Novel modular domain PB1 recognizes PC motif to mediate functional protein-protein interactions

Modular domains mediating specific protein-protein interactions play central roles in the formation of complex regulatory networks to execute various cellular activities. Here we identify a novel domain PB1 in the budding yeast protein Bem1p, which functions in polarity establishment, and mammalian p67(phox), which activates the microbicidal phagocyte NADPH oxidase. Each of these specifically recognizes an evolutionarily conserved PC motif to interact directly with Cdc24p (an essential protein for cell polarization) and p40(phox) (a component of the signaling complex for the oxidase), respectively. Swapping the PB1 domain of Bem1p with that of p67(phox), which abolishes its interaction with Cdc24p, confers on cells temperature- sensitive growth and a bilateral mating defect. These phenotypes are suppressed by a mutant Cdc24p harboring the PC motif-containing region of p40(phox), which restores the interaction with the altered Bem1p. This domain-swapping experiment demonstrates that Bem1p function requires interaction with Cdc24p, in which the PB1 domain and the PC motif participate as responsible modules.     

Kinetic evidence for tandemly arranged ligand binding sites in melanocortin 4 receptor complexes

The melanocortin 4 receptor (MC(4)R) binding of the peptide analogue of melanocyte stimulating hormone, [(125)I]NDP-MSH, and the low molecular weight radionucleid 1-(D-1,2,3,4-tetrahydroisoquinoline-3-carboxy-D-4-(125)iodophenylalanyl)-4-cyclohexyl-4-[(1,2,4-triazol-1-yl)methyl]piperidine trifluoroacetate ([(125)I]THIQ) were compared. Kinetic analysis indicated heterogeneity in the binding of both radioligands, the binding apparently proceeding to two tandemly arranged interconnected mutually dependent binding sites. Steric considerations and BRET analysis of Rluc and GFP tagged receptors proposed that these sites are located on different subunits of receptor dimers, which form receptor complexes. According to the minimal model proposed, ligand binding proceeds consecutively to the two binding sites of the dimer. After binding of the first ligand conformational transformations of the complex occur, which is followed by binding of the second ligand. When both receptor units have bound [(125)I]NDP-MSH, the radioligand can be released only from one unit. The [(125)I]NDP-MSH bound to the remaining unit stays practically irreversibly bound due to a very slow retransformation rate of the transformed complex. The considerably faster binding of [(125)I]THIQ did not allow accurate kinetic differentiation of the two binding sites. However, addition of NDP-MSH as well as a fragment of the human agouti protein, hAGRP(83-132) to the preformed [(125)I]THIQ-MC(4)R complex drastically retarded the release of [(125)I]THIQ from the complex, blocking conformational transformations in the complex by binding into the second binding site. The consecutive binding of ligands to the MC(4)R dimers has substantial impact on the apparent ligand potencies, when determined in competition with the two different radioligands applied herein; the apparent potencies of the same ligand differing up to three orders of magnitude when assayed in competition with [(125)I]NDP-MSH or [(125)I]THIQ.     

