Limnol. Oceanogr., 34(6), 1989, 1025-1033 Q 1989, by the American Society of Limnology and Oceanography, Inc. Diel periodicity in ammonium uptake and regeneration in the oceanic subarctic Pacific: Implications for interactions in microbial food webs Patricia A. Wheeler College of Oceanography, Oregon State University, Corvallis 9733 1 David L. Kirchman College of Marine Studies, University of Delaware, Lewes 19958 Michael R. Landry Department of Oceanography and Hawaii Institute of Geophysics, University of Hawaii, Honolulu 96822 Steven A. Kokkinakis College of Oceanography, Oregon State University Abstract Diel periodicity in NH,’ uptake and regeneration in the nutrient-rich environment of the oceanic subarctic Pacific was examined. Surface water was incubated in large shipboard microcosms that allowed repeated sampling of the planktonic community for NH,+ cycling rates, bacterial production rates, and population densities of the dominant autotrophs and heterotrophs. Changes in NH,+ concentrations and isotopic enrichments indicated that regeneration took place exclusively at night. Nitrogen uptake rates and bacterial production were maximal during the day. Abundance of <2pm autotrophic flagellates reached a maximum at the end of day or beginning of night, whereas abundance of zooflagellates in the <2-~m and I-IO-pm size classes showed a twofold variation with maximal abundances occurring at the beginning of day. These contrasting diel patterns suggest short-term, cyclic disequilibrium in production and grazing within the microbial food web. Hence, analysis of relationships among the various components of microbial populations in this type of environment will require sampling on much shorter time scales than has been attempted in past Ammonium is an important nitrogen source for phytoplankton in both oligotrophic and eutrophic waters. Experimental studies generally report a close coupling between NH,+ uptake and regeneration rates (e.g. Caperon et al. 1979; Glibert 1982; Probyn 1987; Probyn and Lucas 1987), but exceptions have been noted. Harrison et al. ( 1983) found that regeneration rates often exceeded uptake rates in the Middle Atlantic Bight. In contrast, Paasche and Kris- tiansen (1982) and LaRoche (1983) concluded that NH,+ regeneration was not sufficient to meet the uptake requirements of phytoplankton. Diel periodicity in either ammonium uptake or regeneration would result in an apparent discrepancy between the two rates for incubations of ~24 h. An extensive study of diel pcriodicity in NH,+ uptake and regeneration was carried out in the Sargasso Sea (Glibert 1982). Glibert concluded that NH,+ uptake and regeneration were equivalent “within our present analytical resolution.” This conclusion was Acknowledgments largely based on absence of significant Support for this research was provided by NSF grants changes in NH,+ concentration, not on a OCE 86-13878, OCE 86-14170, and OCE 86-14401. comparison of rate measurements. When We thank the captain and crew of RV T. G. Thompboth uptake and regeneration rates were son for their assistance. Joyce Lehner-Fournier and Bruce Monger were responsible for sampling the mimeasured directly, uptake exceeded regencrocosms, and Joyce Lehner-Fournier made all the eration for samplings at 0300 and 1100 population counts. R. Keil helped with measuring bachours, and regeneration (with one excepterial production and primary amine concentrations. tion) exceeded uptake for samplings at 2 100 P. M. Glibert and two anonymous reviewers provided comments on an earlier draft of the manuscript. hours. These results suggest a diel difference 1025 1026 Wheeler et al. in the coupling of the two processes which is generally masked by insufficient analytical resolution in oligotrophic waters. Nutrient levels are high throughout the year in the oceanic subarctic Pacific (Anderson et al. 1969), and there is no evidence of nitrogen-limited phytoplankton growth (Miller et al. 1988). Rapid growth of phytoplankton is indicated by carbon uptake and microscopic estimates of total phytoplankton carbon (Booth et al. 1988). Grazing pressure by microzooplankton is hypothesized to maintain phytoplankton biomass at low and relatively constant levels throughout the year (Frost 1987; Miller et al. 1988). Despite high concentrations of N03- in the oceanic subarctic Pacific, recycled NH,+ is the dominant nitrogen source accounting for about 50% of the total nitrogen used in spring and 75% in late summer (Wheeler 1985). In the present study, we examined diel periodicity in NH,+ uptake and regeneration in the nitrogen-rich environment of the oceanic subarctic Pacific. Both NH,+ concentrations and 15N-isotopic enrichment were monitored during a 48-h. time-course experiment. We also measured bacterial production and the abundances of the dominant