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COMMENT Limnol. Oceanogr., 33(5), 1988, 1215-1216 0 1988, by the American Society of Limnology and Oceanography, Inc. The concept of “primary production” in aquatic ecology “Primary production” is a term that appears frequently in the literature, being used loosely to describe production at the base of a conceptual food chain; it is difficult to find an explicit definition (see Odum 197 1; UNESCO 1973; Barnes and Mann 1980; Fogg 1980; Parsons et al. 1984). Terrestrial ecologists use “primary production” to describe an increase in biomass of higher plants and, by analogy, aquatic ecologists have used it to describe micro- as well as macrophytic algal production. During this decade something of a revolution has occurred in our perception of marine ecology with the recognition of the importance of marine bacteria and the “microbial loop” (Azam et al. 1983; Hobbie and Williams 1984). It would appear to be an appropriate time to question the meaning and use of the term “primary production” in aquatic ecology. In higher plants only a few percent of cells are actually photosynthetic. These cells release dissolved organic C (DOC) into the phloem which is then used by heterotrophic cells elsewhere in the plant. When higher plant production is estimated, the biomass of the entire plant and not just of the photosynthetic tissue is considered. By strict analogy, when considering microalgal primary production we should include production by heterotrophs using DOC leaked or released by algae. Before the ramifications of the microbial loop were apparent, UNESCO (1973, p. 9) defined primary production as “the formation of organic particulate material at the primary stages of the food chain.” Such a definition allows inclusion of heterotrophic production but colloquially primary production is considered to be limited to autotrophy or C fixation. The inclusion of heterotrophic microbial activity has the advantage that measure- ments of 14C0, fixation could be considered a better estimate of potential primary production because the significant proportion released or leaked by the algae as DOC (Lancelot and Billen 1985) and subsequently used by heterotrophs would still be included in the estimate of biomass production. Another advantage is that, because marine organisms appear often to feed on particles within certain size ranges and hence, for example, picophytoplankton and bacteria could be preyed upon by the same organism (Goldman and Caron 1985; Fogg 1986), the flow of energy would still be from “primary producers” (in this instance organisms using dissolved matter to produce living particulate matter) to “secondary producers.” There are, however, some important problems to weigh against these arguments. DOC is released by activities other than excess photosynthesis (such as grazing and lysis at death: Cadee 1986) and it may be unlikely that bacteria, or our methods of analysis, will differentiate between “new” and “old” DOC of similar chemistry. Secondly, the conflict between phototrophic and heterotrophic activities, performed by organisms which may compete for common nutrients such as N and P (Currie and Kalff 1984; Laws et al. 1985) may be considered too great to allow inclusion of both within the same trophic level. The concept of primary production that has been borrowed from terrestrial applications appears unsuitable for aquatic use and may be undesirable because it compels us to view aquatic ecosystems in discrete, artificial, trophic levels (Pomeroy 1974). The term has no advantage over more accurate words such as “autotrophic,” “phototrophic,” or “heterotrophic” production which should be substituted. There seems to be a 1215 Comment 1216 compulsion for aquatic scientists to refer to CO2 fixation as “primary production.” What is wrong with the term “CO2 fixation”? It is accurate, concise, and descriptive for the methods most often used. The importance of COZ fixation is in the conversion of radiant to chemical energy, and, as indicators of energy input 14C02 fixation estimates are of undoubted value. But, 14C02 fixation gives an estimate of photosynthesis, not of production (Talling 1984); production has units of Abiomass/space/time (Parsons et al. 1984). Lancelot et al. (1986) and Lohrenz and Taylor ( 1987) described more appropriate methods of estimating production based on determining the rate of protein synthesis, which is at least a direct function of biomass synthesis. Statements claiming “nutrient limitation of primary production” should invariably read “nutrient limitation of phototrophic production.” Frequently, however, such claims should be directed toward limitation of photosynthetic activity because rates of 14C02 fixation and not increase in biomass have been measured. Either way production of predators need not have been limited by such an occurrence provided that there is sufficient particulate material (POM) of suitable size as food. It is essential that scientists define terms simply and rigidly in order to foster a questioning attitude. Whereas a paper titled “Nitrogen limitation of 14C0, fixation” may immediately prompt questions about methodology in the mind of the reader, a title of “Nitrogen limitation of primary production” is much more vague and may not. “Primary production” offers little other than historical convenience. It is used with little thought to mean different things, even within single editions of journals or books. The time has come either to define it properly or to discard it. Kevin J. Flynn School of Biological Sciences University College Swansea Swansea SA2 8PP South Wales, U.K. References AZAM, F., AND OTHERS. 198 3. The ecological role of water-column microbes in the sea. Mar. Ecol. Prog. Ser. 10: 257-263. BARNES, R. K., AND K. H. MANN. 1980. Prologue, p. l-3. In R. S. K. Barnes and K. H. Mann [eds.], Fundamentals of aquatic ecosystems. Blackwell. CADET, G. C. 1986. Organic carbon in the water column and its sedimentation, Fladen Ground (North Sea), May, 1983. Neth. J. Sea Res. 20: 347-358. CURRIE, D. J., AND J. KALFF. 1984. A comparison of the abilities of freshwater algae and bacteria to acquire and retain phosphorus. Limnol. Oceanogr. 29: 298-3 10. FOGG, G. E. 1980. Phytoplankton primary production, p. 24-45. In R. S. K. Barnes and K. H. Mann [eds.], Fundamentals of aquatic ecosystems. Blackwell. 1986. Picoplankton. Proc. R. Sot. Lond. Ser. B 228: l-30. GOLDMAN, J. C., AND D. A. CARON. 1985. Experimental studies on an omnivorous microflagellate: Implications for grazing and nutrient regeneration in the marine microbial food chain. Deep-Sea Res. 8: 899-915. HOBBIE, J. E., AND P. J. LEB. WILLIAMS [EDS.]. 1984. Heterotrophic activity in the sea. NATO Conf. Ser. 4 Mar. Sci. 15. Plenum. LANCELOT, C., AND G. BILLEN. 1985. Carbon-nitrogen relationships in nutrient metabolism of coastal marine ecosystems. Adv. Aquat. Microbial. 3: 263321. -,S.MATHOT,ANDN. J.P. OWENS. 1986. Modelling protein synthesis, a step to an accurate estimate of net primary production: Phaeocystis pouchetii colonies in Belgian coastal waters. Mar. Ecol. Prog. Ser. 32: 193-202. LAWS, E. A., W. G. HARRISON, AND G. R. DITULLIO. 19 8 5. A comparison of nitrogen assimilation rates based on the 15N uptake and autotrophic protein synthesis. Deep-Sea Res. 32: 85-95. LOHRENZ, S. E., AND C. D. TAYLOR. 1987. Primary production of protein: 1. Comparison of net cellular carbon and protein synthesis with 14C-derived rate estimates in steady-state cultures of marine phytoplankton. Mar. Ecol. Prog. Ser. 35: 277292. ODUM, E. P. 197 1. Fundamentals of ecology. Saunders. PARSONS, T. R., M. TAKAHASHI, AND B. HARGRAVE. 1984. Biological oceanographic processes, 2nd ed. Pergamon. POMEROY, L. R. 1974. The ocean’s food web: A changing paradigm. Bioscience 24: 499-504. TALLING, J. F. 1984. Past and contemporary trends and attitudes in work on primary production. J. Plankton Res. 6: 203-2 17. UNESCO. 1973. A guide to the measurement of marine primary production under some special conditions.