The Rice Aquaporin Lsi1 Mediates Uptake of Methylated Arsenic Species

Pentavalent methylated arsenic (As) species such as monomethylarsonic acid [MMA(V)] and dimethylarsinic acid [DMA(V)] are used as herbicides or pesticides, and can also be synthesized by soil microorganisms or algae through As methylation. The mechanism of MMA(V) and DMA(V) uptake remains unknown. Recent studies have shown that arsenite is taken up by rice (Oryza sativa) roots through two silicon transporters, Lsi1 (the aquaporin NIP2;1) and Lsi2 (an efflux carrier). Here we investigated whether these two transporters also mediate the uptake of MMA(V) and DMA(V). MMA(V) was partly reduced to trivalent MMA(III) in rice roots, but only MMA(V) was translocated to shoots. DMA(V) was stable in plants. The rice lsi1 mutant lost about 80% and 50% of the uptake capacity for MMA(V) and DMA(V), respectively, compared with the wild-type rice, whereas Lsi2 mutation had little effect. The short-term uptake kinetics of MMA(V) can be described by a Michaelis-Menten plus linear model, with the wild type having 3.5-fold higher V_max than the lsi1 mutant. The uptake kinetics of DMA(V) were linear with the slope being 2.8-fold higher in the wild type than the lsi1 mutant. Heterologous expression of Lsi1 in Xenopus laevis oocytes significantly increased the uptake of MMA(V) but not DMA(V), possibly because of a very limited uptake of the latter. Uptake of MMA(V) and DMA(V) by wild-type rice was increased as the pH of the medium decreased, consistent with an increasing proportion of the undissociated species. The results demonstrate that Lsi1 mediates the uptake of undissociated methylated As in rice roots.Arsenic (As) contamination affects millions of people worldwide, particularly in South Asia where As-contaminated groundwater has been extracted for drinking (Chakraborti et al., 2002; Nordstrom, 2002). Recent studies have shown that foods, especially rice (Oryza sativa), are an important source of inorganic As to populations dependent on a rice diet (Kile et al., 2007; Ohno et al., 2007; Mondal and Polya, 2008). Paddy rice is more efficient than other cereal crops in accumulating As (Williams et al., 2007). This is because anaerobic conditions in submerged paddy soils lead to mobilization of arsenite [As(III); Takahashi et al., 2004; Xu et al., 2008], which is then taken up by rice roots mainly through the highly efficient transport pathway for silicon (Si; Ma et al., 2008). The relatively high accumulation of As in rice is of concern, as it may pose a significant health risk (Zhu et al., 2008; Meharg et al., 2009).A number of As species may be present in soil depending on soil conditions and the history of As contamination. These include arsenate [As(V)], As(III), and methylated As species such as monomethylarsonic acid [MMA(V): CH₃AsO(OH)₂] and dimethylarsinic acid [DMA(V): (CH₃)₂AsO(OH)]. As(V) is the main species in aerobic soils, while As(III) dominates in anaerobic environments such as flooded paddy soils. Both MMA(V) and DMA(V) have been found in paddy soils (Takamatsu et al., 1982), which may have been derived from microbial and algal biomethylation and/or past uses of methylated As compounds. MMA(V), as sodium or calcium salt, and DMA(V), as sodium salt or free acid (also called cacodylic acid), are herbicides widely used for weed control on cotton (Gossypium hirsutum), orchards, and lawns, or as a defoliant of cotton (U.S. Environmental Protection Agency, 2006). Conversion of cotton fields for the production of paddy rice in the United States may be a reason for the high levels of methylated As reported for the U.S. rice (Meharg et al., 2009).The mechanism of As(V) uptake by plants through the phosphate transport system has been well established (for review, see Zhao et al., 2009). In contrast, As(III) is taken up into the cells by aquaglyceroporins in Escherichia coli, yeast (Saccharomyces cerevisiae), and mammalian tissues (for review, see Bhattacharjee and Rosen, 2007). Recent studies have shown that several plant aquaporin channels belonging to the Nodulin 26-like Intrinsic Protein (NIP) subfamily are permeable to As(III) when