An Estimate on External Fluxes of Phosphorus and its Environmental Signi®cance in Xiamen Western Sea HUASHENG HONG*, SHAOLING SHANG and BANGQIN HUANG The Research Laboratory of SEDC of Marine Ecological Environment/Environmental Science Research Centre, Xiamen University, Xiamen 361005, People's Republic of China Atmospheric deposition, benthic release, freshwater runo and sewage discharge inputs of phosphorus to the Xiamen Western Sea were estimated. It was found that benthic release was probably most signi®cant, having a ¯ux rate of the order of 1 mmol P m 2 d 1 . The Xiamen Western Sea is P limited, and the results of this study suggest that pulse inputs of P may play an important role in the trig- gering of red tides. Ó 1999 Elsevier Science Ltd. All rights reserved. Keywords: phosphorus; ¯uxes; model; Xiamen Sea; China; Red tide. An increasing body of evidence suggests that red tides may be induced in coastal waters by escalating eutro- phication. It is therefore important to understand how an ecosystem responds to the increasing input of nutri- ents. Xiamen Western Sea is a semi-enclosed bay with an area of 50 km 2 that is subject to many environmental stresses, caused by the rapid economic development of Xiamen (Fig. 1). Phosphorus has been identi®ed as a limiting nutrient in this sea. Furthermore, nutrient en- richment has been implicated in the frequent occurrence of red tide in the inner bay (Zhang, 1988; Chen et al., 1990; 1993a,b). Despite a number of studies in the last ten years, focusing on P in Xiamen Western Sea, the mechanism of P cycling in this water body remains poorly understood. Such information is obviously useful for the long-term management of Xiamen Western Sea. Shang (1995) developed a dynamic box model in an attempt to better understand the dynamics of P in Xi- amen Western Sea. This workerÕs model considered variables such as: the species of P (viz. dissolved inor- ganic phosphorus, i.e., DIP, dissolved organic phos- phorus, i.e., DOP and particulate phosphorus, i.e., PP) and phytoplankton biomass. The following three pro- cesses were also considered in the model (Fig. 2): (a) transport between the segments due to water movement and eddy diusion; (b) internal cycling by biological assimilation, regeneration and transformation; and (c) external input from atmospheric deposition, benthic release, freshwater runo and sewage discharge. In this paper, we estimate: external input to the water body, from various pathways, i.e., atmospheric deposi- tion, benthic release, estuary transport and sewage dis- charge, and the factors controlling them. Furthermore, the kinetics of phosphate uptake for dierent size phy- toplankton was studied and related to the eects of nutrient status in ambient water body. External Input Fluxes of P Atmospheric deposition Atmospheric deposition was considered unimportant, until the last decade, because the air±sea exchange mechanism was poorly understood and experimental methods were not developed. Chen (1989) considered atmospheric input of P to the open ocean to be less signi®cant than that of N. Duce et al. (1991) calculated, however, that the global atmospheric ¯ux of P was greater than that contributed from freshwater runo. The situation is therefore still poorly understood, in particular, in coastal regions where the land-ocean in- teraction is important. Dry deposition can be de®ned as the process by which chemicals are transferred from the atmosphere to the ocean in gaseous or solid phases. Wet deposition is de- ®ned as chemical transfer by rainfall. Both forms of deposition are dicult to measure directly. Indirect ap- proaches (usually by measuring the concentration of chemicals in the collected aerosol particles) are, there- fore, often used to estimate air±sea ¯uxes. In this study, aerosol samples were collected (by the Third Institute of Oceanography, State Oceanic Administration, China) during four seasons, i.e., August 1993, November 1993, January 1994 and May 1994. The P content of the aerosol (C pa ) was measured using a method developed for particulate phosphorus in seawater (Shang and Hong, 1997). Dry deposition ¯ux (Fp), wet deposition PII: S0025-326X(99)00080-6 Marine Pollution Bulletin Vol. 39, Nos. 1±12, pp. 200±204, 1999 Ó 1999 Elsevier Science Ltd. All rights reserved Printed in Great Britain 0025-326X/99 $ - see front matter *Corresponding author. 200