“…Most studies use HMDE electrodes, some use MFE electrodes, and there are also many ex situ BiFE electrodes [10,11,14,16,17,36] and gold film electrodes (AuFE) [13,15,[37][38][39], and the later modified electrodes [20,36,[40][41][42][43][44] are applied more for chromium analysis in complex objects. e complex ligands used are DTPA [1,21,22,25,26,28,32,35,45], triethylenetetramine hexaacetic acid (TTHA) [19,29,31,37], diphenylcarbazide (DPCB) [23,29], pyrocatechol violet [24,30], pyrogallol [34], rubeanic acid [33], neo TT [40], and quercetin [20], and the common base ingredients are CH 3 COONa, acetate buffer (CH 3 COOH/CH 3 COONa), and CH 3 COONa/NaNO 3 ; all studies analyzed chromium in river water, seawater, groundwater, tea water, and wastewater, and almost no works have analyzed chromium in sediments by the adsorptive stripping voltammetry method and no author has used in situ BiFE to analyze chromium in environmental objects. Overall, studies have achieved very low detection limits from 10 -9 to 10 -10 M (or from 0.05 ppb to 0.005 ppb).…”