Establishment of a Labile Bound Copper Reference Interval in a Healthy Population via an Inductively Coupled Plasma Mass Spectrometry Dual Filtration-Based Assay.

CONTEXT.­: Clinical testing for Wilson disease (WD) is potentially challenging. Measuring the fraction of labile bound copper (LBC) to total copper may be a promising alternative diagnostic tool with better sensitivity and specificity than some current biomarker approaches. A dual filtration-based inductively coupled mass spectrometry (ICP-MS) assay to measure LBC in serum was developed. OBJECTIVE.­: To establish a reference interval for LBC and LBC to total copper (LBC fraction) in a healthy adult population, and to examine associations between total copper, LBC, and LBC fraction with age, sex, menopausal status, hormone replacement therapy, and supplement use. DESIGN.­: Serum samples were collected from healthy male (n = 110) and female (n = 104) patients between the ages of 19 and 80 years. Total copper and LBC were analyzed using ICP-MS. Results were used to calculate the LBC fraction. Reference intervals were calculated for the 2.5th and 97.5th percentiles for both LBC and LBC fraction. RESULTS.­: The reference intervals for LBC were determined to be 13 to 105 ng/mL and 12 to 107 ng/mL for female and male patients, respectively. The reference intervals for the LBC fraction were 1.0% to 8.1% and 1.2% to 10.5% for female and male patients, respectively. No significant associations were found regarding age, menopausal status, hormone replacement therapy, or vitamin and supplement use. CONCLUSIONS.­: Sex-specific reference intervals have now been established for LBC and LBC fraction. These data in conjunction with further testing of WD populations can be used to assess the sensitivity and specificity of LBC fraction in screening, monitoring, and diagnosis.

Detection of Cadmium and Lead in Kidney Stones. Associations with Patient Demographics, Stone Composition, and Smoking.

BACKGROUND: Kidney stones are a highly prevalent disease worldwide. Additionally, both environmental and occupational exposure to Pb and Cd continue to be prevalent globally and can result in renal toxicity. The objective of this study was to examine the potential presence of Pb and Cd in kidney stones, and to assess for correlation with demographic factors including smoking, gender, age, and kidney stone matrix composition. METHODS: Patient kidney stones (n = 96) were analyzed using Fourier transform infrared spectroscopy to identify the stone constituents. Cd and Pb concentrations (µg/g) were determined by inductively coupled plasma mass spectrometry. Cd and Pb concentrations were correlated using bivariable and multivariable statistical analysis with demographic factors (age, gender, smoking status), and kidney stone composition. RESULTS: Kidney stone Cd (median 0.092 µg/g, range 0.014 to 2.46) and Pb concentrations (median 0.95 µg/g, range 0.060 to 15.4) were moderately correlated (r = 0.56, P < 0.0001). Cd concentrations were positively associated with patient history of smoking, patient age, and calcium oxalate monohydrate levels while negatively associated with struvite and uric acid/uric acid dihydrate. Pb concentrations were positively associated with females and apatite levels while negatively associated with uric acid/uric acid dihydrate. After holding constant other stone type composition levels, smoking status, and age, both Pb and Cd were positively associated with apatite and negatively associated with uric acid/uric acid dihydrate, struvite, and calcium carbonate. CONCLUSIONS: Cd and Pb kidney stone concentrations are associated with specific kidney stone types. Cd and Pb kidney stone concentrations are both associated with smoking.

Assessment of gadolinium and iodine concentrations in kidney stones and correlation with contrast agent exposure, stone matrix composition, and patient demographic factors.

BACKGROUND: Gadolinium-based contrast agents (GBCAs) and Iodinated contrast media are widely utilized to increase medical imaging sensitivity. With predominant renal elimination, the potential for the incorporation of contrast agent derived gadolinium and iodine into kidney stones remains largely uncharacterized. The study objective was to measure gadolinium and iodine concentrations within kidney stones. Observed elemental concentrations were correlated with prior contrast agent administration, kidney stone composition, age, gender, and smoking status. METHODS: Kidney stones from 96 patients were analyzed by Fourier Transform Infrared Spectroscopy to determine stone composition. Residual kidney stone material was digested and analyzed by Inductively Coupled Plasma Mass Spectrometry to determine gadolinium and iodine concentrations. Univariable and multivariable lognormal linear regression were performed to study the relationship between kidney stone element concentrations and contrast agent administration, kidney stone composition, age, gender, and smoking status. RESULTS: Median iodine and gadolinium stone concentrations were 6.4 (range 0.6-3997) and 0.1 (range ≤0.013-113.5) µg/g respectively. Elevated gadolinium was strongly associated with GBCA history with a hazard rate of 2.20 (95 % CI 1.14-3.25 P < 0.001). Gadolinium was positively associated with smoking, as well as stones comprised of apatite and calcium oxalate. Iodine concentrations were negatively associated with uric acid stones. CONCLUSION: Gadolinium, but not iodine, concentrations in kidney stones was strongly correlated with contrast exposure history. Stone matrix composition and demographic factors, particularly smoking, can influence observed kidney stone elemental concentrations. Additional studies are needed to determine if exposure to gadolinium and iodine promote the formation of stone matrix and/or reflect exposure history.

