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Computer models of DNA four-way junctions.

A modeling scheme that combines a constrained backbone generating algorithm with simple hard-sphere packing calculations is offered to build the four-stranded structures of DNA found in Holliday junctions. Two standard B-DNA duplexes are oriented side by side with helix axes at different relative inclinations and then systematically rotated and translated to identify closely spaced contact-free states. Attempts are subsequently made to introduce a low-energy sugar-phosphate linkage that serves as the site of strand exchange between the two duplexes. The chemical connection is sought using an algorithm which identifies the possible arrangements of the intervening backbone torsions between arbitrarily positioned bases. The goal is to identify the multiple conformational solutions associated with a particular arrangement of neighboring DNA helices in the four-way junction rather than a single optimum structure. The methodology is general, in terms of accommodating four-way junctions with arms of variable conformation and chain length and of dimensions much greater than treated heretofore. The only deformation in the four-way structures relative to B-DNA occurs at the site of backbone exchange, with base stacking and Watson-Crick pairing completely preserved in all models. The arrangements of neighboring bases at these sites resemble the unusual conformational steps found in a number of small molecule nucleic acid crystal structures. An interesting outcome of the calculations is the formation of sterically acceptable four-arm Holliday junctions over a wide range of angles at the cross. The potential mobility of the Holliday junctions is inferred from visualization and energetic analysis of the various models. Long-range electrostatic energies based on different currently available treatments of the dielectric constant are used to estimate the conformational preferences and flexibility of the four-stranded structures. The various dielectric schemes, however, are not in complete agreement on the likely conformational variability of the four-way junctions. The structures suggest a possible mechanism for branch migration and detail a pathway linking the antiparallel uncrossed Holliday structure inferred from solution measurements and the parallel cross-packed helical arrangements observed in single-crystal X-ray studies.

Algorithms↗

The high-resolution crystal structure of human annexin III shows subtle differences with annexin V.

The structure of recombinant human annexin III was solved to 1.8 A resolution. Though homologous to annexin I and V, the annexin III structure shows significant differences. The tryptophan in the calcium loop of the third domain is exposed to the solvent, as in the structure of annexin V crystallized in high calcium concentrations, although the annexin III crystals were prepared at low calcium concentrations. The position of domain III relative to the other domains is different from both annexin V and I, suggesting further flexibility of the molecule. The entire N-terminus of the protein is well-defined in the present structure. The side chain of tryptophan 5 interacts with the hinge region of the hydrophillic channel, which could have an effect on the potential mobility of this region, as well as on its possible calcium channel behavior.

Annexin A1↗

Modeling lead input and output in soils using lead isotopic geochemistry.

The aim of this study is to model downward migration of lead from the plow layer of an experimental site located in Versailles (about 15 km southwest of Paris, France). Since 1928, samples have been collected annually from the topsoil of three control plots maintained in bare fallow. Thirty samples from 10 different years were analyzed for their lead and scandium contents and lead isotopic compositions. The fluxes are simple because of the well-controlled experimental conditions in Versailles: only one output flux, described as a first-order differential function of the anthropogenic lead pool, was taken into account; the inputs were exclusively ascribed to atmospheric deposition. The combination of concentration and isotopic data allows the rate of migration from the plowed topsoil to the underlying horizon and, to a lesser extent, the atmospheric fluxes to be assessed. Both results are in good agreement with the sparse data available. Indeed, the post-depositional migration of lead appears negligible at the human time scale: less than 0.1% of the potentially mobile lead pool migrates downward, out of the first 25 cm of the soil, each year. Assuming future lead inputs equal to 0, at least 700 yr would be required to halve the amount of accumulated lead pollution. Such a low migration rate is compatible with the persistence of a major anthropogenic lead pool deposited before 1928. Knowledge of pollution history seems therefore to be of primary importance.

Agriculture↗

Natural humics impact uranium bioreduction and oxidation.

