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[
Nucleic Acids Res,
2002]
Caenorhabditis elegans mitochondria have two elongation factor (EF)-Tu species, denoted EF-Tu1 and EF-Tu2. Recombinant nematode EF-Ts purified from Escherichia coli bound both of these molecules and also stimulated the translational activity of EF-Tu, indicating that the nematode EF-Ts homolog is a functional EF-Ts protein of mitochondria. Complexes formed by the interaction of nematode EF-Ts with EF-Tu1 and EF-Tu2 could be detected by native gel electrophoresis and purified by gel filtration. Although the nematode mitochondrial (mt) EF-Tu molecules are extremely unstable and easily form aggregates, native gel electrophoresis and gel filtration analysis revealed that EF-Tu.EF-Ts complexes are significantly more soluble. This indicates that nematode EF-Ts can be used to stabilize homologous EF-Tu molecules for experimental purposes. The EF-Ts bound to two eubacterial EF-Tu species (E.coli and Thermus thermophilus). Although the EF-Ts did not bind to bovine mt EF-Tu, it could bind to a chimeric nematode-bovine EF-Tu molecule containing domains 1 and 2 from bovine mt EF-Tu. Thus, the nematode EF-Ts appears to have a broad specificity for EF-Tu molecules from different
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[
Structure,
2002]
Elongation factor EF-Tu is a key component in the translation step of protein synthesis, where it forms a complex with amino-acyl tRNA and delivers it to the ribosome. Until now, none of the known EF-Tu molecules have discriminated between the different species of tRNA, but now a new discovery sheds light on a curious EF-Tu homolog that binds just a single tRNA species.
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[
Nat Struct Biol,
2002]
The translation elongation factor Tu (EF-Tu) delivers aminoacyl-tRNAs to ribosomes by recognizing the tRNA acceptor and T stems. However, the unusual truncation observed in some animal mitochondrial tRNAs seems to prevent recognition by a canonical EF-Tu. For instance, nematode mitochondria contain tRNAs lacking a T or D arm. We recently found an atypical EF-Tu (EF-Tu1) specific for nematode mitochondrial tRNAs that lack the T arm. We have now discovered a second factor, EF-Tu2, which binds only to tRNAs that lack a D arm. EF-Tu2 seems unique in its amino acid specificity because it recognizes the aminoacyl moiety of seryl-tRNAs and the tRNA structure itself. Such EF-Tu evolution might explain tRNA structural divergence in animal mitochondria.
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[
J Biol Chem,
2001]
We have found the gene for a translation elongation factor Tu (EF-Tu) homologue in the genome of the nematode Caenorhabditis elegans. Because the corresponding protein was detected immunologically in a nematode mitochondrial (mt) extract, it could be regarded as a nematode mt EF-Tu. The protein possesses an extension of about 57 amino acids (we call this domain 3') at the C terminus, which is not found in any other known EF-Tu. Because most nematode mt tRNAs lack a T stem, domain 3' may be related to this feature. The nematode EF-Tu bound to nematode T stem-lacking tRNA, but bacterial EF-Tu was unable to do so. A series of domain exchange experiments strongly suggested that domains 3 and 3' are essential for binding to T stem-lacking tRNAs, This finding may constitute a novel example of the co-evolution of a structurally simplified RNA and the cognate RNA-binding protein, the latter having apparently acquired an additional domain to compensate for the lack of a binding site(s) on the RNA.
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[
Biochemistry,
2006]
In canonical translation systems, the single elongation factor Tu (EF-Tu) recognizes all elongator tRNAs. However, in Caenorhabditis elegans mitochondria, two distinct EF-Tu species, EF-Tu1 and EF-Tu2, recognize 20 species of T armless tRNA and two species of D armless tRNA(Ser), respectively. We previously reported that C. elegans mitochondrial EF-Tu2 specifically recognizes the serine moiety of serylated-tRNA. In this study, to identify the critical residues for the serine specificity in EF-Tu2, several residues in the amino acid binding pocket of bacterial EF-Tu were systematically replaced with corresponding EF-Tu2 residues, and the mutants were analyzed for their specificity for esterified amino acids attached to tRNAs. In this way, we obtained a bacterial EF-Tu mutant that acquired serine specificity after the introduction of 10 EF-Tu2 residues into its amino acid binding pocket. C. elegans EF-Tu2 mutants lacking serine specificity were also created by replacing seven or eight residues with bacterial residues. Further stressing the importance of these residues, we found that they are almost conserved in EF-Tu2 sequences of closely related nematodes. Thus, these three approaches reveal the critical residues essential for the unique serine specificity of C. elegans mitochondrial EF-Tu2.