autotrophic and heterotrophic picoand nanoplankton in order to relate changes in NH,+ cycling to other microbial processes. Experimental incubations were conducted in large, shipboard microcosms that allowed repeated sampling of the planktonic communities. Methods Experimental work was conducted in June 1987 as part of the SUPER (subarctic Pacific ecosystem research) Program. Shipboard incubations were conducted in 60Liter microcosms made from polyethylene drum liners (J. F. Shelton Co.). The microcosm drums and their operation are described by Landry and Lehner-Fournier (in press). Briefly the drums were closed with a screwtop cap after filling and were sampled through a silicone umbilical cord connecting through the cap to a rigid tube with a flared outlet at the center of the drum. The silicone tubes had stopcocks near the sampling end to completely close the containers when they were not being sampled. The microcosms were screened to the ambient light level at 10-m depth (about 50% incident). To provide gentle mixing, the containers were continuously rotated (about 1 rpm) in a water-cooled incubator. The microcosm drums were soaked with dilute HCl and rinsed with Milli-Q water and seawater before use. The containers were gently filled with seawater collected from 10-m depth at 0130-0430 hours from GoFlo bottles. Isotope additions to the four microcosms were: treatments 1, 2, and 3, +0.5 PM 99.7 atom% 15NH4+; treatment 4, + 10 PM 98.8 atom% 15N03-. Isotopes were mixed into the microcosm containers as lthe filling process neared completion. Initial samples were taken at 0500 hours. Thereafter, at 4-h intervals for the next 48 h e:ach container was sampled for nutrients (NH,+, N03-, NO*-, POd3-, Si04-, and primary amines), particulate nitrogen, and plankton population abundances (phytoplankton, heterotrophic Protozoa, and bacteria). Samples were also taken at each time to determine N03- and NH,+ assimilation and thymidine and leucine incorporation rates and for analysis of the atom% enrichment of dissolved NH4+. Results are plotted 1 h after sample withdrawal to allow for incubation time and sample preparation time. Nutrients (except NH4+) were determined by standard autoanalyzer techniques (Atlas et al. 19’7 1). Ammonium concentrations were determined manually with the phenolhypochlorite method (Stickland and Parsons 1972) scaled down to 10 ml. Primary amines were measured by o-phthalaldehyde fluorescence with glycine as a standard (Parsons et al. 1984). Particulate nitrogen was determined via persulfate digestion of particulate nitrogen (from 500-ml samples) collected on 25-mm GF/F filters and suband sequent :N03- analysis (Strickland Parsons 1972). Slides for enumeration of pica- and nanoplankton populations by epifluorescence microscopy were prepared from 15-ml water samples filtered onto 0.2~pm Nuclepore filters following the DAPI-staining procedure (Porter and Feig 1980). INitrogen uptake rates were determined by measuring rates of assimilation of 15N- NH,+ uptake and regeneration labeled N03- and NH,+ into particulate nitrogen. Isotopic enrichment of particulate nitrogen was measured by emission spectrometry. Samples were prepared by a dry Dumas combustion as described by Whecler and Kirchman (1986). The emission spectrometer was calibrated with Jasco prepared standards, and the atom% enrichment of each sample was determined from the mean of three peak scans. The mean SD for 27 sets of triplicate readings was 0.011 atom% 15N with a mean C.V. of 0.9%. The mean SD for 12 sets of duplicate combustion tubes prepared from the same filter sample was 0.030 atom% 15N with a C.V. of 2.7%. The accuracy of 15N standards dried onto GF/F filters and analyzed by emission spectrometry is within 1% (Dudek et al. 1986). Ammonium regeneration was measured by isotopic dilution. Ammonium in filtrate samples was converted to indophenol (Dudek et al. 1986), which was recovered by a solid-phase extraction (Selmer and Siirensson 1986) with a modification of the rinse and elution solvents. Indophenol was dried onto 47-mm GF/F filters and analyzed for isotopic composition with the same procedure used for labeled particulate nitrogen. The mean SD for 34 sets of triplicate scans was 0.025 atom% 15N, for a C.V. of 0.4%. The mean SD for 15 sets of duplicate extractions from the same filtrate sample was 0.059 atom% 15N, for a C.V. of 1.3%. Bacterial production was determined from the incorporation of [3H-methyl]thymidine and [3H]leucine into the cold, trichloroacctic acid (TCA)-insoluble fraction (Fuhrman and Azam 1980; Kirchman et al. 1985). Briefly, 5 nM [3H]thymidine or 12 nM [3H]leucine were added to duplicate 25-ml subsamples. After 1 h of incubation, subsamples were filtered through Nuclepore filters (0.2~pm pore size) and rinsed twice with cold 5% TCA. Since no significant