Although humic substances occur ubiquitously in soil and groundwater, their effect on the biological reduction of uranium(VI) and subsequent reoxidation of U(IV) is poorly understood. This study investigated the role of humics in enhancing the bioreduction of U(VI) in laboratory kinetic studies, in field push-pull tests, and in the presence or absence of metal ions such as Ca2+ and Ni2+, which are known to inhibit the biological reduction of U(VI). Results from laboratory experiments indicate that, under strict anaerobic conditions, the presence of humic materials enhanced the U(VI) reduction rates (up to 10-fold) and alleviated the toxicity effect of Ni2+ on microorganisms. Humic acid was found to be more effective than fulvic acid in enhancing the reduction of U(VI). Such an enhancement effect is attributed to the ability of these humics in facilitating electron-transfer reactions and/or in complexing Ca2+ and Ni2+ ions. Similarly, field push-pull tests demonstrated a substantially increased rate of U(VI) reduction when humic acid was introduced into the site groundwater. However, humics were also found to form complexes with reduced U(IV) and increased the oxidation of U(IV) (when exposed to oxygen) with an oxidation halflife on the order of a few minutes. Both of these processes render uranium soluble and potentially mobile in groundwater, depending on site-specific and dynamic geochemical conditions. Future studies must address the stability and retention of reduced U(IV) under realistic field conditions (e.g., in the presence of dissolved oxygen and low concentrations of complexing organics).

Biodegradation, Environmental↗

Sorption-desorption of imidacloprid and its metabolites in soil and vadose zone materials.

Sorption-desorption is one of the most important processes affecting the leaching of pesticides through soil because it controls the amount of pesticide available for transport. Subsurface soil properties can significantly affect pesticide transport and the potential for groundwater contamination. This research characterized the sorption-desorption of imidacloprid (1-[(6-chloro-3-pyridinyl)-methyl]-N-nitro-2-imidazolidinimine) and three of its metabolites, 1-[(6-chloro-3-pyridinyl)methyl]-2-imidazolidinone (imidacloprid-urea), 1-[(6-chloro-3-pyridinyl)methyl]-4,5-dihydro-1H-imidazol-2-amine (imidacloprid-guanidine), and 1-[(6-chloro-3-pyridinyl)methyl]-1H-imidazol-2-amine (imidacloprid-guanidine-olefin), as a function of changing soil properties with depth in two profiles extending from the surface to a depth of 1.8 or 8 m. Sorption of each compound was highly variable and hysteretic in all cases. Normalizing the sorption coefficients (K(f)) to the organic carbon or the clay content of the soil did not reduce the variability in sorption coefficients for any compound. These results illustrate the importance of evaluation of the sorption data used to predict potential mobility. Understanding the variability of soil properties and processes as a function of depth is necessary for accurate prediction of pesticide dissipation.

Adsorption↗

Metal leachability and anthropogenic signal in roadside soils estimated from sequential extraction and stable lead isotopes.

Several roadside soil samples were collected at two field sites in Sweden. They were analysed for total elemental content (using both ICP-MS and XRF) and stable lead isotopes. Extraction with deicing salt solution and sequential extraction were performed in order to elucidate the potential mobility due to the use of deicing agents. The total concentrations of elements, especially lead, have decreased and lead is presently almost at background concentrations (15-51 ppm for surface samples). However, the isotopic signature indicates that old gasoline lead still is left at the site constructed prior to 1975. The field site constructed in 1992 showed, however, no 206Pb/207Pb ratio below 1.14. Only minor amounts were leached using deicing salt solutions; for lead only 0.29%, on average, was extracted indicating that the mobile fraction already was released. Sequential extraction indicated that lead mainly was associated with reducible (34.4%) and oxidisable (35.4%) fractions. Exchangable and acid soluble fractions contained 20.3% while 10.0% was found in the residual fraction. The salt extraction released, however, very low concentrations indicating that most in fraction 1 is acid soluble (e.g. carbonates). Tungsten was also found at high concentrations indicating a possible impact from studded tires. For tungsten the following composition was obtained: residual (48.0%) > oxidisable (47.6%) > reducible (3.3%) > exchangeable/acid soluble (1.1%). From the isotopic studies it was also suggested that the order for incorporating anthropogenic lead into soils is exchangeable/carbonates > (hydr)oxides > organic matter > residual. The multivariate technique principal component analysis (PCA) seems promising for evaluating large sequential extraction datasets.

Environmental Monitoring↗

Characterization of the targeting, binding, and phosphorylation site domains of an A kinase anchor protein and a myristoylated alanine-rich C kinase substrate-like analog that are encoded by a single gene.

