Irrigation uses the majority (69%) of fresh groundwater withdrawals in the United States (DeSimone et al., 2015;Dieter et al., 2018). In many aquifers supporting irrigated agriculture, heavy pumping has resulted in unsustainable water-level declines, threatening the economy and environment (Deines et al., 2020;Huggins et al., 2022;Scanlon et al., 2012). As groundwater is a limited resource, how to mitigate these declines to extend the usable lifetime of heavily stressed aquifers is a pressing question (Bierkens & Wada, 2019;Butler et al., 2020b;Castilla-Rho et al., 2019;Gleeson et al., 2020). In semi-arid environments with little access to surface water, groundwater conservation programs that seek to reduce pumping are one of the only viable options to decrease groundwater declines in the near to moderate term (Butler et al., 2020a;Deines et al., 2019;Hu et al., 2010).The fundamental premise of groundwater conservation is to reduce outflows from the aquifer by reducing pumping. However, it is not clear how the effectiveness of such conservation initiatives might change in the future as the hydrological system in areas with groundwater conservation adjusts to the observed pumping reductions (Butler et al., 2020a;Deines et al., 2021;Foster et al., 2017). For example, the transit time for water at the land surface to percolate downward and become groundwater recharge can vary dramatically over the High Plains aquifer due to variations in unsaturated zone thickness and vertical hydraulic conductivity (K Z ), with estimates ranging from decades to centuries (