Lead (Pb) is a toxic element to humans (Carrington et al., 2019;Wani et al., 2015) and accumulation in marine biota a pathway of exposure (Burger et al., 2012;Zimmer et al., 2011). Lead emissions from coal combustion and the use of tetraethyllead as an additive to gasoline through the twentieth century (McConnell & Edwards, 2008;Pacyna & Pacyna, 2001) resulted in large scale atmospheric deposition of anthropogenic Pb across the surface ocean (Boyle et al., 2014). Whilst Pb concentrations across the North Atlantic are now declining, they remain above pre-industrial concentrations (Kelly et al., 2009;Noble et al., 2015). The ultimate fate of Pb in the marine environment is governed by its high affinity to particles (Dewey et al., 2021;Yang et al., 2015), which results in a dissolved Pb (dPb) distribution strongly affected by lateral transfer within sinking matter and burial in sediments (Bruland et al., 2013). However, a growing number of studies have shown intermittent release of dPb from shelf sediments (Cobelo-García & Prego, 2004;Kalnejais et al., 2007;Martino et al., 2002). This suggests that shelf sediments affected by a legacy of anthropogenic Pb deposition may continue to act as a dPb source to the water column (Rusiecka et al., 2018;Vieira et al., 2019).