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Fluorometric sensing of alkali metal and alkaline earth metal cations by novel photosensitive monoazacryptand derivatives in aqueous micellar solutions.

Novel monoazacryptand-type fluorescent chemosensors, (derived from an 18-crown-6) and (derived from a 15-crown-5) both with a pyrene ring as their photoresponsive moiety, were synthesized. Their fluorescence properties for alkali metal and alkaline earth metal cations in water were then examined. The detection of metal cations was accomplished by a change in the fluorescence intensity of the host compounds, based on a photoinduced electron transfer (PET) mechanism. In aqueous solution, showed little fluorescence upon the addition of Ba2+ because of the very weak complexation with Ba2+, but the presence of micelles of polyoxyethylene(10) isooctylphenyl ether (Triton X-100) enabled to show highly sensitive and selective Ba2+ detection among alkali metal and alkaline earth metal cations. With respect to the selective fluorescent detection of important metal cations (Na+, K+, Mg2+, Ca2+) relevant to living organisms, was found to detect K+ with high selectivity in aqueous micellar solutions of polyoxyethylene(20) sorbitan monostearate (Tween-60). The selectivity for metal cations was mainly dependent on the goodness of fit of the host cavity and the metal cation size. In the presence of anionic surfactants, detected alkaline earth metal cations more effectively than alkali metal cations.

Journal Article↗

Periodic trends in metal-metal interactions in face-shared [M2Cl9]z- systems.

The periodic trends in metal-metal interactions in even-electron and mixed-valence [M2Cl9]z- face-shared systems, involving transition metals in Groups 4 to 8 and electronic configurations ranging from d1d1 through to d5d5 and from d1d2 through to d4d5, have been investigated by calculating metal-metal bonding and spin polarization (exchange) effects using density functional theory. These two terms are in opposition to one another and their relative difference determines the extent to which the metal-based electrons are delocalized and thus the degree of metal-metal bonding. Remarkably strong linear correlations between the two terms, and between each term and the square of the spin density on the metal centres, have been obtained for all group and period series considered, and are discussed in terms of their dependence on the metal orbital properties and electron density.

Journal Article↗

Defects in the yeast high affinity iron transport system result in increased metal sensitivity because of the increased expression of transporters with a broad transition metal specificity.

Yeast with defects in vacuolar pH show increased sensitivity to high concentrations of transition metals. This sensitivity has been presumed to result from defective metal storage. We demonstrate that mutations that result in a defective high affinity iron transport system, such as a deletion in the surface ferroxidase FET3, also result in increased metal sensitivity independent of vacuolar function. Multiple copies of transition metal transporter resistance genes, such as COT1 or ZRC1, do not reduce the metal sensitivity of fet3 mutations. Increased metal sensitivity is because of an increased cellular accumulation of transition metals resulting from the increased activity of low affinity iron transporters, such as FET4, that mediates the transport of other transition metals. In cells lacking a high affinity iron transport system, the increased transition metal uptake can be prevented by increased extracellular iron. These results suggest that vacuolar function may not be required for transition metal sequestration.

Base Sequence↗

Activation/attenuation model for RNase H. A one-metal mechanism with second-metal inhibition.

Ribonucleases H (RNases H) comprise a family of metal-dependent enzymes that catalyze the hydrolysis of the 3'-O---P bond of RNA in RNA.DNA hybrids. The mechanism by which RNases H use active-site metal(s) for catalysis is unclear. Based upon the seemingly contradictory structural observations of one divalent metal bound to Escherichia coli RNase HI and two divalent metals bound to the HIV RNase H domain, two models explaining RNase H metal dependence have been proposed: a one-metal mechanism and a two-metal mechanism. In this paper, we show that the Mn2+-dependent activity of E. coli RNase HI is not consistent with either of these mechanisms. RNase H activity in the presence of Mn2+ is complex, with activation and inhibition of the enzyme at low and high Mn2+ concentrations, respectively. Mutations at Asp-134 result in a partial loss of this inhibition, with little effect on activation. Neutralization of His-124 by mutation to Ala results in an enzyme with a significantly decreased specific activity and an absolute loss of Mn2+ inhibition. Inhibition by high Mn2+ concentrations is shown to be due to a reduction in kcat; this attenuation has a critical dependence on the presence of His-124. Based upon these results, we propose an "activation/attenuation" model explaining the metal dependence of RNase H activity where one metal is required for enzyme activation and binding of a second metal is inhibitory.