A novel Drosophila A kinase anchor protein, Drosophila A kinase anchor protein 200 (DAKAP200), is predicted to be involved in routing, mediating, and integrating signals carried by cAMP, Ca(2+), and diacylglycerol (Li, Z., Rossi, E. A., Hoheisel, J. D., Kalderon, D., and Rubin, C. S. (1999) J. Biol. Chem. 274, 27191-27200). Experiments designed to assess this hypothesis now (a) establish the function, boundaries and identity of critical amino acids of the protein kinase AII (PKAII) tethering site of DAKAP200; (b) demonstrate that residues 119-148 mediate binding with Ca(2+)-calmodulin and F-actin; (c) show that a polybasic region of DAKAP200 is a substrate for protein kinase C; (d) reveal that phosphorylation of the polybasic domain regulates affinity for F-actin and Ca(2+)-calmodulin; and (e) indicate that DAKAP200 is myristoylated and that this modification promotes targeting of DAKAP200 to plasma membrane. DeltaDAKAP200, a second product of the DAKAP200 gene, cannot tether PKAII. However, DeltaDAKAP200 is myristoylated and contains a phosphorylation site domain that binds Ca(2+)-calmodulin and F-actin. An atypical amino acid composition, a high level of negative charge, exceptional thermostability, unusual hydrodynamic properties, properties of the phosphorylation site domain, and a calculated M(r) of 38,000 suggest that DeltaDAKAP200 is a new member of the myristoylated alanine-rich C kinase substrate protein family. DAKAP200 is a potentially mobile, chimeric A kinase anchor protein-myristoylated alanine-rich C kinase substrate protein that may facilitate localized reception and targeted transmission of signals carried by cAMP, Ca(2+), and diacylglycerol.

A Kinase Anchor Proteins↗

Overview of analysis of carcinogenic and/or mutagenic metals in biological and environmental samples. I. Arsenic, beryllium, cadmium, chromium and selenium.

One of the most dangerous and pernicious forms of pollution arises from the potential mobilization of a spectrum of toxic trace metals and metalloids in our environment. Among the most important elements in this regard are arsenic, beryllium, cadmium, chromium and selenium whose adverse toxic effects are now well recognized including their carcinogenicity and/or mutagenicity. These agents (and their derivatives) can be widely dispersed throughout the environment as a result of fossil fuel combustion, industrial and agricultural processes and natural processes. The trend for the immediate future appears to be of greater exposure to these metals not only as a result of generally increased usage patterns but also because of prospective enhanced use of fossil fuels for space heating and electricity generation. In order to more readily evaluate trends of human exposure as well as the toxicity, bioavailability, bioaccumulation and transport of these elements, sensitive analytical procedures are required for the determination of their various oxidation states (as well as their organic derivatives) in complex matrices such as those found in both environmental and biological samples. Hence, the principal objective of this overview is to highlight the more recent trends and state-of-the-art methodologies for the determination of arsenic, beryllium, cadmium, chromium and selenium (in their various forms) in environmental compartments such as air, water, soil and in human tissues (primarily blood, urine, and milk). Techniques to be discussed primarily include atomic absorption spectrometry, neutron activation analysis, gas chromatography, differential pulse polarography and electrochemical analysis. The importance of quality control and differentiation according to speciation will also be stressed.

Air↗

Heavy metal pollution of road dust and roadside soil near a major rural highway.

The concentrations of lead, copper, cadmium, zinc, nickel and chromium were measured in road dust and roadside soils from a French major highway. The profiles of total levels in the soil as a function of distance from the road edge and as a function of depth were investigated. Lead, zinc, copper and, to a lesser extent, cadmium contamination were found in samples taken on the surface and in the immediate vicinity of the road. The observed concentrations decreased rapidly with distance and depth. Soil samples appeared to exhibit little nickel and chromium pollution. The geochemical phases on which heavy metals (lead, copper, zinc, cadmium and chromium) were fixed preferentially, as well as the potential mobility of the different metals under certain physical and chemical conditions were evaluated. Sequential extractions and single extractions with different reagents were performed. Chromium, which was present mostly in residual form, was mainly of natural origin in the studied samples and was not highly mobilisable. Cadmium was the most easily exchangeable element in case of variations in the physical and chemical conditions but the quantities involved remained small. Lead and copper did not appear to be highly mobile. Only drastic conditions, such as those that may be produced by accidental spillage of a chemical product (acid or complexing agent), mobilised them quantitatively. A significant risk of mobilisation was to be feared only in the case of zinc, which is very sensitive to acid pH.

