Concentrations of polycyclic aromatic hydrocarbons (PAHs) in liver tissue of golden tilefish collected aboard multiple R/V Weatherbird II cruises in the Gulf of Mexico from 2012-08-13 to 2017-08-01
Funded By:
Gulf of Mexico Research Initiative
Funding Cycle:
RFP-VI
Research Group:
Center for the Integrated Modeling and Analysis of Gulf Ecosystems III (C-IMAGE III)
Erin Pulster
University of South Florida / College of Marine Science
epulster@usf.edu
Fish, polycyclic aromatic hydrocarbons, PAHs, Deepwater Horizon, Liver, Tilefish, Lopholatilus chamaeleonticeps, fish examination
Abstract:
This dataset contains the concentrations of polycyclic aromatic hydrocarbons (PAHs) in liver tissue of golden tilefish (Lopholatilus chamaeleonticeps) collected aboard multiple R/V Weatherbird II cruises WB1304 (2012-08-13 to 2012-08-25), WB1403 (2013-08-15 to 2013-08-30), WB1502 (2014-08-05 to 2014-08-20), WB1602 (2015-08-15 to 2015-08-30), WB1603 (2015-09-10 to 2015-10-02), WB1701 (2016-08-02 to 2016-09-09), and WB1736 (2017-07-18 to 2017-08-01) in the Gulf of Mexico during the Gulf of Mexico-wide surveys from 2012-2017. PAH was extracted from livers with a modified QuEChERS (Bond Elut, Agilent Technologies, Santa Clara, CA, USA) method optimized specifically for this study species. Extracts were analyzed using Agilent’s 7890B gas chromatograph (GC) coupled to a 7010 tandem mass spectrometer (MS/MS) operating in multiple reactions mode (MRM). The dataset contains the location, date and concentrations of multiple PAHs, as well as the total concentration of all polycyclic aromatic hydrocarbon (PAHs). Dataset also includes associated biometric description of fish such as sex, length, weight, fish weight, fish mass and mass of the liver. The cruise documentation was provided for the R/V Weatherbird II cruises WB 1304, WB1403, WB1502, WB1602, WB1701, and WB1736 led by chief scientists Dr. Steven Murawski and Dr. David Hollander.
Suggested Citation:
S.M. Snyder, E.L. Pulster and S.A. Murawski. 2019. Concentrations of polycyclic aromatic hydrocarbons (PAHs) in liver tissue of golden tilefish collected aboard multiple R/V Weatherbird II cruises in the Gulf of Mexico from 2012-08-13 to 2017-08-01. Distributed by: GRIIDC, Harte Research Institute, Texas A&M University–Corpus Christi. doi:10.7266/n7-g27a-x012
Publications:
Purpose:
Data were collected to measure the accumulation of polycyclic aromatic hydrocarbons in tissues of a commercially important demersal fish.
Data Parameters and Units:
Cruise (C-IMAGE, Organization leading the cruises); Vessel (R/V Weatherbird II, Research vessel used for the cruises); P.I. of the project (Steve Murawski); Year of sample collection (YYYY); Latitude and longitude of station where fish was caught in decimal degrees; Station where fish was caught; Fish #; Full fish ID (station + fish #); Species samples (Golden Tilefish); Tissue analyzed (Liver); Naphthalene (ng/g wet weight); C2 naphthalene (ng/g wet weight); C3 naphthalene (ng/g wet weight); C4 naphthalene (ng/g wet weight); Acenaphthylene (ng/g wet weight); Acenaphthene (ng/g wet weight); Fluorene (ng/g wet weight); C1 fluorene (ng/g wet weight); C2 fluorene (ng/g wet weight); C3 fluorene (ng/g wet weight); C4 fluorene (ng/g wet weight); Dibenzothiophene (ng/g wet weight); C1 dibenzothiophene (ng/g wet weight); C2 dibenzothiophene (ng/g wet weight); C3 dibenzothiophene (ng/g wet weight); C4 dibenzothiophene (ng/g wet weight); Phenanthrene (ng/g wet weight); Anthracene (ng/g wet weight); C1 Phenanthrene/Anthracene (ng/g wet weight); C2 Phenanthrene/Anthracene (ng/g wet weight); C3 Phenanthrene/Anthracene (ng/g wet weight); C4 Phenanthrene/Anthracene (ng/g wet weight); C5 Phenanthrene/Anthracene (ng/g wet weight); Fluoranthene (ng/g wet weight); Pyrene (ng/g wet weight); C1 fluoranthene/pyrene (ng/g wet weight); C2 fluoranthene/pyrene (ng/g wet weight); C3 fluoranthene/pyrene (ng/g wet weight); C4 fluoranthene/pyrene (ng/g wet weight); C5 fluoranthene/pyrene (ng/g wet weight); Benzo[a]anthracene (ng/g wet weight); Chrysene (ng/g wet weight); C1 benzo[a]anthracene/chrysene (ng/g wet weight); C2 benzo[a]anthracene/chrysene (ng/g wet weight); C3 benzo[a]anthracene/chrysene (ng/g wet weight); C4 benzo[a]anthracene/chrysene (ng/g wet weight); C5 benzo[a]anthracene/chrysene (ng/g wet weight); Benzo[b]fluoranthene (ng/g wet weight); Benzo[k]fluoranthene (ng/g wet weight); Benzo[a]pyrene (ng/g wet weight); Benzo[e]pyrene (ng/g wet weight); Perylene (ng/g wet weight); Indeno[1,2,3-c,d]pyrene (ng/g wet weight); Dibenzo[a,h]anthracene (ng/g wet weight); Benzo[g,h,i]perylene (ng/g wet weight); Sum of all PAH analytes (ng/g wet weight); Fish sex (in binary matrix form); Fish total length (cm); Fish total weight (kg); Fish liver weight (kg); Fish gastrointestinal tract weight (kg); Fish gonad weight (kg), and Total liver lipid (%).
Methods:
Liver samples were extracted using a modified QuEChERS (Bond Elut, Agilent Technologies, Santa Clara, CA, USA) method optimized specifically for this study species.
Instruments:
Extracts were analyzed using Agilent’s 7890B gas chromatograph (GC) coupled to a 7010 tandem mass spectrometer (MS/MS) operating in multiple reactions mode (MRM).
Error Analysis:
A performance-based QA/QC program was implemented to ensure acceptable levels of analytical accuracy and precision following the EPA’s Method 8270D and the National Oceanic and Atmospheric Administration’s quality assurance and quality control plan for DWH Natural Resource Damage Assessment. The program included the analysis of solvent blanks, procedural blanks, sample replicates, matrix spikes, blank spikes, and matrix-matched standards.