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[
Biochem J,
2006]
Nematode mitochondria possess extremely truncated tRNAs. Twenty of 22 tRNAs lack the entire T-arm. The T arm is necessary for the binding of canonical tRNAs and elongation factor (EF)-Tu. The nematode mitochondrial translation system employs two different EF-Tu factors named EF-Tu1 and EF-Tu2. Our previous study showed that nematode Caenorhabditis elegans EF-Tu1 binds specifically to T-armless tRNA. C. elegans EF-Tu1 has a 57-amino acid C-terminal extension that is absent from canonical EF-Tu, and the T-arm binding residues of canonical EF-Tu are not conserved. In this study, the recognition mechanism of T-armless tRNA by EF-Tu1 was investigated. Both modification interference assays and primer extension analysis of cross-linked ternary complexes revealed that EF-Tu1 interacts not only with the tRNA acceptor stem but also with the D arm. This is the first example of an EF-Tu recognizing the D-arm of a tRNA. The binding activity of EF-Tu1 was impaired by deletion of only 14 residues from the C-terminus, indicating that the C-terminus of EF-Tu1 is required for its binding to T-armless tRNA. These results suggest that C. elegans EF-Tu1 recognizes the D-arm instead of the T-arm by a mechanism involving its C-terminal region. This study sheds light on the co-evolution of RNA and RNA-binding proteins in nematode mitochondria.
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[
Nucleic Acids Res,
2005]
Nematode mitochondria expresses two types of extremely truncated tRNAs that are specifically recognized by two distinct elongation factor Tu (EF-Tu) species named EF-Tu1 and EF-Tu2. This is unlike the canonical EF-Tu molecule that participates in the standard protein biosynthesis systems, which basically recognizes all elongator tRNAs. EF-Tu2 specifically recognizes Ser-tRNA(Ser) that lacks a D arm but has a short T arm. Our previous study led us to speculate the lack of the D arm may be essential for the tRNA recognition of EF-Tu2. However, here, we showed that the EF-Tu2 can bind to D arm-bearing Ser-tRNAs, in which the D-T arm interaction was weakened by the mutations. The ethylnitrosourea-modification interference assay showed that EF-Tu2 is unique, in that it interacts with the phosphate groups on the T stem on the side that is opposite to where canonical EF-Tu binds. The hydrolysis protection assay using several EF-Tu2 mutants then strongly suggests that seven C-terminal amino acid residues of EF-Tu2 are essential for its aminoacyl-tRNA-binding activity. Our results indicate that the formation of the nematode mitochondrial (mt) EF-Tu2/GTP/aminoacyl-tRNA ternary complex is probably supported by a unique interaction between the C-terminal extension of EF-Tu2 and the tRNA.
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Schmitt C, Streck G, de Zwart D, Tuikka AI, Brix R, de Deckere E, Kocan A, Hoss S, Sormunen AJ, Mothes S, von der Ohe PC, Barcelo D, van Hattum B, Bandow N, Kukkonen JV, Brack W
[
Ecotoxicol Environ Saf,
2011]
The toxicity of four polluted sediments and their corresponding reference sediments from three European river basins were investigated using a battery of six sediment contact tests representing three different trophic levels. The tests included were chronic tests with the oligochaete Lumbriculus variegatus, the nematode Caenorhabditis elegans and the mudsnail Potamopyrgus antipodarum, a sub-chronic test with the midge Chironomus riparius, an early life stage test with the zebra fish Danio rerio, and an acute test with the luminescent bacterium Vibrio fischeri. The endpoints, namely survival, growth, reproduction, embryo development and light inhibition, differed between tests. The measured effects were compared to sediment contamination translated into toxic units (TU) on the basis of acute toxicity to Daphnia magna and Pimephales promelas, and multi-substance Potentially Affected Fractions of species (msPAF) as an estimate for expected community effects. The test battery could clearly detect toxicity of the polluted sediments with test-specific responses to the different sediments. The msPAF and TU-based toxicity estimations confirmed the results of the biotests by predicting a higher toxic risk for the polluted sediments compared to the corresponding reference sediments, but partly having a different emphasis from the biotests. The results demonstrate differences in the sensitivities of species and emphasize the need for data on multiple species, when estimating the effects of sediment pollution on the benthic community.
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Bandow N, Munoz I, Tuikka A, Lopez Doval JC, Wolfram G, Van Liefferinge C, Schmitt C, Leloup V, Adamek Z, Orendt C, Hoss S, GroBschartner M, von der Ohe PC, Kukkonen JV, Traunspurger W, de Deckere E
[
Sci Total Environ,
2012]
The aim of this study was to combine different lines of evidence on the impact of chemical pollution on benthic invertebrate communities in three European river basins (Elbe, Scheldt, and Llobregat). The study integrates chemical analyses, a battery of different sediment toxicity tests, and field data from soft-sediment meio- and macrobenthic fauna within a sediment-quality triad in which chironomids, oligochaetes, and nematodes are identified on the species level. The use of TU (toxic units) and msPAF (multi-substance potentially affected fraction) in an approach assessing the chemical impact as well as the integration of sediment toxicity tests with bacteria (Vibrio fischeri), benthic invertebrates (Caenorhabditis elegans, Potamopyrgus antipodarum, Lumbriculus variegatus, Chironomus riparius), and fish embryos (Danio rerio), together with univariate and non-parametric multivariate statistical analyses of the biological data revealed significant differences between unpolluted and polluted sites in all three river basins. To combine the different results obtained in the sediment-quality triad, a scoring system was successfully developed based on a simple algorithm. This system provides an easily understandable scheme for non-experts among decision makers and water managers.