Dust↗

Accumulation and partitioning of phosphorus and heavy metals in a sandy soil under long-term vegetable crop production.

Increased inputs of phosphorus (P) and heavy metals to agricultural soils have caused considerable concern. Information on accumulation and chemical forms of the elements in soils is needed as a guide for the judicious application of agricultural chemicals and organic manures. The focus of this study was to assess accumulation of P and heavy metals among various fractions of a sandy soil with a 25 year history of vegetable crop production and primarily inorganic fertilization. The results demonstrated that long-term vegetable production practices changed concentrations and partitioning of P and heavy metals in the soil. Phosphorus, Cu, Zn, and Mn were significantly accumulated and moved downward along the soil profile. Most of the total Cr in the vegetable soil accumulated in the upper 0-15 cm. However, there was no significant accumulation and transport of Cd, Co, Mo, Ni, and Pb in the vegetable soil. Major P fractions in the vegetable soil were NaHCO3-P, followed by HCl-P and residual P. Copper, Zn, and Mn accumulated predominantly in the CaCO3 fraction or oxide fraction, whereas Cr accumulated mainly in the organically bound fraction, indicating that P, Cu, Zn, and Mn in the vegetable soil have greater mobility potential. Compared with adjacent forest soil, the vegetable soil had a lower percentage of P, Cu, Zn, and Mn in the residual fractions, and a higher percentage of P, Cu, Zn, and Mn in the CaCO3 fractions or organically bound fraction.

Agriculture↗

Distribution of forms of heavy metals in soils contaminated by metallurgical smelter emissions.

The objective of this study was to investigate the chemical partitioning of heavy metals occur in soils polluted with metallurgical smelters as well as to estimate potential mobility of these metals. Six soil profiles situated at different distances from metallurgical smelters were chosen and soil samples were taken from top- and sub-surfiace layers. Total contents of metals were much higher in top-soil than in sub-surface soil and varied in the following ranges (mg kg(-1)): Cu, 1-298; Zn, 2.4-322; Pb, 2.8-196; Cd, 0.34-2.04; Cr. 1.89-6.68; Ni, 2.59-10.15. The speciation of metals (Cu, Zn, and Pb) originating from metallurgical smelters showed considerably higher percentages of exchangeable and carbonate fractions which were likely to be leached from surface layer of sandy soils. The distribution of forms of metals were found to depend strongly both on soil properties and metal origin.

Air Pollutants↗

Gene therapy of HIV-1 infection using lentiviral vectors expressing anti-HIV-1 genes.

The use of vectors based on primate lentiviruses for gene therapy of human immunodeficiency virus type 1 (HIV-1) infection has many potential advantages over the previous murine retroviral vectors used for delivery of genes that inhibit replication of HIV-1. First, lentiviral vectors have the ability to transduce dividing and nondividing cells that constitute the targets of HIV-1 infection such as resting T cells, dendritic cells, and macrophages. Lentiviral vectors can also transfer genes to hematopoietic stem cells with a superior gene transfer efficiency and without affecting the repopulating capacity of these cells. Second, these vectors could be potentially mobilized in vivo by the wild-type virus to secondary target cells, thus expanding the protection to previously untransduced cells. And finally, lentiviral vector backbones have the ability to block HIV-1 replication by several mechanisms that include sequestration of the regulatory proteins Tat and Rev, competition for packaging into virions, and by inhibition of reverse transcription in heterodimeric virions with possible generation of nonfunctional recombinants between the vector and viral genomes. The inhibitory ability of lentiviral vectors can be further increased by expression of anti-HIV-1 genes. In this case, the lentiviral vector packaging system has to be modified to become resistant to the anti-HIV-1 genes expressed by the vector in order to avoid self-inhibition of the vector packaging system during vector production. This review focuses on the use of lentiviral vectors as the main agents to mediate inhibition of HIV-1 replication and discusses the different genetic intervention strategies for gene therapy of HIV-1 infection.

Genes, Viral↗

Determination of deoxynivalenol (DON, vomitoxin) in wheat by high-performance liquid chromatography with photolysis and electrochemical detection (HPLC-hv-EC).

