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Emerging contaminants, also known as contaminants of emerging concern (CEC), refer to relatively new substances that have recently been recognized as potential environmental contaminants. CECs have attracted a great deal of interest and concern among environmental professionals because of the limited information available on the risks posed to human health and the environment by releasing these toxins. There are few formal studies on the potential human health effects of exposure to specific chemical substances.
Specializing in environmental analysis and environmental consulting and supporting emerging contaminant monitoring programs for many years, Alfa Chemistry can provide tailored solutions for the analysis and assessment of CECs to meet specific testing needs.
Perchlorate, 1,4-dioxane, and PFASs (perfluoroalkyl and poly-fluoroalkyl substances) are some of the most recognizable and well-known examples of emerging contaminants. Perchlorate was included in the first round of UCMR (1996) monitoring (UCMR 1). 1,4-dioxane was included in UCMR 4 and detected more frequently than expected in monitored water systems.
The occurrence of perchlorate in the environment is mainly due to anthropogenic sources. Due to its high nitrate content, it can be used as a fertilizer. In aqueous systems, perchlorate exists in anionic form, most commonly associated with ammonium, potassium, and sodium salts. Perchlorate is highly soluble in water and relatively inert, making it a mobile and persistent contaminant.
Alfa Chemistry uses the IC/MS/MS method to analyze perchlorate, eliminating interference from other anions and the possibility of false positive results.
The primary association of 1,4-dioxane with environmental releases is its use as a stabilizer and chemical inhibitor of chlorinated solvents. Although this is the most common source, it is also used in a variety of other industrial processes. 1,4-Dioxane's physical properties make it particularly challenging to analyze in groundwater sample media.
Alfa Chemistry offers two analytical method options for analyzing 1,4-dioxane when the desired reporting limit is less than 1 ug/L.
Method 8270 SIM incorporating the isotope dilution technique | This technique uses a deuterated form of the target analyte (1,4-dioxane-d8), which is added to each sample as an internal standard for a specific target and incorporated into the sample quantification to standardize extraction recoveries. The method also has the advantage of not being interfered with by chlorinated solvents. |
EPA Method 522 | A modified method using GC/MS SIM (without isotope dilution) was used to analyze 1,4-dioxane in drinking water. The process extracts the water sample through a solid phase extraction (SPE) technique. |
PFAS compounds are an emerging class of contaminants that have attracted a great deal of attention and concern from the environmental community and the public at large. PFAS compounds are highly soluble in water and are chemically stable and persistent.
Alfa Chemistry provides PFAS analytical support using several different procedures depending on the project application.
Drinking water | We provide PFAS analysis by EPA Method 537.1 and EPA Method 533. |
Non-drinking water, soil, and tissue samples | The method is liquid chromatography-tandem mass spectrometry (LC/MS/MS) with SPE, which also utilizes isotope dilution techniques. |
Determination of TOP in water samples | The total oxidizable precursors (TOP) determination is a differential method analysis in which two aliquots of the sample are analyzed. One aliquot is used for pretreatment and the other for post-treatment, which is subjected to strong oxidizing conditions prior to PFAS analysis. The difference in PFAS concentration between the pre-and post-treated samples is defined as the amount of oxidizable precursor present in the sample. |
Designation | Title |
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EPA 332.0 | Determination of perchlorate in drinking water by suppressed conductivity ion chromatography-electrospray ionization mass spectrometry |
EPA 6860 | Determination of perchlorate in water, soil, and solid waste using ion chromatography/electrospray ionization/mass spectrometry (IC/ESI/MS or IC/ESI/MS/MS) |
EPA 522 | Determination of 1,4-Dioxane in Drinking Water by Solid Phase Extraction (SPE) and Gas Chromatography Mass Spectrometry (GC/MS) with Selected Ion Monitoring (SIM) |
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Mass Spectrometry Technology
Liquid Chromatography-Mass Spectrometry (LC-MS): Combines the separation capability of liquid chromatography with the quantitative ability of mass spectrometry, enabling the detection of trace new pollutants in water, such as drug residues and endocrine disruptors.
Gas Chromatography-Mass Spectrometry (GC-MS): Used to detect volatile and semi-volatile organic pollutants, such as solvents and certain drug residues.
Triple Quadrupole Mass Spectrometer (Q-TOF): Used for quantitative analysis of new pollutants, such as decabromodiphenyl ether and polychlorinated naphthalenes.
