by vines (Putz 1988). In fact, site disturbance often leads to an abundance of vine growth (Webb 1958; Putz 1988; Putz 1984). Hommel (1987) suggested that vines might have prevented forest re-colonization on some abandoned fields on Krakatau, thus leaving the system in a scrub state of arrested succession. Bush and others (1995) disagree, suggesting that vines do not appear to have limited forest regeneration on Krakatau. In fact, they concluded that the detrimental effects of vines are certainly more obvious and prevalent on an individual tree basis than for entire communities. While Bush and others (1995) did not specifically support the theory that vines play some significant and beneficial role in succession of forested systems, they did not find any evidence against this theory. In fact, Friedland and Smith (1982) found that herbaceous vegetation rooted within experimental quadrats with vines actually grew taller and had greater mean overall dry biomass weights suggesting an increased growth rate of herbaceous vegetation when growing in competition with vines. In a removal and fertilization experiment on the effects of competitive suppression by vines, Gough and Grace (1997) found that fertilized plots, containing both vines and other vegetation, displayed no overall change in species richness or non-vine vegetative biomass accrual. Additionally, they found that non-vine vegetation biomass increased in sites where vines were removed, but that no significant change occurred in species richness. However, this contradicts Friedland and Smith's (1982) findings for herbaceous vegetation. Whigham (1984) also performed a removal experiment using the hardwood tree Liquidambar styraciflua (sweetgum). He found increased tree growth associated with release from below ground vine competition. However, when the above-ground vine biomass was removed from the trunks and crowns of trees without uprooting the vines, Liquidambar styraciflua showed no improvement in growth. Successional Trends of Vines Some researchers have theorized a shift from herbaceous to woody vines in forested ecosystems over time, and others have suggested that the climbing mode of vines can be used as an estimation of forest maturity (Bush and others 1995; Putz and Chai 1987). In highly disturbed tropical forests and in early successional forests tendrillar species are abundant. As forests mature, the abundance of twining species and root climbers increases proportionately. Carter and others (1987) found that tendrillar vine species are better adapted to climb the structures typical of closed canopy deciduous forests, and are physiologically better adapted to low-light conditions than other vines that have a variety of other climbing mechanisms. Considering the physiological adaptations of early- versus later-successional plants, Carter and others (1987) suggest that physiological performance on disturbed sites might be reduced for the tendrillar vine species as opposed to the non-tendrillar vine species.