Deoxynivalenol (DON, vomitoxin) is a naturally occurring toxic fungal metabolite found in grains such as wheat, corn, rye, and barley. Current methods of analysis for DON and related trichothecene mycotoxins involve gas chromatography with electron capture detection, thin-layer chromatography, and high-performance liquid chromatography with ultraviolet detection. Improved sensitivity and selectivity for DON, as well as for the related compounds nivalenol and fusarenon-X, are made possible by the use of high-performance liquid chromatography with online, postcolumn photolysis and oxidative amperometric detection (HPLC-hv-EC). Conditions are optimized with respect to residence time in the photolytic reactor, applied potentials, mobile phase pH, and chromatographic parameters for the separation of DON, nivalenol, and fusarenon-X, and the technique is found to be linear over a range of 10 ppb-2 ppm with minimum detection limits on the order of 1-2 ng on-column (10-20 ppb). Since these compounds are not electroactive in the absence of photolysis, an additional mode of specificity is realized in addition to the chromatographic retention time and the dual-electrode response ratio. Some market samples of wheat naturally contaminated with DON are analyzed by this method, and the results are in agreement with those obtained by HPLC-UV and TLC analyses of the same samples.

Chromatography, High Pressure Liquid↗

Contribution of vegetative storage proteins to seasonal nitrogen variations in the young shoots of peach trees (Prunus persica L. Batsch).

Qualitative and quantitative variations in the level of two low molecular weight vegetative storage proteins (VSP 19 kDa and 16.5 kDa) in peach shoots were compared with annual variations in total nitrogen and total soluble proteins. Protein patterns were obtained by SDS-PAGE and silver staining on each of the 12 kinetic samples collected between October 1995 and November 1996. VSP 16.5 kDa and 19 kDa exhibited typical annual VSP variations in both parenchyma and phloem. In wood, VSP 16.5 kDa was only present in November. All N compounds tested were stored in the autumn and their levels fell in the spring. Parenchyma was the principal stem storage tissue for all N compounds tested, even if proteins were more often highly concentrated in phloem and even if wood was the major shoot constituent. In winter, the two VSP accounted for 13% of bark proteins and 11% of wood proteins. Their storage yield, given by the winter/summer (W/S) ratio was higher (18.5) than that of total proteins (4). Between August to March, i.e. during the storage phase, N fractions obtained from VSP (N3) and total soluble proteins minus VSP (N2) accounted, respectively, for only 3% and 21% of total N accumulation in the bark, the remainder being due to the fraction not extracted (N1). A marked drop in all N compound levels characterized the mobilization phase (March to April), particularly for N3 (-84% between March and April) which were mobilized slightly before other N compounds. Although N3 exhibited the best mobilization yield, it represented only 5% of the total N mobilized. So, in spite of a similarity between VSP and N annual variation patterns, there was no tight correlation between their contents in bark. N2 supplied a high proportion of the N used for spring regrowth (40%), but the larger share (55%) came from N1 which was probably made up of free amino acids. Very tight positive correlations have been observed between these two N fractions and the N status. The lower bark total N content measured in August (6.4 mg N g(-1 )DW) during the assimilation phase (April to August) was equal to the unavailable N fraction, and the bark N mobilization potential (between March and August) was estimated at 6.35 mg N g(-1) DW. VSP did not quantitatively represent the main stored N pool. But, because of their high W/S ratio and their early remobilization, they seemed to play an important role in spring regrowth initiation.

Electrophoresis, Polyacrylamide Gel↗

A novel neurotoxin, cobrotoxin b, from Naja naja atra (Taiwan cobra) venom: purification, characterization, and gene organization.

