14 research outputs found
A rapid method to determine antibiotic residues in milk using liquid chromatography coupled to electrospray tandem mass spectrometry
Residue Analysis of Glyphosate and Aminomethylphosphonic Acid (AMPA) in Soybean Using Liquid Chromatography Coupled with Tandem Mass Spectrometry
Residue Analysis of Glyphosate and Aminomethylphosphonic Acid (AMPA) in Soybean Using Liquid Chromatography Coupled with Tandem Mass Spectrometry
14+ MILLION TOP 1% MOST CITED SCIENTIST 12.2% AUTHORS AND EDITORS FROM TOP 500 UNIVERSITIES Residue Analysis of Glyphosate and Aminomethylphosphonic Acid (AMPA) in Soybean Using Liquid Chromatography Coupled with Tandem Mass Spectrometry
A validated method to quantify folic acid in wheat flour samples using liquid chromatography: tandem mass spectrometry
Determination of Organochlorines in Soil of a Suburban Area of São Paulo Brazil
Technological advances have promoted improvements in several science fields, especially related to environmental and analytical areas with the improvement of detection and development of environmentally friendly extraction techniques. This study applied Quick, Easy, Cheap, Effective, Rugged and Safe method (QuEChERS) for soil extraction and assessed its performance through a validation study using samples from the soil of a contaminated area in Caieiras, SP, Brazil. Nine organochlorine pesticides, including the isomers alpha, beta, gamma and delta- hexachlorocyclohexane; cis- and trans-heptachlor epoxide; cis- and trans-chlordane and heptachlor were analyzed by gas chromatography coupled to electron capture detector. The method was validated according to ISO 5725-4 (2020), EURACHEM (2014) and DOQ-CGCRE-008 (2016). The limits of detection and quantification of the method for the nine organochlorines were α-HCH (1.2 and 12.6 µg kg−1), β-HCH (1.7 and 12.0 µg kg−1), γ-HCH (1.5 and 11.6 µg kg−1), δ-HCH (0.8 and 11.6 µg kg−1), heptachlor (1.0 and 10.8 µg kg−1), cis-heptachlor epoxide (0.9 and 11.5 µg kg−1), trans-heptachlor epoxide (0.9 and 11.5 µg kg−1), cis-chlordane (0.4 and 7.9 µg kg−1) and trans-chlordane (0.5 and 10.9 µg kg−1), respectively, and all of them were within the maximum limits recommended by the EPA for the compounds α-HCH (86.0 and 360.0 µg kg−1), β-HCH (300.0 and 1.3 × 103 µg kg−1), γ-HCH (570.0 and 2.5 × 103 µg kg−1), δ-HCH (not defined), heptachlor (130.0 and 630.0 µg kg−1), cis-/trans-heptachlor epoxide (7.0 and 330.0 µg kg−1), cis-/trans-chlordane (1.77 × 103 and 7.7 × 103 µg kg−1) in residential and industrial soil, respectively. Recovery results were between 65% and 105% for almost all compounds, which is an optimum result for multi-residue analytical methods, considering the complexity of the matrix used in the study. Caieiras presented contamination levels of α-HCH in the range of 2.0 to 66.0 µg g−1, which was higher than the limits established by EPA, corresponding to 0.077 µg g−1 for residential soil and 0.27 µg g−1 for industrial soil. According to the validation study, the analytical method proposed was reliable for organochlorine quantification, and the QuEChERS was considered efficient for organochlorine extraction from soil
Exposure to crack cocaine causes adverse effects on marine mussels Perna perna
Our study aimed to evaluate crack cocaine effects in different life stages of the marine mussel Perna perm. For this purpose, fertilization rate, embryo-larval development, lysosomal membrane stability and DNA strand breaks were assessed. Effect concentrations in gametes and in larval development were found after 1 h (IC50 = 23.53 mg.L-1) and 48 h (IC50 = 16.31 mg.L-1),respectively. The highest tested concentration showing no acute toxicity (NOEC) was 10 mg.L-1, while the lowest observed effect concentration (LOEC) was 20 mg.L-1. NOEC concerning embryo-larval development was 0.625 mg.L-1, while the LOEC was 1.25 mg.L-1. Cyto-genotoxic effects were evidenced in mussels exposed to crack cocaine concentrations ranging from 5 to 500 mu g.L-1. Our results report the first data on effects of an illicit drug to marine organisms and should encourage further ecotoxicological studies of these contaminants of emerging concern in coastal ecosystems.Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)Univ Fed Sao Paulo, Dept Ciencias Mar, Rua Dr Carvalho Mendonga 144, BR-11070102 Santos, BrazilUniv Santa Cecilia, Lab Ecotoxicol, Rua Oswaldo Cruz 266, BR-11045907 Santos, BrazilCIETEC IPEN, CEMSA Ctr Espectrometria Massas Aplicada, Ave Prof Lineu Prestes 2242,Salas 112 & 113, BR-05508000 Sao Paulo, BrazilUniv Estadual Paulista, Campus Litoral Paulista, Inst Biociencias, Infante Dom Henrique S-N, BR-11330900 Sao Vicente, BrazilUniv Fed Sao Paulo, Dept Biociencias, Av Ana Costa 95, BR-11060001 Santos, BrazilUniv Fed Sao Paulo, Dept Ciencias Mar, Rua Dr Carvalho Mendonga 144, BR-11070102 Santos, BrazilUniv Fed Sao Paulo, Dept Biociencias, Av Ana Costa 95, BR-11060001 Santos, BrazilFAPESP: 2015/17329-0CNPq: 402931/2015-7Web of Scienc