Cadmium is highly toxic to almost all forms of life. It is released into the environment through natural and anthropogenic activities. Natural sources originate from volcanic activity, forest fires, fossil fuel burning, and soil particles contaminated with cadmium (Joseph, 2009). Cadmium is extensively used in industries such as nickel-cadmium battery manufacturing, electroplating, welding, smelting and refining, pigments, and plastic stabilizers (Joseph, 2009). Inhalation through occupational exposure, cigarette smoking, and indoor inhalable particles contaminated with cadmium is one of the main routes of exposure to cadmium in humans, with more than 90% of a dose being absorbed through the lung after inhalation of cadmium (Nawrot et al., 2010; Waalkes, 2003). Both epidemiological and experimental studies have identified cadmium as a lung carcinogen in humans (IARC, 2012). Due to persistence in the environment and a long biological half-life in humans, cadmium has always been a serious public health concern. Even though much work has been carried out to elucidate the molecular mechanisms of cadmium-induced carcinogenesis, the exact mechanisms still remain unclear. The ability of cadmium to induce gene mutations in bacteria was limited (Beyersmann and Hartwig, 1994), and no clear association between cadmium exposure and cytogenetic endpoint in humans has been found (Verougstraete et al., 2002), both of which implied that cadmium-induced carcinogenesis may be mediated through nongenotoxic or indirect genotoxic mechanisms (Beyersmann and Hechtenberg, 1997; Bolognesi et al., 1999). It has been proposed that epigenetic mechanisms may play a role in cadmium-induced carcinogenesis (Waalkes, 2003). Over the last decade or two, accumulating evidences have shown that cadmium is able to alter DNA methylation both at the global and gene-specific levels, which may play a role in carcinogenesis. Takiguchi et al. (2003) reported that after 10 weeks of exposure to cadmium, TRL1215 rat liver cells showed indications of transformation and significant increases in genomic DNA methylation and DNA methyltransferase (DNMT) activity. In cadmium-transformed human prostate epithelial RWPE-1 cells, the tumor suppressor genes RASSF1A and p16 were inactivated due to DNA hypermethylation at their promoter regions (Benbrahim-Tallaa et al., 2007). Another study showed that chronic exposure to cadmium in human embryo lung fibroblast cells resulted in increases in global DNA methylation and DNMTs activities (Jiang et al., 2008). A recent study reported that in cadmium-transformed human bronchial epithelial (16HBE) cells, global DNA methylation, and DNA methylation at the promoter regions of DNA repair genes (hMSH2, ERCC1, XRCC1, and hOGG1) were increased (Zhou et al., 2012). These findings suggested that cadmium disrupts DNA methylation, which may be involved in cadmium-induced carcinogenesis. To date, much of the work has been focused on DNA methylation. Whether cadmium induces aberrant histone methylation has yet to be investigated. In general, DNA methylation may act as a template for some histone modifications following DNA replication but more likely histone methylation can aid in directing DNA methylation patterns (Cedar and Bergman, 2009). Therefore, it’s likely that cadmium is able to induce aberrant histone methylation. Histone H3 on lysine 4 (H3K4) and H3K9 are the regular sites of lysine methylations, both of which can be mono-, di-, or trimethylated. In general, trimethylated H3K4 (H3K4me3) is always found at the promoter regions of transcriptionally activated genes (Santos-Rosa et al., 2002), whereas dimethylated H3K9 (H3K9me2) is located in the regulatory regions of transcriptionally silent genes (Rice et al., 2003). Aberrant modifications of H3K4me3 and H3K9me2 have been found to be closely associated with carcinogenesis. H3K4me3 has been found to be increased at the promoter region of MT-3 in cadmium-transformed human urothelial cells compared with that in parental human urothelial cells (Somji et al., 2011). Activation of H3K4me3 has also been found to be associated with overexpression of LAMB3 and LAMC2 genes in gastric cancer cell line, which may play an important role in gastric carcinogenesis (Kwon et al., 2011). Gain of H3K9me2 has been observed in silencing RASSF1A in prostate cancer (Kawamoto et al., 2007). However, to the best of our knowledge, no one has investigated the effects of cadmium on global H3K4me3 and H3K9me2 and their potential roles in cadmium-induced carcinogenesis. In this present study, we investigated the effects of cadmium on global H3K4me3 and H3K9me2 in immortalized normal human bronchial epithelial (BEAS-2B) cells and whether histone demethylases played a role in cadmium-induced histone modifications. BEAS-2B cells are similar to normal human lung cells in characteristics and cellular responses to carcinogens (Jing et al., 2012; Son et al., 2012; Wang et al., 2011), thus they are often used to establish the model of cell transformation. Since cell transformation assay is considered as a predictive test for carcinogenicity (Barrett et al., 1984), we further studied whether cadmium modulated global H3K4me3 and H3K9me2 during cadmium-induced transformation of BEAS-2B cells. Our work would further contribute to the understanding of the mechanisms of cadmium-induced carcinogenesis.