High-Performance Liquid Chromatography (HPLC)
HPLC-UV: Suitable for detecting organic pollutants with ultraviolet absorption, such as certain drugs and synthetic chemicals.
HPLC-FLD: Used to analyze pollutants with fluorescent properties, offering high sensitivity and selectivity.
Other Equipment
Fourier Transform Infrared Spectrometer (FTIR): Used for analyzing chemical components in complex samples.
Fully Automated Solid-Phase Extraction System: Used for sample pretreatment, improving detection efficiency and accuracy.
Meng, Lingning, et al. Environment International 192 (2024): 109027.
As the pharmaceutical industry develops, halogenated hydrocarbons, which are both key raw materials and emissions from the industry, may be considered emerging atmospheric contaminants due to their toxicity and low atmospheric oxidation.
This study analyzed volatile organic compounds (VOCs) emitted from four pharmaceutical companies. Samples were taken three times from both fixed and fugitive sampling sites at each company. A total of 141 VOCs were identified. The mean concentration and proportion of halogenated hydrocarbons from these companies were the highest compared to other industries in the industrial park, reaching 18.9 ppm and 28.8%, respectively. Fixed emissions from the companies showed the highest concentrations of dichloromethane and chlorobenzene, with mean concentrations of 11.4 ppm and 250.67 ppb, respectively. The mean concentration of fugitive emissions of dichloromethane from these companies was lower than in other pharmaceutical studies. Newly detected halogenated hydrocarbons, such as 1,1-dichloropropanone and dichloronitromethane, present potential non-cancer and cancer risks to workers. Chlorobenzene was identified as a significant potential cancer risk, with a value of 0.00965, and 2,6-dichloropyridine was highlighted as a potential emerging contaminant due to its lower MIR value and higher cancer risk. The study suggests that pharmaceutical companies focus on controlling the emissions of chlorobenzene and dichloromethane, which may be key emerging contaminants, and improve the treatment of waste gases in workshops and sewage stations.
Scur, Rafael, et al. Green Analytical Chemistry (2024): 100118.
Traditional analytical methods for detecting organic contaminants in water are often complex, time-consuming, and require large quantities of chemicals. In this study, we developed an environmentally friendly sample preparation method using Araucaria angustifolia bracts as a natural sorbent in the bar adsorptive microextraction technique.
We analyzed eight emerging contaminants (methyl, propyl, and butylparaben, bisphenols A and F, estradiol, ethinylestradiol, and benzophenone) in river water samples using high-performance liquid chromatography with diode-array detection (HPLC-DAD). Central composite design identified optimal extraction conditions, which involved adding 30% (w/v) NaCl to the sample at pH 6 and allowing it to sit for 180 minutes. Simplex-centroid design indicated that the best desorption solvent was a mixture of acetonitrile and water (3:1) at 80 μL, with a desorption time of 40 minutes. Calibration curves showed correlation coefficients greater than 0.995, and the limits of quantification ranged from 1 to 10 µg/L, with inter-day precision between 13 and 22%. Relative recoveries in two river water samples ranged from 62% to 116%, with relative standard deviations between 5% and 28%, confirming the method's accuracy and precision. This method provides a more environmentally sustainable approach to sample preparation for contaminant analysis.
Méndez-Catalán, Julia, et al. Journal of Chromatography Open 6 (2024): 100178.
The presence of emerging contaminants in water is a significant route of human exposure, potentially leading to severe health effects. Effective elimination of these contaminants through proper treatment is crucial, necessitating the monitoring of effluents from wastewater treatment plants and areas near their discharge points.
This study focuses on developing and validating an analytical method for detecting 15 organic contaminants of emerging concern in both wastewater and seawater samples. The method utilizes an automated solid-phase extraction system and ultra-high-performance liquid chromatography coupled with tandem mass spectrometry. Matrix-matched calibration exhibited good linearity, with determination coefficients ≥ 0.990. An evaluation of the matrix effect revealed substantial signal suppression for most analytes, highlighting the importance of addressing this effect for accurate quantification. Recovery values ranged from 74.7% to 109%, with relative standard deviations ≤ 20.5% for the majority of analytes. In seawater and wastewater samples, 11 target analytes were detected in at least one sample, with concentrations ranging from below the method's limit of quantification to 217 ± 92 ng/L in seawater and up to 2340 ± 107 ng/L in wastewater samples.
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