expressed heterologously in yeast (Bienert et al., 2008; Isayenkov and Maathuis, 2008; Ma et al., 2008). The rice Si transporter Lsi1 (OsNIP2;1; Ma et al., 2006) is also permeable to As(III) when expressed in yeast or Xenopus laevis oocytes (Ma et al., 2008). Furthermore, the lsi1 rice mutant lost 57% of the influx capacity for As(III) compared to the wild type in short-term assays, suggesting that Lsi1 is an important entry route for As(III) (Ma et al., 2008). In rice roots, a second Si transporter, Lsi2, functions as an efflux carrier to transport Si efflux from the exodermis and endodermis cells toward the stele for xylem loading (Ma et al., 2007). This transporter also mediates As(III) efflux; two independent lsi2 mutants had 73% to 91% lower concentrations of As(III) in the xylem sap than their wild types (Ma et al., 2008). The shared uptake pathway between Si (silicic acid) and As(III) (arsenous acid) is consistent with their physiochemical properties; both are present predominantly as undissociated neutral molecules at the normal environmental and physiological pH range (pK_a = 9.2, >99% undissociated at pH ≤ 7.0), and the two molecules have similar sizes.The uptake mechanisms of methylated As species by plant roots are not known. Previous studies showed that both MMA(V) and DMA(V) can be taken up by roots and translocated to shoots in a number of plant species (Marin et al., 1992; Carbonell-Barrachina et al., 1998, 1999; Burló et al., 1999). Marin et al. (1992) found that uptake by rice followed the order of As(III) > MMA(V) > As(V) > DMA (V), although DMA(V) was more efficiently translocated from roots to shoots than other As species. Raab et al. (2007) reported large variations in the absorption and translocation efficiencies for As(V), MMA(V), and DMA(V) among the 46 plant species tested. On average, root absorption of As(V) was 2.5- and 5-times higher than MMA(V) and DMA(V), respectively. The translocation efficiency, defined as the shoot-to-root concentration ratio after 24-h exposure, was highest for DMA(V) (0.8), followed by MMA(V) (0.3) and As(V) (0.09). The concentration-dependent uptake kinetics of MMA(V) in rice roots could be described by the Michaelis-Menten equation, whereas the limited uptake of DMA(V) appeared to be linear in relation to the increasing concentration in the uptake medium (Abedin et al., 2002). Abbas and Meharg (2008) showed that DMA(V) uptake by maize (Zea mays) seedlings was enhanced by more than 10-fold by a pretreatment of phosphorus starvation; this compared with only 2-fold increase in As(V) uptake. They thought that DMA(V) might be taken up by the phosphate transporters, or that phosphorus starvation altered expression of a range of membrane transporters or even membrane permeability itself.In addition to the root uptake of methylated As species, some plants appear to be able to biomethylate As, but the pathway and enzymology remains unclear (Wu et al., 2002; Zhao et al., 2009). In microbes, As methylation follows the Challenger pathway involving repeated steps of As reduction and oxidative methylation (Bentley and Chasteen, 2002). As(V) is first reduced to As(III), which is methylated by S-adenosylmethyltransferase using S-adenosyl-l-Met as the methyl donor. The product of this reaction is pentavalent MMA(V), which is reduced by a reductase to trivalent MMA(III) with thiols (e.g. glutathione). Methylation and reduction steps continue to produce di- and trimethyl As compounds. MMA(III) and DMA(III) are intermediates in the As methylation pathway, which is not very stable (Gong et al., 2001). In rice grain, DMA(V) is the main form of methylated As, and can account for up to 80% of the total As (Zavala et al., 2008; Meharg et al., 2009). In light of the significant presence of methylated As in rice, it is important to elucidate the transport and assimilation pathways of these As species in plants.In this study, we present evidence that MMA(V) and DMA(V) are taken up by rice roots, at least partly, through the NIP aquaporin channel Lsi1, and that this process is strongly pH dependent. We also show that MMA(V) can be reduced to MMA(III) in planta.     

