Our recent attempt to determine ultra-trace level 236 U and 233 U in small volume seawater samples was challenged by high and unstable procedure blanks in our environmental radioactivity laboratory, which used to be a spent fuel research facility. Through intercomparison experiments with different laboratories and background checks on the chemical reagents and laboratory dust, the resuspended U-bearing dust was identified as the dominating source of the 236 U and 233 U contamination.With the implementation of background control (especially dust control) measures, the procedure blanks and detection limits of 236 U and 233 U for the radiochemical separation procedure has been significantly improved by three orders of magnitudes. With well-controlled blanks, the analytical precision for 236 U and 233 U predominantly relies on the AMS counting statistics. Background check and dust control are strongly recommended before the analyses of environmental level long-lived radionuclides (such as 236 U and 233 U) that are conducted in the former or active nuclear facilities, even if clearance of radioactivity relevant for radioprotection was achieved.The long-lived uranium isotope 236 U (t1/2 = 23.4 Myr) has become a popular tracer in oceanic studies because of improved measurement techniques by accelerator mass spectrometry (AMS) and its excellent properties, including high solubility, long residence time, and conservative features. [1][2][3][4] Besides a minor amount of naturally produced 236 U, 5 the majority of environmental 236 U was released through anthropogenic nuclear activities, including atmospheric nuclear weapon tests, 1,6-8 authorized discharges of nuclear reprocessing plants 9 and nuclear accidents [10][11][12] . The pulse injection of anthropogenic 236 U results in a wide scale of 236 U/ 238 U atomic ratios (10 -13 -10 -6 ) in the global oceanic systems (Figure 1), 1,7,[13][14][15][16][17][18][19][20][21][22][23][24][25][26][27][28][29]29,30 which roughly corresponds to a range of (10 3 -10 9 ) atoms/kg for 236 U concentrations in seawater.This makes 236 U a suitable transient tracer to investigate the oceanic circulation patterns, water masses mixing, and transit time.Recent developments of the AMS technique enable the measurement and tracer application of another long-lived anthropogenic uranium isotope 233 U (t1/2 = 0.16 Myr) in the environment. 3,30,31 Different from 236 U, the only massive emission of anthropogenic 233 U occurred during the global fallout of nuclear weapons testing (GF). In contrast, little 233 U is produced by nuclear reactors and released from reprocessing plants or nuclear accidents. 3 The representative level of the 233 U/ 236 U atomic ratio in natural reservoirs exposed to GF is estimated to be (1.40 ± 0.15) × 10 -2 by a recent study on a peat core (Black forest, Germany), 3 while the documented levels in the discharges of the nuclear reprocessing plant at La Hague are 10 -7 -10 -6 (HELCOM MORS Discharge database). 32 In the Irish Sea, an average 233 U/ 236 U atomic ratio of (0.12 ±...