differences were observed among the three NH,+ treatments, results were pooled across sampling times and the mean and standard error are reported. Similarly, no significant differences were observed among the four treatments for primary amine concentrations, bacterial production, and abundances of autotrophic 1027 and heterotrophic microorganisms. Thus, for these parameters results from the four microcosms were pooled for each sampling time, and the mean and standard error are given. Specific uptake rates were calculated as the rate of increase of atom% enrichment in particulate nitrogen divided by the mean atom% enrichment of dissolved NH4+ (see below). Since isotopic dilution was discontinuous, uptake rates were calculated for specific time intervals. No significant isotopic dilution occurred between 0600 and 1800 hours, so the mean atom% enrichment of NH4+ during this interval was used to calculate uptake rates. Significant isotopic dilution occurred between 1800 and 0200 hours; consequently the mean of the logarithm of NH,+ enrichment (Glibert et al. 1982) was used to calculate uptake rates during this period. Assumption of a linear rather than exponential decrease in NH4+ enrichment would lead to < 10% difference in the estimated uptake rates. Absolute uptake rates were calculated as the specific uptake rate times the mean PN value for each time interval. Ammonium regeneration was calculated with equations presented by Blackburn (1979). Growth rates and mortality rates were estimated from the regression of the natural log of cell abundance against time. Mean abundances for the four treatments were used, and the standard error of the slope is reported when three or four time points were available for the calculation. Daily rates were calculated by multiplying hourly rates by the number of hours in the relevant time interval. It should bc noted that this calculation provides a minimal estimate of growth and mortality since only net changes are considered. Results Ammonium concentrations, uptake, and regeneration - Ammonium concentrations decreased during the first day to about 60% of initial levels and then increased again during the night to N 92% of initial levels (Fig. IA). The mean increase in NH,+ during the first night was 0.128+0.024 PM (mean and SE, n = 3). During the second Wheeler et ~1. 1028 change significantly during the 48-h sampling period (data not shown). z 80 The mean atom% enrichment of dis‘” solved NH,+ for the three NH,+ treatments s 60 0.6 2s ranged from 80 to 96 atom% 15N but showed 5 J s 40 0.4 + no significant change during the first light d period. During the first dark period, the E 20 0.2 mean NH4+ enrichment decreased from 96 I I ’ -I 0 0 to 7 1 atom% 15N (Fig. 1). A similar isotopic an dilution (from 74 to 53 atom% 15N) occurred during the second dark period, but was not accompanied by a further increase in NH,+ concentration. These results indicatc that net uptake of NH,+ occurred during both daylight periods and the second darlk period, while a net increase in NH,+ concentration occurred only during the first dark period. Daylight NH,+ uptake rates averaged 10.9+0.3 nmol liter-l h-l, and dark NH,+ uptake rates averaged 5.6 +0.4 (mean and SE, Table 1). Daylight N03- uptake rates (9.lkO.7 nmol liter-l h-l) were similar to NH,+ uptake rates, but night uptake rates (2.7 rtO.1 nmol liter-l h-l) were significantly lower (mean and SE, Table 1). Uptake rates increased during the second light period, but TIME OF DAY because of depletion of NH4+ and approach Fig. 1. A. Mean concentration (A) and atom% 15N of equilibrium values for N03-, dark uptake of dissolved NH,+ 0 for three microcosms with NH,+ enrichment. B. Net NH,+ uptake (W) and total NH4+ rates for the second dark period could not assimilation (A). C. Total NH,+ depletion from net be accurately determined. As shown by isochanges in chemical concentration m and calculated topic dilution, regeneration of NH,+ ocas the difference between isotopic measurements of curred only during the dark and exceeded uptake and regeneration rates (A). Error bars indicate dark uptake by a factor of three (Table 1). standard errors (n = 3); black bars indicate dark period. Ammonium uptake rates determined by 24-h period, however, NH,+ concentrations assimilation of 15NH,+ and by net changes decreased at a constant rate through the day in NH,+ concentration were similar for the and night. The other inorganic nutrients first 14 h of the incubation (Fig. 1B). Once (N03-, NO;?-, POd3-, and Si04-) did not NH,+ regeneration began, however, the net Table 1. Summary of uptake and regeneration rates (nmol liter-’ h-l), means, and SE with n given in parentheses. (Not determined, - .) .