Environmental assessment of brownfield rehabilitation using two different life cycle inventory models

Goal, Scope and Background The primary goal of this paper is to present a LCI modelling approach that allows the inclusion of all three types of impacts. The approach is based on consequential LCA (CLCA) rather than more common attributional LCA (ALCA). In CLCA, system boundaries are expanded in order to include all significantly affected activities. In addition we show how changing from an attributional to a consequential approach alters how the impacts are evaluated, and discuss the applicability of these two distinct approaches to brownfield rehabilitation decision support. The paper is restricted to urban and contaminated brownfields that are the result of industrial use and whose rehabilitation is aimed at allowing residential redevelopment. Main Features The approach is based on an analogy between the open-loop recycling of material resources and brownfield rehabilitation. Brownfield rehabilitation is associated with two functions: (1) managing the legacy of past occupations on the site, analogous to a waste management function, and (2) providing redevelopable land, analogous to a commodity production function. The consequential system is expanded to cover the subsequent occupation life cycle of the brownfield and the effects on the occupation life cycles of other sites. The proposed model quantifies effects on sites competing to supply the same occupation function. Two approaches are proposed to determine the nature of the sites that are affected and to what extent they are affected: the first resembling a closed-loop approximation, and the second based on economic partial-equilibrium models. Results and Conclusions The scope of the CLCA is far more complex than that of the ALCA. It requires additional data that are associated with important sources of uncertainty. It does allow, however, for the inclusion of tertiary impacts, making it suitable for the evaluation of the often cited environmental benefits of reintegrating the site in the economy. In addition, the ALCA methodology seems to be inappropriate to compare brownfield management options that result in different subsequent uses of the site. Since the effects of this fate are included within the scope of CLCA, however, virtually any brownfield management option available to a decision-maker can aptly be compared. The evaluation of primary and secondary impacts also differs when the consequential approach is used rather than the attributional approach. It is impossible to anticipate the effects of these methodological differences on the results based on the qualitative discussion presented in this paper. Perspectives The complexity and uncertainty introduced by switching to a consequential approach is very high: it is therefore recommendable to evaluate the significance in the gain of environmental information in an actual case study to determine if system expansion is recommendable. Such a case study is presented in Part II to this paper. [39] Lesage P, Ekvall T, Deschênes L, Samson R (20006): Environmental Assessment of Brownfield Rehabilitation Using Two Different Life Cycle Inventory Models. Part 2: Case Study. Int J LCA, OnlineFirst (DOI: )     

Preferences for paper bedding material of the laboratory mice.

In order to identify indicators of the preferences for bedding materials, the paper bedding material preferences of laboratory mice were investigated in the present study. Four cages, each containing a different structure of paper bedding material were connected to allow free access to each cage. The preferences for paper bedding materials of laboratory mice were judged by the differences in the length of stay and sleep in each cage. The mice preferred the bedding material that allowed them to easily hide and build nests and was soft. We conclude that the comfort and well-being of laboratory mice can be increased through the appropriate selection of bedding material.     

Kinetic evidence for isomerization of the dopamine receptor-raclopride complex

The binding kinetics of the specific dopamine D₂ antagonist [³H]raclopride to dopamine D₂ receptors in rat neostriatum were studied. The pseudo-first-order rate constants of [³H]raclopride binding with these membranes revealed a hyperbolic dependence upon the antagonist concentration, indicating that the reaction had at least two consecutive and kinetically distinguished steps. The first step was fast binding equilibrium, characterized by the dissociation constant K_A = 12 ± 2 nM. The following step corresponded to a slow isomerization of the receptor-antagonist complex, characterized by the isomerization equilibrium constant K_i = 0.11. The dissociation constant K_d = 1.3 nM, calculated from these kinetic data, was similar to K_d = 2.4 nM, determined from equilibrium binding isotherm for the radioligand. Implications of the complex reaction mechanism on dopamine D₂ receptor assay by [³H]raclopride were discussed.     

Novel Features of Eukaryotic Photosystem II Revealed by Its Crystal Structure Analysis from a Red Alga

Photosystem II (PSII) catalyzes light-induced water splitting, leading to the evolution of molecular oxygen indispensible for life on the earth. The crystal structure of PSII from cyanobacteria has been solved at an atomic level, but the structure of eukaryotic PSII has not been analyzed. Because eukaryotic PSII possesses additional subunits not found in cyanobacterial PSII, it is important to solve the structure of eukaryotic PSII to elucidate their detailed functions, as well as evolutionary relationships. Here we report the structure of PSII from a red alga Cyanidium caldarium at 2.76 Å resolution, which revealed the structure and interaction sites of PsbQ′, a unique, fourth extrinsic protein required for stabilizing the oxygen-evolving complex in the lumenal surface of PSII. The PsbQ′ subunit was found to be located underneath CP43 in the vicinity of PsbV, and its structure is characterized by a bundle of four up-down helices arranged in a similar way to those of cyanobacterial and higher plant PsbQ, although helices I and II of PsbQ′ were kinked relative to its higher plant counterpart because of its interactions with CP43. Furthermore, two novel transmembrane helices were found in the red algal PSII that are not present in cyanobacterial PSII; one of these helices may correspond to PsbW found only in eukaryotic PSII. The present results represent the first crystal structure of PSII from eukaryotic oxygenic organisms, which were discussed in comparison with the structure of cyanobacterial PSII.