A novel neurotoxin, cobrotoxin b, was isolated from Naja naja atra (Taiwan cobra) venom by successive chromatographies on gel filtration and SP-Sephadex C-25 columns. The yield of this novel toxin was 5% of that of cobrotoxin from the same venom. Its neurotoxicity determined as the inhibition of acetylcholine-induced muscle contractions was approximately 50% of that of cobrotoxin. Cobrotoxin b consists of 61 amino acid residues including 8 cysteine residues. Moreover, there are 12 amino acid substitutions between cobrotoxin b and cobrotoxin. The genomic DNA, with a size of 2,386bp, encoding the precursor of cobrotoxin b was isolated from the liver of N. naja atra. The gene consists of three exons separated by two introns. This exon/intron structure is essentially the same as that reported for the cobrotoxin gene. Moreover, the nucleotide sequences of the two neurotoxin genes exhibit 92% identity. These results highly suggest that the cobrotoxin b and cobrotoxin genes are derived from a common ancestor. Comparative analyses of cobrotoxin b and cobrotoxin precursors showed that the protein-coding regions of the exons are more diverse than introns, except for in the signal peptide domain. This indicates that the protein-coding regions may have arised via accelerated evolution. BLAST searches for sequence similarity in the GeneBank databases showed that intron 1 of the cobrotoxin b and cobrotoxin genes encodes a small nucleolar RNA (snoRNA). However, the snoRNA gene is absent from the gene encoding the Laticauda semifasciata erabutoxin c precursor (L. semifasciata and N. naja atra are sea and land snakes, respectively). Since previous studies suggested the potential mobility of snoRNA genes during evolution, we propose that intron insertions or deletions of snoRNA genes occurred with the evolutionary divergence between the sea snake and land snake neurotoxins.

Amino Acid Sequence↗

Antibody-induced redistribution of virus antigens on the surface of influenza virus-infected cells.

The behaviour of virus-specific antigen-antibody complexes at the plasma membrane of HeLa cells infected with influenza virus (A0PR8) was studied by immunofluorescence- and immunoelectron-microscopy. As early as 7 h after infection the virus-induced plasma membrane antigens are evenly distributed over the surface of the infected cells. The addition of antiviral antibodies interferes with this distribution. The appearance of a subsequent patchlike and 'capping' distribution, followed by the disappearance of virus antigen-antibody complexes from the cell surface, is described. These findings demonstrate the potential mobility of virus-induced antigens in the plane of the cell surface.

Antibodies, Viral↗

Retention and internal loading of phosphorus in shallow, eutrophic lakes.

This paper gives a general overview of the nature and important mechanisms behind internal loading of phosphorus (P), which is a phenomenon appearing frequently in shallow, eutrophic lakes upon a reduction of the external loading. Lake water quality is therefore not improved as expected. In particular summer concentrations rise and P retention may be negative during most of the summer. The P release originates from a pool accumulated in the sediment when the external loading was high. In most lake sediments, P bound to redox-sensitive iron compounds or P fixed in more or less labile organic forms constitute major fractions--forms that are potentially mobile and eventually may be released to the lake water. The duration of the recovery period following P loading reduction depends on the loading history, but it may last for decades in lakes with a high sediment P accumulation. During the phase of recovery, both the duration and net P release rates from the sediment seem to decline progressively. Internal P loading is highly influenced by the biological structure as illustrated by lakes shifting from the turbid to the clearwater state as a result of, for example, biomanipulation. In these lakes P concentrations may be reduced to 50% of the pre-biomanipulation level and the period with negative retention during summer can thus be reduced considerably. The duration of internal loading can be reduced significantly by different restoration methods such as dredging to remove accumulated P or addition of iron or alum to elevate the sorption capacity of sediments. However, an important prerequisite for achieving long-term benefits to water quality is a sufficient reduction of the external P loading.

Ecosystem↗

Subtle but variable conformational rearrangements in the replication cycle of Sulfolobus solfataricus P2 DNA polymerase IV (Dpo4) may accommodate lesion bypass.

The possible conformational changes of DNA polymerase IV (Dpo4) before and after the nucleotidyl-transfer reaction are investigated at the atomic level by dynamics simulations to gain insight into the mechanism of low-fidelity polymerases and identify slow and possibly critical steps. The absence of significant conformational changes in Dpo4 before chemistry when the incoming nucleotide is removed supports the notion that the "induced-fit" mechanism employed to interpret fidelity in some replicative and repair DNA polymerases does not exist in Dpo4. However, significant correlated movements in the little finger and finger domains, as well as DNA sliding and subtle catalytic-residue rearrangements, occur after the chemical reaction when both active-site metal ions are released. Subsequently, Dpo4's little finger grips the DNA through two arginine residues and pushes it forward. These metal ion correlated movements may define subtle, and possibly characteristic, conformational adjustments that operate in some Y-family polymerase members in lieu of the prominent subdomain motions required for catalytic cycling in other DNA polymerases like polymerase beta. Such subtle changes do not easily provide a tight fit for correct incoming substrates as in higher-fidelity polymerases, but introduce in low-fidelity polymerases different fidelity checks as well as the variable conformational-mobility potential required to bypass different lesions.

Arginine↗