- N source Ammonium Nitrate -- Time interval 0600-2250 2250-1045 1045-1905 1905-0630 0600-2250 2250-1045 1045-l 905 1905-0630 Substrate uptake 3.0.9+0.3(4) 5.6+_0.4(3) 116.6+0.7(3) 9.1 f0.7(4) 2.7&O. l(3) 21.7k5.0(3) - * The lowest rate of regeneration that could be detected in this study was 0.4 nmol .I Regeneration rate is for the interval 2250-0600 hours. liter-’ h-l. Regeneration rate <0.4* 16.1-+0.3-f(3) co.4 16.0-+8.2(3) - - NHik uptake and regeneration change in NH,+ concentration underestimates uptake (Fig. 1B). The difference between NH4+ uptake and regeneration (as determined isotopically) should be equivalent to the net change in NH4+ concentration. Calculated and measured changes in NH,+ concentration show close correspondence (Fig. lC), thus validating the isotopic rate measurements. Bacterial production-With the exception of one high value during the first night, primary amines were high (1144 10 nM, mean and SE, n = 4) during the day and low (50+ 11 nM, mean and SE, n = 4) at night (Fig. 2A). The patterns for both diel cycles were similar. Thus net release of primary amines was maximal at noon, in sharp contrast to the net release of NH4+, which was highest during the first dark period. There was no difference between primary amine concentrations in microcosms receiving NH,+ and N03-. Bacterial production measured by leucine and thymidine incorporation followed the same pattern observed for concentrations of primary amines, i.e. rates were highest at 1400 and lowest at 2300 hours in the dark (Fig. 2). The diel pattern was more evident, however, and production rates were significantly higher during the second 24 h (Fig. 2B, C). Abundances of pica- and nanoplankton Bacterial numbers ranged from 6.2 to 10.2 x 1O5 cells ml-l. Highest numbers (7.8OkO.24 X lo5 cells ml-l, mean and SE, n = 4) occurred between 1400 and 2200 hours but were not significantly higher than the overall mean (7.77f0.14 x lo5 cells ml-l). Autotrophic flagellates ~2 pm in size showed a pronounced daily periodicity in abundance (Fig. 3A). Minimal growth rates (estimated from the increase in cell numbers during the daylight period) were 0.75 and 0.73 d-l for the 2 d, while mortality rates (estimated from decreases in cell numbers during the night) were 0.72 and 0.58 d-l for the 2 d (Table 2). Autotrophic flagellates in the l-lo-pm size class did not show diel periodicity in abundance, but a decrease occurred during the first 12 h and was followed by a continuous increase for the next 36 h (data not shown). Growth and mortality 300 ,- 0600 180 TIME OF DAY Fig. 2. A. Concentration of primary amines. B. Leucine incorporation. C. Thymidine incorporation. Symbols represent mean for four microcosms and error bars indicate standard errors (n = 4); black bars indicate dark period. rates for the l-l O-pm autotrophic flagellates were 0.30 and 0.22 d-l (Table 2). Zooflagellates in the < 2- and l-l O-pm size classes showed similar patterns, with a decline in numbers during the day and increases in numbers at night (Fig. 3B, C). Growth rates for the zooflagellates (from the nighttime increase in abundance) ranged from 0.26 to 1.19 d-l, while estimates of mortality rates during daylight ranged from 0.31 to 1.17 d-* (Table 2). Discussion The large r5NH,+ addition (0.5 PM) to three of the microcosms represented a significant increase over ambient levels, but allowed a 48-h monitoring of uptake and regeneration rates for three parallel incubations with natural microbial communities. Standard practice for determination of Wheeler et al. 1800 0600 TIME OF DAY Fig. 3. A. Abundance of c2-pm autotrophic flagellates. B. Abundance of <2-pm zooflagellates. C. Abundance of l-l O-km zooflagellates. Symbols represent mean for four microcosms and error bars indicate standard errors (n = 4); black bars indicate dark period. “‘in situ” rates is to keep isotopic additions to I 10% of ambient concentrations whenever possible. In the high-nutrient subarctic waters, however, the large isotopic addition did not significantly alter metabolic rates of and N03- upphytoplankton. Ammonium take rates were similar during the light period, suggesting that either nitrogen source can be used to supply phytoplankton nitrogen requirements. Finally, regeneration rates reported here are similar to short-term rate measurements made for bottle incubations with 0.1 PM l 5NH,+ additions (Kirchman et al. 1989). Thus, these data can be considered representative of in situ, water-column rates. Diel periodicity in ammonium remineralization has been difficult to demonstrate in open ocean studies, where low NH,+ con- centrations preclude accurate measurement of isotope dilution (Glibert et al. 1982). Although considerable variability was evident in the 15N data for the first 8 h of our experiment, the subsequent results clearly indicate a rapid regeneration of NH4+ between 1800 and 0200 hours and insignificant regeneration from 0200 to 1800 hours. Caperon