Amino Acid Substitution↗

Diagenesis of metals chemically complexed to bacteria: laboratory formation of metal phosphates, sulfides, and organic condensates in artificial sediments.

Cells of Bacillus subtilis, when suspended in a 5mM metal solution, bind metals tenaciously to their cell walls. These metal-loaded cells, when mixed with a synthetic sediment and put under laboratory conditions to simulate low-temperature sediment diagenesis, nucleate the formation of a mixed assemblage of crystalline metal phosphates, metal sulfides, and polymeric, metal-complexed, organic residues. The sequential series of diagenetic events leading to the formation of authigenic mineral phases was followed by transmission electron microscopy and energy-dispersive X-ray analysis. The minerals quartz (SiO(2)) and calcite (CaCO(3)) were employed in the synthetic sediment. Crystalline magnetite (Fe(2)O(3)) and elemental sulfur were added as redox buffering agents to ensure anoxic conditions. Quartz and magnetite appeared unreactive throughout the experimental conditions. Elemental sulfur interacted with the metal-loaded cells, affected both the eventual chemistry and crystal habit of the metal phosphates, and formed a variety of crystalline metal sulfides. Calcite raised the pH of the fluid phase of the sediment, which influenced phosphate mineralization and inhibited metal sulfide genesis.

Journal Article↗

Phospholipid Fatty Acid Composition and Heavy Metal Tolerance of Soil Microbial Communities along Two Heavy Metal-Polluted Gradients in Coniferous Forests.

The effects of long-term heavy metal deposition on microbial community structure and the level of bacterial community tolerance were studied along two different gradients in Scandinavian coniferous forest soils. One was near the Harjavalta smelter in Finland, and one was at Ronnskar in Sweden. Phospholipid fatty acid (PLFA) analysis revealed a gradual change in soil microbial communities along both pollution gradients, and most of the individual PLFAs changed similarly to metal pollution at both sites. The relative quantities of the PLFAs br18:0, br17:0, i16:0, and i16:1 increased with increasing heavy metal concentration, while those of 20:4 and 18:2(omega)6, which is a predominant PLFA in many fungi, decreased. The fungal part of the microbial biomass was found to be more sensitive to heavy metals. This resulted in a decreased fungal/bacterial biomass ratio along the pollution gradient towards the smelters. The thymidine incorporation technique was used to study the heavy metal tolerance of the bacteria. The bacterial community at the Harjavalta smelter, exposed mainly to Cu deposition, exhibited an increased tolerance to Cu but not to Cd, Ni, and Zn. At the Ronnskar smelter the deposition consisting of a mixture of metals increased the bacterial community tolerance to all tested metals. Both the PLFA pattern and the bacterial community tolerance were affected at lower soil metal concentrations than were bacterial counts and bacterial activities. At Harjavalta the increased Cu tolerance of the bacteria and the change in the PLFA pattern of the microbial community were found at the same soil Cu concentrations. This indicated that the altered PLFA pattern was at least partly due to an altered, more metal-tolerant bacterial community. At Ronnskar, where the PLFA data varied more, a correlation between bacterial community tolerance and an altered PLFA pattern was found up to 10 to 15 km from the smelter. Farther away changes in the PLFA pattern could not be explained by an increased community tolerance to metals.

Journal Article↗

Use of metal-on-metal total hip resurfacing for the treatment of osteonecrosis of the femoral head.

BACKGROUND: Recently, with the advent of improved metal-on-metal prostheses, total hip resurfacing has emerged as a viable arthroplasty option. However, it remains controversial whether this procedure should be used in patients with osteonecrosis when the femoral resurfacing component is cemented onto dead bone. The purpose of this study was to analyze the clinical and radiographic outcomes of metal-on-metal total hip resurfacing arthroplasty in patients with osteonecrosis of the femoral head. In addition, this group was compared with a matched group of patients who were diagnosed as having osteoarthritis. METHODS: Forty-two osteonecrotic hips that were treated with a metal-on-metal total hip resurfacing arthroplasty were studied. They were matched by gender, age, prosthesis, surgeon, and surgical approach to forty-two osteoarthritic hips that were treated with the same metal-on-metal prosthesis. In the osteonecrosis group, there were twenty-five men and eleven women, and in the osteoarthritis group, there were twenty-eight men and thirteen women. The mean age at the time of surgery was forty-two years. Patients were followed both clinically and radiographically for a mean of forty-one months. RESULTS: The clinical outcomes were similar for both groups, with a good or excellent outcome in thirty-nine hips (93%) with osteonecrosis and a good or excellent outcome in forty-one hips (98%) with osteoarthritis. In each of the two groups, there were two failures that required conversion to a standard total hip arthroplasty. Survivorship curves were similar for the two patient groups. CONCLUSIONS: The short-term results for metal-on-metal total hip resurfacing for this challenging patient population with osteonecrosis were excellent and comparable with those seen in patients with osteoarthritis. We await long-term results to see if these early results are maintained. LEVEL OF EVIDENCE: Prognostic Level II. See Instructions to Authors on jbjs.org for a complete description of levels of evidence.

