Entrapped air in soils beneath the water table is one of the key factors controlling the hydraulic behavior under conditions of ponded infiltration, in perched waters, and in unconfined aquifers. The term quasi-saturated soils defines the soils with entrapped air, and the term quasi-saturated hydraulic conductivity defines the relationship between the hydraulic conductivity and entrapped air content. This paper focuses on an investigation of how entrapped air, along with other factors, affects the three-stage temporal behavior of the quasi-saturated hydraulic conductivity of soils. During the first stage the quasi-saturated hydraulic conductivity of soils decreases by as much as 5-8 times, presumably because mobile entrapped air blocks the largest pores. During the second stage, as the mobile entrapped air is discharged from the core, the quasi-saturated hydraulic conductivity of the soils slowly increases. When the mobile air is removed, the remaining immobile entrapped air is discharged as a dissolved phase, and the. quasisaturated hydraulic conductivity increases rapidly by about 1-2 orders of magnitude, essentially reaching the value of the saturated hydraulic conductivity. During the third stage the hydraulic conductivity is decreased to minimum values. The effects of sealing at the soil surface and microbiological activities are assumed to be major factors in the final decrease of the hydraulic conductivity. This three-stage temporal behavior of percolation in loam soils is repeatable. A new power law and an exponential relationship are proposed to describe the quasi-saturated hydraulic conductivity of loams as a function of the entrapped air content. in developing (1) a theory of two-phase flow [Morel-Seytoux, 1973], (2) methods for field investigations and monitoring [Stephens et al., 1984], (3) methods for managing groundwater systems for many practical applications, such as irrigation and drainage systems [Powers, 1934; Aver3:anov, 1950; Luthin, 1957], injection of water in the vadose zone [Stephens and Neuman, 1982a; Stephens et al., 1984], secondary water recovery [Moridis and Reddell, 1991a, b], remediation of waste site soils using air barriers [Wilson and Clarke, 1994], artificial recharge of groundwater [Todd, 1980], and (4) designing waste Copyright 1995 by the American Geophysical Union. Paper number 95WR01654. 0043-1397/95/95WR-01654505.00 water treatment plants using filtration and aeration [Sekoulov, 1982; Amirtharajah, 1993]. Air from the atmosphere can migrate down to depths of several meters [Massmann and Farrier, 1992] or as much as 100 m [Montazer et al., 1988] as the atmospheric pressure fluctuates. In the case of soil contamination by volatile organic compounds (VOC), air in the vadose zon e can become mixed with VOC [Cho et al., 1993]. If part of this air has been immobilized as entrapped gas, it can be a long-term source of VOC in the soils. The VOC contained in this immobile air phase is not easily removed during air extraction. Consequently, the effectiveness of remediation activit...