<?xml version="1.0" encoding="UTF-8"?><xml><records><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kathleen Mullen</style></author><author><style face="normal" font="default" size="100%">Briana N Rivera</style></author><author><style face="normal" font="default" size="100%">Lane G Tidwell</style></author><author><style face="normal" font="default" size="100%">Renata Ivanek</style></author><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author><author><style face="normal" font="default" size="100%">Dorothy Ainsworth</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Environmental surveillance and adverse neonatal health outcomes in foals born near unconventional natural gas development activity.</style></title><secondary-title><style face="normal" font="default" size="100%">Sci Total Environ</style></secondary-title><alt-title><style face="normal" font="default" size="100%">Sci. Total Environ.</style></alt-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">Animals</style></keyword><keyword><style  face="normal" font="default" size="100%">Animals, Newborn</style></keyword><keyword><style  face="normal" font="default" size="100%">Environmental Monitoring</style></keyword><keyword><style  face="normal" font="default" size="100%">Female</style></keyword><keyword><style  face="normal" font="default" size="100%">Horses</style></keyword><keyword><style  face="normal" font="default" size="100%">Humans</style></keyword><keyword><style  face="normal" font="default" size="100%">Infant, Newborn</style></keyword><keyword><style  face="normal" font="default" size="100%">Male</style></keyword><keyword><style  face="normal" font="default" size="100%">Natural Gas</style></keyword><keyword><style  face="normal" font="default" size="100%">New York</style></keyword><keyword><style  face="normal" font="default" size="100%">Outcome Assessment, Health Care</style></keyword><keyword><style  face="normal" font="default" size="100%">Pennsylvania</style></keyword><keyword><style  face="normal" font="default" size="100%">Pregnancy</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2020</style></year><pub-dates><date><style  face="normal" font="default" size="100%">2020 Aug 20</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">731</style></volume><pages><style face="normal" font="default" size="100%">138497</style></pages><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">&lt;p&gt;Studies of neonatal health risks of unconventional natural gas development (UNGD) have not included comprehensive assessments of environmental chemical exposures. We investigated a clustering of dysphagic cases in neonatal foals born between 2014 and 2016 in an area of active UNGD in Pennsylvania (PA),USA. We evaluated equine biological data and environmental exposures on the affected PA farm and an unaffected New York (NY) farm owned by the same proprietor. Dams either spent their entire gestation on one farm or moved to the other farm in late gestation. Over the 21-month study period, physical examinations and blood/tissue samples were obtained from mares and foals on each farm. Grab samples of water, pasture soil and feed were collected; continuous passive sampling of air and water for polycyclic aromatic hydrocarbons was performed. Dysphagia was evaluated as a binary variable; logistic regression was used to identify risk factors. Sixty-five foals were born, 17 (all from PA farm) were dysphagic. Odds of dysphagia increased with the dam residing on the PA farm for each additional month of gestation (OR&amp;nbsp;=&amp;nbsp;1.4, 95% CI 1.2, 1.7, p&amp;nbsp;=&amp;nbsp;6.0E-04). Males were more likely to be born dysphagic (OR&amp;nbsp;=&amp;nbsp;5.5, 95% CI 1.2, 24.5, p&amp;nbsp;=&amp;nbsp;0.03) than females. Prior to installation of a water filtration/treatment system, PA water concentrations of 3,6-dimethylphenanthrene (p&amp;nbsp;=&amp;nbsp;6.0E-03), fluoranthene (p&amp;nbsp;=&amp;nbsp;0.03), pyrene (p&amp;nbsp;=&amp;nbsp;0.02) and triphenylene (p&amp;nbsp;=&amp;nbsp;0.01) exceeded those in NY water. Compared to NY farm water, no concentrations of PAHs were higher in PA following installation of the water filtration/treatment system. We provide evidence of an uncommon adverse health outcome (dysphagia) in foals born near UNGD that was eliminated in subsequent years (2017-2019) following environmental management changes. Notably, this study demonstrates that domestic large animals such as horses can serve as important sentinels for human health risks associated with UNGD activities.&lt;/p&gt;
</style></abstract></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>13</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Briana N Rivera</style></author></authors><secondary-authors><author><style face="normal" font="default" size="100%">K. Mullen</style></author></secondary-authors><tertiary-authors><author><style face="normal" font="default" size="100%">Lane G Tidwell</style></author></tertiary-authors><subsidiary-authors><author><style face="normal" font="default" size="100%">R. Ivanek</style></author><author><style face="normal" font="default" size="100%">D. Ainsworth</style></author><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author></subsidiary-authors></contributors><titles><title><style face="normal" font="default" size="100%">Time-Integrated Exposures to Identify Chemical Profiles between Health and Dysphagic Foals </style></title><secondary-title><style face="normal" font="default" size="100%">Society of Toxicology</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">2020</style></year><pub-dates><date><style  face="normal" font="default" size="100%">03/2020</style></date></pub-dates></dates><language><style face="normal" font="default" size="100%">eng</style></language></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>3</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Briana N Rivera</style></author><author><style face="normal" font="default" size="100%">Kathleen Mullen</style></author><author><style face="normal" font="default" size="100%">Lane G