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dc.contributor.authorJohengen, T.
dc.contributor.authorSmith, G.J.
dc.contributor.authorPurcell, H.
dc.contributor.authorLoranger, S.
dc.contributor.authorGilbert, S.
dc.contributor.authorMaurer, T.
dc.contributor.authorGundersen, K.
dc.contributor.authorRobertson, C.
dc.contributor.authorTamburri, M.
dc.date.accessioned2019-01-21T11:52:01Z
dc.date.available2019-01-21T11:52:01Z
dc.date.issued2013
dc.identifier.citationJohengen, T.; Smith, G.J.; Purcell, H.; Loranger, S.; Gilbert, S.; Maurer, T.; Gundersen, K.; Robertson, C. and Tamburri, M. (2013) Performance Verification Statement for the Turner C3 Fluorometer. Solomons MD, Alliance for Coastal Technologies, 73pp. (ACTVS12-03). DOI: http://dx.doi.org/10.25607/OBP-321en_US
dc.identifier.other[UMCES] CBL 2013-020
dc.identifier.urihttp://hdl.handle.net/11329/764
dc.identifier.urihttp://dx.doi.org/10.25607/OBP-321
dc.description.abstractInstrument performance verification is necessary so that effective existing technologies can be recognized, and so that promising new technologies can become available to support coastal science, resource management, and ocean observing systems. The Alliance for Coastal Technologies (ACT) has therefore completed an evaluation of commercially available in situ hydrocarbon sensors. This verification included test applications for: (1) controlled laboratory tanks with additions of various organic, fluorescent compounds, (2) experimental wave tank with additions of two sources of crude oils with and without dispersants, (3) a moored deployment in Baltimore Harbor, and (4) hydrocast surveys in the Gulf of Mexico near a leaking oil barge. In this Verification Statement, we present the performance results of a Turner Designs C3 in situ fluorometer configured for concurrent measurement of refined fuel, crude oil, and CDOM levels. The C3 package tested in this verification integrated the Cyclops Refined Fuel Fluorometer (Ex 254 nm, Em 350 nm), the Cyclops Crude Oil Fluorometer (Ex 320, Em 510) and the Cyclops CDOM fluorometer (Ex 320, Em 470). Response specificity of each individual sensor on the C3 to a range of organic compounds was evaluated in a series of lab tests. Instrument response with respect to challenge compound concentration varied with respect to the inherent fluorescence properties of the challenge compound, as well as, sensor optical configuration. The CDOM sensor detected quinine sulfate (QS) over a large dynamic range (0-5000 ppb tested) and was insensitive to other organic compounds tested. The Crude Oil sensor exhibited a similar but dampened response to QS challenges, as expected based on the optical overlap with the CDOM sensor, but additionally displayed a weak response to carbazole and #2 Diesel Fuel challenges. The Refined Fuel sensor exhibited a lower linear dynamic range (0-100 ppb) and distinct sensitivity to challenge compounds, with sensitivity ranked as Carbazole > #2 Diesel Fuel> NDSA > QS. Instrument responses to various challenge compounds linearly scaled with standardized EEMs fluorescence intensity for each compound as estimated to correspond with the instruments emission optics. The C3 package provided discrimination between crude oil source type and dispersion state during wave tank trials at the COOGER facility at the Bedford Institute of Oceanography. Response sensitivity among the three sensors ranked as Refined Fuel > Crude Oil > CDOM. The Crude Oil and CDOM sensors response baselines were sensitive to daily changes in ambient water CDOM while the Refined Fuel sensor response was dampened to this ambient background. Field deployments in Baltimore Harbor and northern Gulf of Mexico were equivocal as all but three field reference samples were below the limit of detection for total petroleum hydrocarbons (≤ 25 ppb), yet the output of each of the three sensors was significantly above the baseline response in deionized water. Instrument response was consistent with environmental background fluorescence as determined by EEMs analysis for both moored and hydrocast surveys, indicating that ambient fluorescence properties need to be accounted for to make quantitative hydrocarbon estimates from these sensors. During this evaluation, no problems were encountered with the provided software, set-up functions, or data extraction at any of the test sites. One hundred percent of the data was recovered from the instrument and no outlier values were observed for any of the laboratory tests, field deployment tests, or tank exposure tests. Quality assurance (QA) oversight of the verification was provided by an ACT QA specialist, who conducted technical systems audits and a data quality audit of the test data We encourage readers to review the entire document for a comprehensive understanding of instrument performance.en_US
dc.language.isoenen_US
dc.publisherAlliance for Coastal Technologies (ACT)en_US
dc.relation.ispartofseriesACT VS; 12-03
dc.rightsCC0 1.0 Universal*
dc.rights.urihttp://creativecommons.org/publicdomain/zero/1.0/*
dc.titlePerformance Verification Statement for the Turner C3 Fluorometeren_US
dc.typeReporten_US
dc.description.statusPublisheden_US
dc.format.pages73pp.en_US
dc.description.refereedRefereeden_US
dc.publisher.placeSolomons, MDen_US
dc.subject.parameterDisciplineBiogeochemistryen_US
dc.description.currentstatusCurrenten_US
dc.description.eovOcean Colouren_US
dc.description.bptypeBest Practiceen_US
dc.description.bptypeStandard Operating Procedureen_US
obps.contact.contactemailinfo@act-us.info
obps.contact.contactemailTamburri@umces.edu
obps.resourceurl.publisherhttp://www.act-us.info/evaluations.phpen_US


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