JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact support@jstor.org.. Abstract. Four radiotracer releases were performed over an annual period in 1981-1982 to de? termine seasonal variation in indices and pathways of phosphorus spiralling in Walker Branch, a small woodland stream in eastern Tennessee, USA. Each release consisted of an addition of ^370 MBq each of carrier-free 32P04 and 3H20 over a 1 -h period during baseflow. Concentrations of 32P and 3H dissolved in stream water were measured intensively at several stations downstream from the radio? tracer input during and immediately following each release. Activity of 32P in coarse particulate organic matter (CPOM), fine particulate organic matter (FPOM), and aufwuchs was measured 2-3 h after each release and at various intervals for 7 wk. Total biomass of CPOM, FPOM, and aufwuchs at the time of each release was also measured.
Ecological Society of AmericaUptake of 32P04 from the water was greatest in November and lowest in August. Uptake length {Sw) of phosphorus, defined as the average distance travelled by a P04 ion dissolved in water, varied from 22 m in November to 97 m in August. Uptake of 32P04 by CPOM was generally greatest, with ~50% of total uptake, while that by aufwuchs was lowest, with < 15% ofthe total. CPOM abundance was the major determinant of whole-stream P04 uptake rate and Sw. Turnover length {Sp) of phos? phorus, defined as the average distance traveled by an atom of P taken up by particulate material, was short compared to Sw, varying from 1 m in November to 3 m in January. Consequently total spiralling length {S) of P varied from 23 m in November, just after peak autumn leaf fall, to 99 m in August, and reflected primarily the travel of P in the dissolved form.Our results indicate that the greatest increase in Sw (and consequently in S) in Walker Branch occurs in late autumn or winter after storms reduce the abundance of CPOM in the lower portions of the stream bed. Although we calculate that Sp may increase by one to two orders of magnitude for short periods during storms, the greatest effect of storms on P spiralling over the long term is their impact on the quality and quantity of CPOM and FPOM in the stream bed after the return to baseflow. For most of the year, detrital organic carbon probably influences phosphorus spiralling more than phosphorus spiralling influences the processing of organic carbon in Walker Branch. Only during the fall and early winter periods, when CPOM abundance is high and Sw is short, does phosphorus spiralling exert strong control over biotic processes downstream.