Tidwell</style></author><author><style face="normal" font="default" size="100%">Renata Ivanek</style></author><author><style face="normal" font="default" size="100%">Dorothy Ainsworth</style></author><author><style face="normal" font="default" size="100%">Susan C Tilton</style></author><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Determining Environmental Exposure Profiles of Health and Dysphagic Foals</style></title><secondary-title><style face="normal" font="default" size="100%">Society of Environmental Toxicology and Chemistry North America, Toronto, ON</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">2019</style></year><pub-dates><date><style  face="normal" font="default" size="100%">11/2019</style></date></pub-dates></dates><language><style face="normal" font="default" size="100%">eng</style></language></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>3</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Briana N Rivera</style></author><author><style face="normal" font="default" size="100%">Kathleen Mullen</style></author><author><style face="normal" font="default" size="100%">Lane G Tidwell</style></author><author><style face="normal" font="default" size="100%">Renata Ivanek</style></author><author><style face="normal" font="default" size="100%">Dorothy Ainsworth</style></author><author><style face="normal" font="default" size="100%">Susan C Tilton</style></author><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Determining Environmental Exposure Profiles of Health and Dysphagic Foals</style></title><secondary-title><style face="normal" font="default" size="100%">Superfund Research Program, Seattle, WA</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">2019</style></year><pub-dates><date><style  face="normal" font="default" size="100%">11/2019</style></date></pub-dates></dates><language><style face="normal" font="default" size="100%">eng</style></language></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>13</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Briana N Rivera</style></author><author><style face="normal" font="default" size="100%">Kathleen Mullen</style></author><author><style face="normal" font="default" size="100%">Lane G Tidwell</style></author><author><style face="normal" font="default" size="100%">Renata Ivanek</style></author><author><style face="normal" font="default" size="100%">Dorothy Ainsworth</style></author><author><style face="normal" font="default" size="100%">Susan C Tilton</style></author><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Using Passive Samplers to Evaluate Inhalation Exposure</style></title><secondary-title><style face="normal" font="default" size="100%">Military Health System Research Symposium, Kissimmee, FL</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">2019</style></year><pub-dates><date><style  face="normal" font="default" size="100%">08/2019</style></date></pub-dates></dates><language><style face="normal" font="default" size="100%">eng</style></language></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author><author><style face="normal" font="default" size="100%">Brandon Isaacs</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Simultaneous Determination of Arsenic, Selenium, and Antimony in Environmental Samples by Hydride Generation for Inductively Coupled Plasma Atomic Emission Spectrometry Get access Arrow</style></title><secondary-title><style face="normal" font="default" size="100%">AOAC International</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1995</style></year><pub-dates><date><style  face="normal" font="default" size="100%">07/1995</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">78</style></volume><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">&lt;p&gt;Total arsenic, selenium, and antimony are determined simultaneously by inductively coupled plasma atomic emission spectrometry (ICP AES) with hydride vapor generation. A1 g wet, 0.25 g dry, or 10 mL water sample is digested by 1 of 2 methods in a 10 mL volumetric culture tube on a programmed heating block by heating with nitric acid and then boiling in a mixture of sulfuric and perchloric acids. For soils, a 0.25 g sample is digested in a 10 mL volumetric culture tube with hydrochloric acid. After digestion, the sample is treated with additional hydrochloric acid. Arsenic, selenium, and antimony are reduced to their hydrides by sodium borohydride in a simplified continuous- flow manifold. A standard pneumatic nebulizer separates the gaseous hydrides (AsH&lt;sub&gt;3&lt;/sub&gt;, SeH&lt;sub&gt;2&lt;/sub&gt;, and SbH&lt;sub&gt;3&lt;/sub&gt;), which are then quantitated by ICP AES at 193.696,196.026, and 231.147 nm, respectively. The detection limits for As, Se, and Sb are 0.55,1.0, and 0.41 μg/L, respectively. Recoveries from 10 matrixes are 65 to 109%; recovery ranges for As, Se, and Sb are 81–109,87–108, and 65–123%, respectively. The method demonstrates good accuracy and precision for environmental samples and is especially suited for analysis of small samples. It requires no additional apparatus for hydride generation or sample introduction.&lt;/p&gt;
</style></abstract><section><style face="normal" font="default" size="100%">1055</style></section></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author><author><style face="normal" font="default" size="100%">Brandon Isaacs</style></author><author><style face="normal" font="default" size="100%">Mark Tracy</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Cold-Vapor Generation for Inductively Coupled Argon Plasma/Atomic Emission Spectrometric Analysis. Part 3. Mercury Get access Arrow</style></title><secondary-title><style face="normal" font="default" size="100%">AOAC International</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1994</style></year><pub-dates><date><style  face="normal" font="default" size="100%">03/1994</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">77</style></volume><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">&lt;p&gt;A method is presented for the