologs are widely distributed in prokaryotes, and we propose that ArsI-catalyzed organoarsenical degradation has a significant impact on the arsenic biogeocycle. To our knowledge, this is the first report of a molecular mechanism for organoarsenic degradation by a C⋅As lyase.The metalloid arsenic is the most common environmental toxic substance, entering the biosphere primarily from geochemical sources, but also through anthropogenic activities (1). Arsenic is a group 1 human carcinogen that ranks first on the Agency for Toxic Substances and Disease Registry Priority List of Hazardous Substances (www.atsdr.cdc.gov/SPL/index.html). Microbial arsenic transformations create a global arsenic biogeocycle (1). These biotransformations include redox cycles between the relatively innocuous pentavalent arsenate and the considerably more toxic and carcinogenic trivalent arsenite (2, 3). In addition, many microbes, both prokaryotic and eukaryotic, have arsM genes for inorganic arsenite [As(III)] S-adenosylmethionine methyltransferases that methylate inorganic As(III) to mono-, di-, and tri-methylated species (4, 5). The genes encoding arsenic transforming enzymes are widely distributed, and these arsenic biotransformations have been proposed to play significant roles in the arsenic biogeocycle and in remodeling the terrain in volcanic areas such as Yellowstone National Park and regions of the world with high amounts of arsenic in soil and water such as West Bengal and Bangladesh (3, 6).Arsenicals, both inorganic and organic, have been used in agriculture in the United States for more than a century (7). Historically, the use of inorganic arsenical pesticides/herbicides has been largely replaced by methylated arsenicals such as monosodium methylarsonic acid (MSMA), which is still in use as an herbicide for turf maintenance on golf courses, sod farms, and highway rights of way, and for weed control on cotton fields (7). More complex pentavalent aromatic arsenicals such as roxarsone [4-hydroxy-3-nitrophenylarsonic acid, Rox(V)] have been largely used since the middle of the 1940s as antimicrobial growth promoters for poultry and swine to control Coccidioides infections and improve weight gain, feed efficiency, and meat pigmentation (8, 9). These aromatic arsenicals are largely excreted unchanged and introduced into the environment when chicken litter is applied to farmland as fertilizer (8). Pentavalent organoarsenicals are relatively benign and less toxic than inorganic arsenicals; however, aromatic (8–10) and methyl (11, 12) arsenicals are degraded into more toxic inorganic forms in the environment, which may contaminate the foods and water supplies. Although microbial degradation of environmental organoarsenicals has been documented (8, 9, 11, 13), no molecular details of the reaction have been reported. We recently demonstrated that a microbial community in Florida golf course soil carries out a two-step pathway of MSMA reduction and demethylation (14). Here we report the isolation of an environmental methylarsonous acid [MAs(III)]-demethylating bacterium Bacillus sp. MD1 (for “MAs(III) demethylating”) from Florida golf course soil and the cloning of the gene, termed arsenic inducible gene (arsI), responsible for MAs(III) demethylation. The gene product, ArsI, is nonheme iron-dependent dioxygenase with C⋅As lyase activity. ArsI cleaves the C⋅As bond in a wide range of trivalent organoarsenicals, including the trivalent roxarsone [Rox(III)], into As(III), which strongly suggests that the environmental pentavalent phenylarsenicals such as Rox(V) also undergo a two-step pathway of sequential reduction and ArsI-catalyzed dearylation, in analogy with the demethylation of MSMA by a microbial community. Thus, ArsI-catalyzed C⋅As bond cleavage is a newly identified mechanism for degradation of organoarsenical herbicides and antimicrobial growth promoters.     

Impaired regulatory T cell reconstitution in patients with acute graft-versus-host disease and cytomegalovirus infection after allogeneic bone marrow transplantation

To elucidate the correlation between regulatory T cells (Tregs) and acute graft-versus-host disease (aGVHD) or cytomegalovirus infection following allogeneic bone marrow transplantation (allo-BMT), we evaluated either CD4?CD25(high) or FOXP3? Treg-enriched cells in peripheral blood (PB) from 20 patients who received allo-BMT, and in biopsies of skin with aGVHD. Proportions of CD4?CD25(high)FOXP3? cells in total lymphocytes, but not other types of T cells, were lower in patients who eventually developed grades II-IV aGVHD (n = 13) than in others (n = 7, P < 0.001). Proportions of CD62L? cells in CD4?CD25(high) cells at day +30 were lower (P < 0.01) in patients who eventually showed cytomegalovirus viremia (n = 6) than in others (n = 14). Incidence of aGVHD (P < 0.05) or cytomegalovirus viremia (P < 0.05) was higher in patients without these complications, but with lower proportions of PB CD4?CD25(high)FOXP3? cells at day +30 (n = 8) than in others (n = 8). However, in skin with aGVHD (n = 5), there was marked or slightly increased infiltration of CD8? cells (P < 0.001) or CD3?FOXP3? cells (P < 0.05), respectively, when compared with control (n = 5), resulting in threefold higher ratio of CD8?/CD3?FOXP3? cells in aGVHD relative to controls (P < 0.05). Thus, impaired reconstitution of Tregs may be associated with aGVHD and CMV infection. Moreover, imbalance of Tregs and CD8? cells may play a role in aGVHD tissue.