Reliable, Rapid, and Robust Speciation of Arsenic in Urine by IC-ICP-MS.

BACKGROUND: Arsenic is a naturally occurring element with varying species and levels of toxicity. Inorganic arsenic (e.g., arsenite (AsIII) and arsenate (AsV)) are toxic, while its metabolites (e.g., monomethylarsonic acid (MMA) and dimethylarsinic acid (DMA)) are less toxic). Symptoms of exposure can include headaches, confusion, diarrhea, and drowsiness. As these symptoms overlap with many other conditions, arsenic exposure can often be overlooked as a cause. Arsenic toxicity may be treated with chelation and/or electrolyte replacement therapy. However, treatment is not without risks and is unnecessary for exposure to organic (nontoxic) forms of arsenic. This makes screening and differentiation of arsenic important for clinical testing. METHOD: An IC-ICP-MS method was developed using a Dionex 5000 with ion exchange chromatography for separation and iCAP Q for detection. Nontoxic species are arsenobetaine and arsenocholine, and toxic species are AsIII, DMA, MMA, and AsV. RESULTS: Precision, linearity, and specificity studies produced acceptable results. For accuracy, proficiency testing and method comparison samples were analyzed and produced acceptable results. Carryover studies demonstrated single species carryover from the diluter at levels of 500 µg/L, which can be avoided by analysis rules in the standard operating procedure. Limit of detection studies yielded a lower limit of quantitation of 1 µg/L per species. CONCLUSIONS: Here, we present a rapid and reliable method for quantifying and differentiating toxic and nontoxic forms of arsenic to allow for swift and appropriate management of patients with exposure.

Challenges in the Measurement and Interpretation of Serum Titanium Concentrations.

The measurement of circulating metal ion levels in total hip arthroplasty patients continues to be an area of clinical interest. National regulatory agencies have recommended measurement of circulating cobalt and chromium concentrations in metal-on-metal bearing symptomatic total hip arthroplasty patients. However, the clinical utility of serum titanium (Ti) measurements is less understood due to wide variations in reported values and methodology. Fine-scale instrumentation for detecting in situ Ti levels continues to improve and has transitioned from graphite furnace atomic absorption spectroscopy to inductively coupled plasma optical emission spectrometry or inductively coupled plasma mass spectrometry. Additionally, analytical interferences, variable sample types, and non-standardized sample collection methods complicate Ti measurement and underlie the wide variation in reported levels. Normal reference ranges and pathologic ranges for Ti levels remain to be established quantitatively. However, before these ranges can be recognized and implemented, methodological standardization is necessary. This paper aims to provide background and recommendations regarding the complexities of measurement and interpretation of circulating Ti levels in total hip arthroplasty patients.

Certification of Total Arsenic in Blood and Urine Standard Reference Materials by Radiochemical Neutron Activation Analysis and Inductively Coupled Plasma - Mass Spectrometry.

A newly developed procedure for determination of arsenic by radiochemical neutron activation analysis (RNAA) was used to measure arsenic at four levels in SRM 955c Toxic Elements in Caprine Blood and at two levels in SRM 2668 Toxic Elements in Frozen Human Urine for the purpose of providing mass concentration values for certification. Samples were freeze-dried prior to analysis followed by neutron irradiation for 3 h at a fluence rate of 1×1014cm-2s-1. After sample dissolution in perchloric and nitric acids, arsenic was separated from the matrix by extraction into zinc diethyldithiocarbamate in chloroform, and 76As quantified by gamma-ray spectroscopy. Differences in chemical yield and counting geometry between samples and standards were monitored by measuring the count rate of a 77As tracer added before sample dissolution. RNAA results were combined with inductively coupled plasma - mass spectrometry (ICP-MS) values from NIST and collaborating laboratories to provide certified values of (10.81 ± 0.54) µg/kg and (213.1 ± 0.73) µg/kg for SRM 2668 Levels I and II, and certified values of (21.66 ± 0.73) µg/kg, (52.7 ± 1.1) µg/kg, and (78.8 ± 4.9) µg/kg for SRM 955c Levels 2, 3, and 4 respectively. Because of discrepancies between values obtained by different methods for SRM 955c Level 1, an information value of < 5 µg/kg was assigned for this material.