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The product of the POUSF1 gene, Oct4, plays an important role both in embryonic development and in the self-renewal and differentiation of totipotent cells. To understand the function of Oct4 in rabbit ES cells, we cloned and sequenced the rabbit POU5F1 gene, as well as the cDNA encoded by the gene. The Oct4 cDNA contains a 1083 bp ORF encoding a 360 aa protein and a 241 bp 3' UTR sequence. Oct4 mRNA was expressed at a high level in rabbit ES cells and was barely detectable in the adult spleen, kidney, brain and muscle tissues. The POU5F1 gene is approximately 6 kb in length and includes five exons and four introns. Gene organization is similar to that of the mouse, human and bovine orthologs. Sequencing of the gene revealed an 82% (mouse), 90% (human) and 89% (bovine) overall identity at the protein level. The rabbit POUSF1 gene was mapped to chromosome 12q1.1 by PCR amplification of DNA from two putative POU5F1-containing BAC clones, which were previously mapped to chromosome 12q1.1. The cloning of the rabbit POU5F1 gene will facilitate studies on its roles in rabbit embryogenesis and ES cells.

This paper proposed an innovative approach by stepwise moving anode towards cathode to enhance the cadmium (Cd) removal from soil during the process of electrokinetic (EK) remediation. Fixed anode tests and moving anode tests were carried out for 60 hours to compare their performances. The anode-cathode spacing was 21 cm. Constant voltage grade of 1.0 V cm(-1) was applied in this study. The parameters included pH, electrical conductivity, current, Cd concentration and speciation distributions, energy consumptions, etc. It was found that the pH values in the moving anode tests were relatively lower than those of the fixed tests. In the moving anode test, the removal efficiency of Cd in the soils at the fraction of S4 was enhanced by 54.9% compared with that of the fixed anode tests. After 60 hours of treatment, approximately 80% of the spiked soils (100.63 mg x kg(-1) of Cd) in the system were successfully remedied in the moving anode tests; and the mean removal efficiency was 73% for actual field-contaminated soil (54.26 mg x kg(-1) of Cd). It is effective to remedy actual contaminated soils. In addition, the cumulative energy consumptions were 59.29 kWhm(-3) and 31.52 kWhm(-3) for the fixed and moving tests, respectively. The results revealed that the Cd removal efficiency was improved by the moving anode method. Moreover, less energy was consumed in the moving test. The proposed approach does not need to introduce extra chemicals nor adjust the pH in the system to enhance the Cd removal by EK remediation. The basic idea proposed in this paper provides a novel and environmental friendly method to enhance the EK remediation of heavy metals contaminated soils.