Adolescent↗

Differential metal response and regulation of human heavy metal-inducible genes.

A number of heavy metal-inducible genes have been reported, but their ranges of response to various metal species are not well known. It is also unclear if these genes are regulated through common mechanisms. To answer these questions, we compared induction kinetics of human metal-inducible genes including the MT-IIA (coding for a metallothionein isoform), hsp70 (coding for the 70-kDa heat-shock protein), and c-fos genes in HeLa cells exposed to Zn, Cd, Ag, Hg, Cu(II), Co, or Ni ions. Transcripts from these three genes were increased after exposure to wide ranges of metals, but each gene was unique in its induction kinetics. Generally, induction was observed at lower metal concentrations in the order of MT-IIA, hsp70, and c-fos. These genes also showed differential responses in time course: more rapid induction was observed in the order of c-fos, hsp70, and MT-IIA after exposure to Zn or Cd. Since the metal-responsive element (MRE) and heat shock element (HSE) of the MT-IIA and hsp70 genes, respectively, are thought to be the cis-acting DNA elements that mediate metal response, we compared the properties of proteins that specifically bind to these elements. MRE-binding activity was detected only in the extract from cells exposed to Zn. By contrast, HSE-binding activity was detected in extracts from cells treated with Zn, Cd, Ag, and Cu. The former was also activated by Zn in vitro, while the latter was not. Each of these DNA-binding activities showed no affinity to the recognition sequence of the other. These results demonstrate that the human metal-inducible genes have broad ranges of response to a variety of heavy metals, but suggest that they are probably regulated through independent mechanisms.

Antigens, Nuclear↗

NMR identification of heavy metal-binding sites in a synthetic zinc finger peptide: toxicological implications for the interactions of xenobiotic metals with zinc finger proteins.

Lead (Pb), mercury (Hg), and cadmium (Cd) are toxic and interfere with protein metal-binding sites. The Cys(2)/His(2) zinc finger is a structural motif required for sequence-specific DNA binding and is present in zinc finger transcription factors (ZFP): Sp1, Egr-1, and TFIIIA. Neurotoxic studies have shown that heavy metals directly inhibit the DNA binding of ZFP and result in adverse cellular effects. Recently, we demonstrated the ability of heavy metals to alter the DNA binding of a synthetic Cys(2)/His(2) finger peptide (Razmiafshari and Zawia, Toxicol. Appl. Pharmacol. 166, 1-12, 2000). To determine the precise site of interactions between heavy metals and this protein domain, Pb, Hg, Cd, and Ca were reconstituted with the synthetic apopeptide and studied by one- and two-dimensional NMR spectroscopy. In the presence of Zn, Cd, Hg, and Pb, but not Ca, distinct peptide NMR signal changes in the aliphatic region were observed and attributed to metal-cystiene interactions. However, chemical shifts indicative of metal-histidine binding were elicited by all the metals in the peptide's aromatic region. Chemical shift assignments and sequential connectivity were established in the presence and absence of Zn, Pb, and Ca through TOCSY and NOESY spectra. Cysteine and histidine residues showed a distinct change in their amide and beta resonances in the presence of Zn and Pb, suggesting the metal-ligand binding sites were near these residues. However, Ca led to no significant spectral changes in these regions, suggesting that it is not actively involved in the binding site. These studies reveal this structure as a mediator of metal-induced alterations in protein function.

Binding, Competitive↗

[Metal-on-metal pairs for hip prostheses].

