Biomass of winter £ounder Pseudopleuronectes americanus, a target species of both recreational and commercial ¢sheries, is at an all-time low (Northeast Fisheries Science Center 2008), and due to new unprecedented regulations, the largest of the three stocks is closed to all ¢shing activities in federal waters (National Oceanic and Atmospheric Activities 2009).Winter £ounder population recovery could be expedited by stock enhancement (Waters 1996; Le Francois, Lemieux & Blier 2002), and experimental stocking studies have been conducted since 1996 in New Hampshire. The goal of past projects has not been to initiate large-scale releases. Instead, ‘responsible approach’ (Blankenship & Leber 1995) has been applied to develop the processes needed to successfully enhance winter £ounder by answering key questions in the event that large-scale stocking efforts occur. Much of the research has focused on optimal release strategies for juvenile winter £ounder. In many stock enhancement programmes, initial survival rates of newly released cultured ¢sh are low (Pitman & Gutreuter 1993; Stottrup & Sparrevohn 2007; Sudo, Kajihara & Fujii 2008). These may be due, in part, to stress responses in hatchery-reared ¢sh causing departures from behavioural norms which result in a higher probability of mortality (Schreck, Olla & Davis1997). Developing release strategies that minimize stress responses and reduce post-release mortality is essential to any enhancement eiort and can be done with a combination of hatchery and ¢eld techniques. One such technique is using acclimation cages in situ. For many ¢sh species, acclimation cages improve post-release survival, growth, and site ¢delity (Koshiishi, Itano & Hirota 1991; Jonssonn, Brannas & Lundqvist1999; Kuwada, Masuda, Shiozawa, Kogane, Imaizumi & Tsukamoto 2000; Brennan, Darcy & Leber 2006; Sparrevohn & Stottrup 2007). For juvenile winter £ounder, predation by green crabs Carcinus maenas is of special concern (Fairchild & Howell 2000;Taylor 2005). Acclimation cages have been used at the release site under the assumption that these cages reduce immediate post-release mortality. Cultured £ounder, stocked into these cages for 48 h, adjust to the release site, hone their burial skills, begin pigment change, recover from the stress of transport to the release site and maintain high site ¢delity post release (Fairchild & Howell 2004; Sulikowski, Fairchild, Rennels, Howell & Tsang 2005, 2006; Fairchild, Rennels & Howell 2009). However, the cages also can be detrimental byattracting predators to the release site. In a recent study, Fairchild, Rennels and Howell (2008) compared green crab density when cages were absent, present but empty Aquaculture Research, 2009, 1^5 doi:10.1111/j.1365-2109.2009.02343.x