Spatial distribution and seasonal variation of phthalate esters in the Jiulong River estuary, Southeast China.

The spatial distribution and seasonal variation of 16 phthalate esters (PAEs) in water, suspended particulate matter (SPM) and sediment were investigated in the Jiulong River estuary, Fujian, Southeast China. Of the 16 PAE congeners analyzed, only six PAEs, including dimethyl phthalate (DMP), diethyl phthalate (DEP), diisobutyl phthalate (DIBP), di-n-butyl phthalate (DBP), di(2-ethylhexyl) phthalate (DEHP) and diisononyl phthalate (DINP), were identified and quantified. The total concentrations of the six PAEs (∑6PAEs) detected for all seasons ranged from 3.01 to 26.4µg/L in water, 1.56 to 48.7mg/kg in SPM, and 0.037 to 0.443µg/kg in sediment. DEHP, DIBP and DBP were the most abundant PAE congeners in all of the water, SPM and sediment phases. The spatial distributions of PAEs in the estuary were controlled not only by the riverine runoff, seasons, hydrodynamic condition and human activities but also the physicochemical properties of PAEs.

Hepatitis B virus pre-existing drug resistant mutation is related to the genotype and disease progression.

INTRODUCTION: Previous studies have indicated that the drug-resistant mutations of hepatitis B virus (HBV) are a major obstacle to antiviral therapy. However, it is still unclear whether there are pre-existent resistance mutations in patients with HBV infection and the relationship between drug-resistant mutation, genotypes, and progression of hepatitis B disease. METHODOLOGY: A total of 357 treatment-naïve patients with HBV infection were involved in this retrospective study. The drug-resistant mutations of HBV reverse transcriptase domain were screened by direct gene sequencing. RESULTS: Lamivudine (LAM) resistance was detected in 8 patients (3.7%) with chronic hepatitis B (CHB), 13 (11.7%) patients with liver cirrhosis (LC), and 6 (21.4%) patients with hepatocellular carcinoma (HCC). Adefovir(ADV)-resistant mutations were detected in 10 (4.6%) patients with CHB, 15 (13.5%) patients with  LC and 4 (14.5%) patients with HCC. Both LAM and ADV resistant mutations were detected in 2 patients (0.9%) with CHB, 1 patient (0.9%) with LC and 1 patient (3.6%) with HCC. Significant differences (p <0.01) were observed in the drug-resistance rates among patients with CHB, LC and HCC. Meanwhile, all the drug-resistant mutations were found in patients with HBV genotype C. CONCLUSIONS: This study demonstrated higher risk of pre-existing drug-resistant mutations in patients with HBV genotype C comparing to patients with HBV genotype B. Likewise, increasing prevalence of pre-existing drug-resistant mutations was shown, alongside with the progression of the disease.

Occurrence, spatial distribution, historical trend and ecological risk of phthalate esters in the Jiulong River, Southeast China.

The occurrence and spatial distribution of phthalate esters (PAEs) in the Jiulong River of southeast China were investigated in water and sediment samples collected from 35 stations along the river in Mar. 2014. The historical trend of the past 26years was reconstructed with a sediment core collected in Dec. 2012 via a 210Pb dating technique. The potential ecological risk of PAEs was assessed using the risk quotient (RQ) method. Of the 16 PAE congeners analyzed, only 6 PAEs, including dimethyl phthalate (DMP), diethyl phthalate (DEP), diisobutyl phthalate (DIBP), di-n-butyl phthalate (DBP), di(2-ethylhexyl) phthalate (DEHP) and diisononyl phthalate (DINP), were identified and quantified; the remaining 10 PAEs were below their respective limits of quantification (LOQs) for the analytical methods used here. The cumulative concentration of 6 PAEs (∑6PAEs) found in the samples spanned a range of 3.48-17.7µg/L in water and 0.046-1.65mg/kg in sediment. The most abundant PAEs in the water-phase were DEHP and DIBP, together accounting for 84.9% of ∑6PAEs in the North River, 82.8% of ∑6PAEs in the West River and 91.6% of ∑6PAEs in the estuary. DEHP and DINP were the richest congeners in the sediment-phase, with proportions of 84.9% in the North River, 81.0% in the West River and 65.4% in the estuary. The spatial distribution of ∑6PAEs in water and sediment phases showed that the riverside environment had influence on the distribution pattern. The reconstruction profile of the PAE congeners and the ∑6PAEs vs the depth of the sediment core indicated that PAEs became increasingly present pollutants around 2006 in the Jiulong River. The results of the potential ecological risk assessment of the RQ method revealed that DIBP and DEHP posed a high risk because of their relatively higher concentrations, while DBP and DINP posed a medium risk to the aquatic system. The baseline data of PAEs in this river will be benefits to the regulatory attention and future strategies of the pollutants control along the river network.

Removal of high-salinity matrices through polymer-complexation-ultrafiltration for the detection of trace levels of REEs using inductively coupled plasma mass spectrometry.

The polymer-complexation-ultrafiltration (PCUF) technique was applied to separate trace levels of rare earth elements (REEs), including scandium, yttrium and the lanthanides, from high-salinity matrices prior to their determination by inductively coupled plasma mass spectrometry (ICP-MS). The REEs were converted into REE-polymer complexes using the water-soluble polymer polyacrylic acid (PAA) at a specified pH, retained on the ultrafiltration membrane of centrifugal filter units, and finally eluted using diluted nitric acid to achieve separation from matrices with relatively high levels of various inorganic ions, such as sodium, potassium, calcium, magnesium, and chlorine ions. Numerous factors affecting the PCUF efficiency were optimized. The optimal conditions included the addition of 30 mg L(-1) of PAA, a pH of 7.5, a reaction time of 40 min at room temperature, and 5.0 mL of 3% nitric acid (v/v) eluent. Under these conditions, the analytes were quantitatively separated and recovered, with a resulting relative standard deviation (RSD) of less than 4.0% (0.05 µg L(-1), n=5) and standard addition recoveries between 89.2% (La) and 95.8% (Sm) for matrices of various salinities. The blank samples for the method ranged from 0.0003 µg L(-1) (Dy) to 0.0031 µg L(-1) (Sc), and the limits of quantification (LOQs, 10σ) were between 0.0006 µg L(-1) (Dy) and 0.0026 µg L(-1) (Sc). Furthermore, the salinity of the sample exhibited no effect on the REE-polymer complex formation process. Finally, the method was successfully applied for the determination of trace levels of dissolved Sc, Y, and lanthanides in coastal and estuarine seawater samples.