Due to engineering deficiencies as well as problems in the basic material, the first generation of metal-on-metal hip prostheses was not up to standard.Furthermore, unsatisfying clinical results led to a decrease in the use of these prostheses.Nevertheless, there were several cases which demonstrated good results in long-term clinical outcome. After distinct improvements in manufacturing and materials, metal-on-metal prostheses have made a come back. This second generation, which are known mainly under the names METASUL and SIKOMET,have been in clinical use for up to 10 years and the good results found in biomechanical set ups seem to be confirmed in clinical trials. However, a possible disadvantage of this second generation of metal-on-metal hip prostheses might be the production of large amounts of particulate wear debris in the nanometer size range. Whether the great number of small size particles with an extended metal surface and the possible distribution of these particles in the body have biological effects on the cells and tissues (such as allergic or toxic reactions) remains unknown. Among the tribological problems, there is currently a discussion on the possible inflammatory effect of these metal particles, which might play a crucial role in longterm, systemic reactions of the body to metal particles.

Biomechanical Phenomena↗

Transformations of metal species in ageing humic hydrocolloids studied by competitive ligand and metal exchange.

Transformations of metal species (particularly Al, Ca, Fe, Mg, Mn, Zn) in ageing humic hydrocolloids were studied, applying a competitive ligand and metal exchange approach. For this purpose, metal-containing hydrocolloids, freshly collected from humic-rich German bog lake waters (Hohlohsee (HO), Black Forest; Venner Moor (VM), Muensterland; Arnsberger Wald (AW), Northrhine-Westfalia) and conventionally pre-filtered through 0.45 microm membranes, were subjected on-site to an exchange with EDTA and Cu(II) ions, respectively, as a function of time. EDTA complexes gradually formed, metal fractions exchanged by Cu(II) (as well as free Cu(II) concentrations) were operationally discriminated by means of a small time-controlled tangential-flow ultrafiltration unit (nominal cutoff: 1 kDa). Metal and DOM (dissolved organic matter) fractions obtained this way were determined off-site using instrumental methods (AAS, ICP-OES, carbon analyzer). After weeks of storage, the collected hydrocolloids were studied again by this approach. The EDTA availability of colloid-bound metals (particularly Al and Fe) exhibited different ageing trends, dependent on the sample (VM: decrease of Fe availability (98-76%), HO: increase of Fe availability (76-82%)). In contrast, the Cu(II) exchange equilibria of colloid-bound metals revealed merely low availability of Al (16-38%) and Fe (5-11%) towards Cu(II) ions, also dependent on ageing effects. In particular, the conditional copper exchange constants Kex obtained from the exchange between Cu(II) ions and available metal species (such as Ca, Mg, Mn, Zn) exhibited a strong decrease (by a factor of 2-100) during sample storage, indicating considerable non-equilibria complexation of these metal ions in the original bogwaters studied on-site.

Colloids↗

Reduced metals concentrations of water, sediment and hyalella azteca from lakes in the vicinity of the sudbury metal smelters, Ontario, Canada.

Hyalella azteca (Crustacea: Amphipoda), water and sediments from 12 circum-neutral lakes between Sudbury and North Bay in Ontario, Canada were sampled in August 1998 and analyzed for 10 metals including Cu, Zn, Cd, Ni, Pb, Co, Mo, V, Ba and Ti. Statistical analyses showed that concentrations of the metals in H. azteca, water and sediment differed significantly (ANOVA, P<0.05) among lakes (except for Zn and Pb in H. azteca and Mo in water). There was a trend of declining metal concentration, especially for Cu, Ni and Co (in water, Hyalella and sediment), with distance from the smelters indicating the reduced impact of atmospheric pollution. Metal concentrations of lakes (water) in the Sudbury area were found to be lower compared to data from the 1970s and 1980s indicating an improvement in water quality. Metal concentrations in field-collected amphipods compared favorably with those measured in the laboratory in animals exposed to deep-water sediments, provided metal concentrations were not extremely low (e.g., Pb) and that water chemistry differences (e.g., pH) were taken into account for some metals (especially Cd). In general bioaccumulation of metals in H. azteca was predicted better from surface water than from sediment total metal.

Animals↗

Resolution of an ATP-metal chelate from metal-free ATP by reverse-phase high-performance liquid chromatography.

