{"refrec":{"BRefID":361051,"RR":"<b>Peperzak, L.</b> (2023). The critical adenosine triphosphate (ATP) concentration in treated ballast water. <i>Mar. Pollut. Bull. 187</i>: 114506. <a href=\"https://dx.doi.org/10.1016/j.marpolbul.2022.114506\" target=\"_blank\">https://dx.doi.org/10.1016/j.marpolbul.2022.114506</a>","BEntID":358766,"PublicFlag":1,"CheckedFlag":0,"wosflag":1,"vabbflag":1,"RefStringPartII":". <i>Mar. Pollut. Bull. 187</i>: 114506. <a href=\"https://dx.doi.org/10.1016/j.marpolbul.2022.114506\" target=\"_blank\">https://dx.doi.org/10.1016/j.marpolbul.2022.114506</a>","DocTypID":8,"DocType":"Journal article","MarineFlag":0,"FreshFlag":0,"BrackishFlag":0,"TerrestrialFlag":0,"Authorstring":"Peperzak, L.","OrigTitleTranslFlag":0,"Authorstringtrunc":"Peperzak, L.","Englishabstract":"<p>    Measuring Adenosine triphosphate (ATP) provides a proxy to check compliance    with IMO's ballast water D-2 standard: <10 cells mL<sup>−1</sup> in the    10–50 μm size class. Measured with standard boiling techniques the ATPconcentration in aquatic eukaryotic microorganisms is 0.6 mol m    <sup>−3</sup>. Model calculations with 10–50 μm spherical organisms show    their ATP content is 0.2 to 20 pg cell<sup>−1</sup>, in line with several    cell lysis data. However, at 10 cells mL<sup>−1</sup>, these ATP contents    lead to a maximum of only 2 to 200 pg ATP mL<sup>−1</sup>, at least 7.5×    below a D-2 test kit 1500 pg ATP mL<sup>−1</sup> upper limit. Differentcell shape and ATP extraction scenarios to reach 1500 pg ATP mL    <sup>−1</sup> are discussed but remain improbable. Because cell lysis data    are inconclusive, and a novel phosphoric acid-benzalkonium chloride method    indicates up to 3× higher ATP concentrations, an independent test kit    validation and a comparison of all three techniques are recommended.</p>","AbstractOtherLang":null,"BibLvlCode":"AS","StandardTitle":"The critical adenosine triphosphate (ATP) concentration in treated ballast water","OrigTitleLangCode":"en","OrigTitleLangCodeExtended":"eng","OrigTitleLangID":15,"DateLastModified":{"date":"2026-04-18 01:32:32.350693","timezone_type":1,"timezone":"+02:00"},"UserAccessRight":null,"UserAccID":null,"AuthorKeywords":"Adenosine triphosphate (ATP); Ballast water; Compliance; Model; IMO; Compliance monitoring devices (CMD); Phosphoric acid benzalkonium chloride (P-BAC)","OtherDescriptors":null,"Notes":null,"AnaPub":2023,"MonPub":null,"DateUpdate":"2023-02-09","DateCreate":"2023-02-09","SecASFANote":null,"ConfID":null,"PeerRev":1,"VlizCoreFlag":1,"WoScode":"WOS:000920866000001","VABBcode":null,"OpenAcc":1,"DOI":"10.1016/j.marpolbul.2022.114506"},"refs":null,"anarec":{"AnaID":361051,"PubliDate":2023,"Pagination":"114506","XtraPublOfAnaID":null,"ISBN":null,"Volume":"187","Issue":null,"BRefMon":null,"BRefMonRR":null,"BRefXtra":null,"BRefXtraRR":null,"SerBRefID":43520,"SerRR":"Marine Pollution Bulletin. 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