determination of total mercury in environmental samples by inductively coupled argon plasma/atomic emission spectroscopy (ICP/AES) using cold-vapor generation. A 1.0 g or 10 mL test portion is digested 6–12 h in a 16 × 150 mm, 10 mL volumetric test tube at room temperature and is subsequently digested on a programmed heating block at 95°C with trace-metal grade nitric acid. The digested samples are next treated with potassium permanganate and heated between 70 and 95°C; thereafter, oxalic acid is added to reach the final endpoint. The mercury(II) is reduced by sodium borohydride in a simplified continuous manifold. A standard pneumatic nebulizer effects the gas–liquid separation of mercury. Mercury is quantitated by ICP/AES at 194.232 nm. The instrument detection limit for the method is 0.2 μg/L. Water samples are analyzed directly. The detection limit is below the current National Primary Drinking Water Standard Maximum Concentration Limit of 2 μg/L for mercury. For a 10:1 dilution of a nominal 1.0 g solid test portion, the detection limit is 2.0 μg/L. This concentration is also less than the regulatory limit of 200 μg/L for the U.S. Environmental Protection Agency’s Toxicity Characteristic Leaching Procedure. The quantitation is linear up to 300 μg/kg. The method demonstrated statistical control for samples of biological and environmental interest.&lt;/p&gt;
</style></abstract><section><style face="normal" font="default" size="100%">473</style></section></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author><author><style face="normal" font="default" size="100%">Brandon Isaacs</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Determination of Antimony in Environmental Samples by Hydride Generation–Inductively Coupled Plasma Spectrometry Get access Arrow</style></title><secondary-title><style face="normal" font="default" size="100%">AOAC International</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1994</style></year><pub-dates><date><style  face="normal" font="default" size="100%">11/1994</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">77</style></volume><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">&lt;p&gt;Total antimony was determined by inductively coupled plasma atomic emission spectrometry (ICP AES) using hydride vapor generation. A1 g wet, 0.25 g dry, or 10 mL water sample was digested by one of 2 distinct methods in a 10 mL graduated Kimax culture tube on a programmed heating block by heating with nitric acid and then boiling in a mixture of sulfuric acid and perchloric acid. For soils, a 0.25 g sample was digested in a 10 mL volumetric culture tube with hydrochloric acid. After digestion, the samples were treated with hydrochloric acid and potassium iodide. The antimony was then reduced by sodium borohydride to stibine (SbH3) in a simplified, continuous-flow manifold. A standard pneumatic nebulizer effected the gas–liquid separation of SbH&lt;sub&gt;3&lt;/sub&gt;, which was then quantified by ICP AES at 231.147 nm. The instrument detection limit was 0.41 μg/L. Recoveries from 10 matrixes were 80 to 100%, with a typical relative standard deviation of 5.3%. The digestion and analysis methods demonstrated statistical control for samples of environmental and biological interest and are especially well suited to analysis of small samples. This method requires no additional apparatus for hydride generation or sample introduction.&lt;/p&gt;
</style></abstract><section><style face="normal" font="default" size="100%">1562</style></section></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Kim A Anderson</style></author><author><style face="normal" font="default" size="100%">Brandon Isaacs</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Determination of Selenium in Feeds, Premixes, Supplements and Injectable Solutions by ICP-AES Hydride Generation</style></title><secondary-title><style face="normal" font="default" size="100%">AOAC International</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1993</style></year><pub-dates><date><style  face="normal" font="default" size="100%">1993</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">76</style></volume><language><style face="normal" font="default" size="100%">eng</style></language><section><style face="normal" font="default" size="100%">910</style></section></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>27</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">LaFleur, L. L.</style></author><author><style face="normal" font="default" size="100%">Dodo, G</style></author><author><style face="normal" font="default" size="100%">Bousquet, T</style></author><author><style face="normal" font="default" size="100%">Glenn R Wilson</style></author><author><style face="normal" font="default" size="100%">Ikoma, J</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Results of NCASI Analyses of Champion Internation, Cantonment Samples for Selected Chlorinated Phenolics, Total Organic Halogen and PCDD/PCDF</style></title><secondary-title><style face="normal" font="default" size="100%">NCASI</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1989</style></year></dates><language><style face="normal" font="default" size="100%">eng</style></language></record><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>27</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">Dodo, G</style></author><author><style face="normal" font="default" size="100%">Glenn R Wilson</style></author><author><style face="normal" font="default" size="100%">Ikoma, J</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Results of NCASI Analyses of the Scott Paper, Everett Treated Effluent Sample for Selected Resin/Fatty Acids, Chlorinated Phenolic Compounds and Total Organic Halogen</style></title><secondary-title><style face="normal" font="default" size="100%">NCASI</style></secondary-title></titles><dates><year><style  face="normal" font="default" size="100%">1989</style></year></dates><language><style face="normal" font="default" size="100%">eng</style></language></record></records></xml>