The modulation of many enzymatic reactions involved in the metabolism of nucleotide phosphates such as ATP often require divalent metal ions. In the present study reverse-phase high-performance liquid chromatography (HPLC) was used to study the chelation of divalent metal ions, such as Mn2+, Mg2+, and Ca2+, by ATP. The results of our study using radiolabeled [45Ca] showed that the metal-ATP chelate formed in solution was retained longer than the metal-free ATP due to the nonpolar groups on the column packing. Recovery of the two forms of ATP showed that the [45Ca] coeluted exclusively with the ATP-metal chelate. Other experiments showed that the retention time of the chelated form of the ATP was unaffected by eluent flow rate, but was affected by eluant pH and methanol concentration. The amount of ATP in the chelated form was found to be dependent on the amount of the metal in solution and that under appropriate conditions, i.e., with 0.1 mM CaCl2 in the mobile phase, on the divalent cation as well. Thus, we found that in terms of effectiveness in chelate formation, the metal ions were Ca2+ greater than Mg2+ greater than Mn2+. Recovery of the chelate and its reanalysis by HPLC revealed that the complex had dissociated. The chelate could be reformed by restoring the metal concentration to its original value and dissociated again by the addition of EDTA. The resolution of the ATP in a metal chelated form from the ATP in an unchelated form is discussed in terms of the stability of these chelates and the role of the hydrophobic groups of the column packing used in the reverse-phase HPLC in enhancement of this stability.

Adenosine Triphosphate↗

Metal determinations in biological specimens of diseased and non-diseased hard metal workers.

Biological monitoring of Co, Ta and W, using mainly neutron activation analysis, was carried out on the urine, blood, pubic hair and toe nails of 251 subjects occupationally exposed to hard metal dusts (23 individuals were diagnosed as 'diseased subjects', affected by asthma and/or lung fibrosis). Airborne dust at hard metal workplaces were also analyzed for Co and W content. Cobalt and tungsten exposure at workplaces varied widely and frequently exceeded the TLV (0.05 mg Co/m3). Cobalt in urine (CoU), which is better than Co in blood (CoB), could represent a valuable indicator in discriminating between exposed groups, but is of little value as an indicator of exposure for single individuals. The high concentrations of cobalt in public hair (CoH) and toe nails (CoN) could also be valuable indicators of exposure although they are not useful, however, in establishing quantitatively the levels of cobalt accumulation. Tungsten and tantalum in pubic hair (WH and TaH) and toe nails (WN and TaN) also seem to be useful indicators in proving hard metal exposure qualitatively. The determination of these two elements, rather than cobalt, in the bronchoalveolar lavage (BAL) is very useful in complementing the diagnosis of hard metal disease proving hard metal exposure. The analysis of the BAL subfractions showed that W and Ta were firmly incorporated into the macrophage fraction while Co was distributed between cellular fraction and supernatant, which suggests a different mobility of hard metals in pulmonary tissue. The metal concentrations determined when submitted to statistical analysis indicated a positive correlation with P < 0.001 for the pairs (CoB-CoU), (Co-W) in urine, and (Co-W) in toe nails. Multielement analysis of biological specimens from diseased subjects suggests that hard metal disease does not relate to Co, W and Ta levels in the specimens considered. The disease does not depend on sex, age, working age and length of hard metal exposure. These findings support the theory on the possible haptenic properties of Co which may induce hypersensitivity and immuno-related toxic effects.

Adolescent↗

Processes controlling metal transport and retention as metal-contaminated groundwaters efflux through estuarine sediments.

Factors affecting the transport and retention of Cd, Cr, Cu, Ni, Pb and Zn in acidic groundwaters as they pass through estuarine sediments were investigated using column experiments. Acidic groundwaters caused the rapid dissolution of iron sulfide (AVS) and other iron and manganese phases from sediments that are important for metal binding and buffering. Metal breakthrough to overlying water occurred in the order of Ni>Zn>Cd>>Cu>>Cr/Pb. Metal transport increased as the sediment permeability increased, reflecting the low resistance to flow caused by larger sand-sized particles and the decreased abundance of metal adsorption sites on these materials. Metal mobility increased as the groundwater pH decreased, as flow rate or metal concentrations increased, and as the exposure duration increased. Groundwater Cr and Pb were promptly attenuated by the sediments, the mobility of Cu was low and decreased rapidly as sediment pH increased above 4.5, while Cd, Ni and Zn were the most easily transported to the surface sediments and released to the overlying waters. For groundwaters of pH 3, metal migration velocities through sandy sediments were generally 0.5-2% (Cr, Pb), 1-6% (Cu) and 4-13% (Cd, Ni, Zn) of the total groundwater velocity (9-700 m/yr). The oxidative precipitation of Fe(II) and Mn(II) in the groundwaters did not affect metal mobility through the sediments. The results indicated that the efflux of acidic and metal-contaminated groundwater through estuarine sediments would affect organisms resident in sandy sediments more greatly than organisms resident in fine-grained, silty, sediments.

