Selected naturally regenerated flatwoods forests were burned in preparing a large, long-term study of the effects of several multiple use management practices on forest vegetation and wildlife. Early effects of burning on understory vegetation are reported here. Fire reduced woody understory coverage (from 72 to 66% of surface area), and increased herbaceous species frequency (from 60 to 81%) and herbaceous standing biomass (from 124 to 245 kg/ha). Graphical analyses show an increase in herbaceous species diversity as a result of burning. Successful production of wood, cattle, and wildlife in the southern pinelands depends on methods of managing both overstory and understory simultaneously to increase multiple product yields while avoiding environmental and ecological degradation. In 1976 a large study was begun to examine various effects of an array of forest management practices on wildlife, wildlife habitat, and herbage production. Portions of the study areas have only been burned. Reported here is an early assessment of the effects fire produced on the understory vegetation. Our objective is to show in a simple but compelling way certain beneficial effects of prescribed fire in a forest ecosystem. Study Area and Methods The 73-ha experimental area is on the University of Florida's Austin Cary Memorial Forest near Gainesville, Alachua County, Fla. When this study began the area was occupied by a 50-year old mixed stand of slash and longleaf pine averaging 20.7 m2 of basal area per ha. (This overstory was apparently not altered by the fires described in this paper.) Soils on about 70% of the experimental area are mainly a sandy, siliceous, hyperthermic Ultic haplaquod of the Pomona series. These soils are acid sands that contain an organic stain layer between 41 and 61 cm, and a clay layer at about 109 cm. Basinger fine sand (a siliceous, hyperthermic Spodicpsammaquent), which occurs at slightly lower elevations, occupies about 15%. Sparr sand (a loamy, siliceous, hyperthermic Grossarenic paleudult) and Adamsville sand (a hyperthermic, uncoated Aquic quartzipsamment) occur at slightly higher elevations and occupy most of the remaining 15% of the area. The entire experimental area was prescribe-burned during the winter of 1975-76. Prior to that, the forest had been protected from fire and other disturbances for many years, and consequently the understory was dominated by shrubs, mainly saw-palmetto and common gallberry. Bracken fern was plentiful and pineland threeawn was common in open spaces. Other herbaceous species were scarce and hard to find. Burning was designed to consume as much surface litter and understory biomass as possible with minimum damage to overstory vegetation. The objectives were to improve light penetrations and to expose seeds of desirable plants to mineral soil. Burning took place during February, two or three days after a rain while the Authors are research wildlife biologist (retired) and research forester, Southeastern Forest Exp. Sta., U.S. Forest Serv. and range research biologist, School of Forest Resources and Conservation, Univ. of Florida, Gainesville 32611. soil was moist, air temperature cool, relative humidity high, and wind light and steady. The results were extensive dieback of many shrubs, but shrub consumption by flames was far from complete. In September and October of 1976, six 1-ha plots randomly dispersed over the experimental area were selected for subsequent burning and the understory vegetation on these plots was surveyed. Three 30-m line transects were randomly located in each plot and monumented so they could be relocated. Coverage of all woody vegetation less than 1.5 m aboveground was determined by measuring to the nearest centimeter the portion of each transect covered by crowns of each woody species. In those spaces where woody plants did not cover the transect, measureTable 1. Canopy coverage (%) below 1.5 m of woody plants on line transects following prescribed fires in February 1976 and in February 1978.