Animals↗

Transfer and accumulation of metals in a soil-diet-wood mouse food chain along a metal pollution gradient.

We studied the accumulation and transfer of As, Cd, Cu, Pb and Zn in the compartments of a soil-diet-wood mouse (Apodemus sylvaticus) food chain at five sites located along a metal pollution gradient. We observed a clear gradient in metal exposure at increasing distance from the smelter in all compartments of the food chain for the non-essential metals. The gradient was less clear or absent for the essential metals in acorn and mice target tissues. Regression analysis showed overall strong relationships within the soil-diet and diet-wood mouse compartments for the non-essential metals, while relationships for the essential metals were weak or absent. Total metal in soil appeared as a better predictor for the diet metal content than the available metal fraction. Our results suggest a more important transfer of non-essential elements through the food chain than essential elements, which is probably a consequence of homeostatic control of the latter group.

Animals↗

Heavy metal stabilization in municipal solid waste incineration flyash using heavy metal chelating agents.

Heavy metal chemical stabilization with synthesized heavy metal chelating agent was assessed for flyash from municipal solid waste incinerator. Flyash can contain heavy metals (e.g. Pb, Cd) which can leach. A new kind of heavy metal chelating agent showed more attractive competition than inorganic chemicals in stabilizing flyash. The synthesizing method of this kind of heavy metal chelating agent was explained in this paper, and the technology process and treatment efficiency of the chelating agent in treating flyash were experimentally studied, which was compared with the results of inorganic chemical agents such as sodium sulfide and lime. The heavy metals in flyash were stabilized more effectively by using heavy metal chelating agents than by using sodium sulfide and lime, furthermore, the stabilized products using the chelating agents can meet the landfill disposal controlling standards for heavy metal waste. pH-dependent leaching experiment showed the stabilized flyash by treatment with heavy metal chelating agent could keep long-term stabilization within a broad range of pH value. Thus, the risk of secondary pollution for the stabilized products was reduced dramatically when the environment condition changes during its disposal period.

Carbon↗

Spectrophotometric evaluation of the optical influence of different metal alloys and porcelains in the metal-ceramic complex.

STATEMENT OF THE PROBLEM: Color matching between natural teeth, shade guides, and metal-ceramic restorations is a common clinical problem. Difficulties related to color matching arise from structural differences that exist between metal-ceramic crowns and natural teeth, the limited range of available ceramic shades, inadequate shade guides, different types of metal alloys, and varying compositions of ceramic materials. PURPOSE: The aim of this study was to investigate the influence of various metal alloys and 2 porcelains on the final color of metal-ceramic complex. Material and methods Four commercial alloys for metal-ceramic restorations, a Ni-Cr (Thermobond), a Co-Cr (Wirobond), a Pd-rich noble (Cerapal-2), and a high noble Au-alloy (V-Delta) were combined with 2 porcelains (Vita Omega and Ceramco Silver) in metal-ceramic specimens with a standardized thickness of layers. Five disc-shaped (10 x 1 mm) specimens were prepared for each alloy/porcelain combination. Only opaque and dentin layers were applied (shade A3). The specimens were analyzed with a spectrophotometer, and data were obtained in the CIE Lab color system. The recorded data were analyzed with a 2-way multiple analysis of variance , a pair-wise comparison of group means (Student's t test), and finally, a categorical regression analysis of variance (CATREG) (alpha=.01). RESULTS: The types of alloy substrate and overlying porcelain significantly affected the color (P < .01). Au and Co-Cr alloys were found to be brighter (higher L* values) than the Ni-Cr and the Pd alloys ( P <.01, SE 0.239). Ceramco porcelain was found to be most red (higher a* values) of all tested alloys ( P <.01). Gold and Pd alloys caused a yellow shift to the metal-ceramic color compared to the Ni-Cr and the Co-Cr alloys with both porcelains ( P < .01, SE 0.165). The detected color differences were visually perceptible for some alloy-porcelain combinations. CONCLUSIONS: The final color of metal ceramic specimens was influenced both from the type of alloy substructure and from the type of overlying porcelain.

Chromium Alloys↗