et al. (1979) also presented evidence that regeneration of NH,+ was faster at night than during the day, but added that bottle effects may contribute to the difference. Diel periodicity in NH4+ uptake and regeneration has important implications for comparison of uptake and regeneration rates. Paa.sche and Kristiansen (1982) and LaRoche ( 1983) found that regeneration was insufficient to balance uptake rates in Oslofjord and Bedford Basin, respectively. Probyn (1987) found NH,+ assimilation and regeneration to be roughly in balance in the Benguela upwelling region, though notable deviations were evident at low rates, where uptake exceeded regeneration. Uptake and regeneration were roughly in balance in the oligotrophic Agulhas Bank regions (Probyn and Lucas 1987). In these studies only daytime measurements of uptake and regeneration were made, and this bias may be the reason that regeneration rates were less than uptake rates. If diel periodicity occurs in either one or both processes, then accurate daily averages will require repeated shortter:m measurements throughout the diel period. Ammonium can be released by mesozooplankton, microzooplankton, and bacteria. We did not attempt size fractionation of NH,+ regeneration during this study, but changes in abundances of the dominant picoand nanoplankton can be compared with isotopic rate measurements to examine relationships among the members of the microbial community. Maximal bacterial production co-occurs with the highest phytoplankton activity (NH,+ and N03uptake) and the highest levels of dissolved primary amines. Short-term variations (< 24 h) in bacterial production and in situ concentrations of dissolved compounds such as fre:e amino acids (DFAA) are complex. Bacterial production has been observed to peak during the day in freshwater (Jorgensen NH,+ uptake and regeneration 1031 Table 2. Summary of mean growth and mortality rates (d- ‘, &SE) for pica- and nanoplankton (n = 4). Organisms Autotrophic flagellates, < 2 pm Autotrophic flagellates, I-10 pm Zooflagellates, < 2 pm Zooflagellates, I- 10 pm Time interval 0600-1400 0200-l 000 1000-2200 2200-0600 0600-l 800 0600-0600* 0600-l 800 0200-I 000 1000-l 800 1800-0600 0600-l 800 0200-0600 1000-1400 Growth rate Mortality rate 0.75kO.12 0.72f0.01 0.73kO.05 0.58+0.19 0.22kO.03 0.3o-to.03 1.17+0.17 1.19-to.32 0.40+0.07 0.26kO.04 0.76kO.05 0.4220.15 0.3 1-+NA(n = 2) * Second 24-h interval. 198 7, but see Riemann and Sondergaard 1984) and in coastal marine waters (Fuhrman et al. 1985). Likewise, DFAA concentrations are sometimes maximal during the day in lakes (Jorgensen 1987) and coastal marine waters (Carlucci et al. 1984), but exceptions have been observed (Mopper and Lindroth 1982). The coupling between phytoplankton production, levels of free amino acids, and bacterial production may be clearer in open ocean waters, such as the subarctic Pacific where phytoplankton abundance is low and bacterial production may bc limited by the availability of dissolved organic carbon and nitrogen. Daytime peaks in bacterial production in our experiments would seem to indicate that bacteria do not play a significant role in nighttime ammonium regeneration. Phytoplankton biomass in the oceanic subarctic Pacific is dominated by cells < 10 pm in diameter (Booth 1988), and within this size range autotrophic and heterotrophic cells are about equally abundant (Fig. 3). Changes in cell numbers reflect the balance between growth and mortality rates and must be interpreted carefully since we do not have independent estimates of the two components. Increases in the <2-pm autotrophs in the light indicate a mean minimal growth rate of 0.71 d-l. Decreases in abundance of <2-pm zooflagellates during the same period indicate a mortality rate of 0.72 d-l. If grazing pressures on autotrophic and heterotrophic plankton in the <2-pm size class are equivalent, a mean gross growth rate of 1.4 d-l is obtained from the summation of the net increase in numbers of autotrophic cells plus the net decrease in zooflagellates. Both autotrophic and heterotrophic nanoplankton in this study were growing at close to maximal rates expected for the temperature of surface water in the subarctic Pacific during May (Booth et al. 1988). Despite these fast growth rates, abundances were maintained at a relatively constant level over a diel cycle, presumably by grazing. Can the diel changes in pica- and nanoplankton abundances be related to the observed periodicity in NH,+ remineralization? Microzooplankton are important grazers in the subarctic Pacific (Miller et al. 1988; Parsons and Lalli 1988) and presumably are responsible for a significant portion of both grazing pressure on the nanoplankton and NH4+ regeneration. The isotopic dilution results indicate that excretion occurs between 1800 and 0200 hours, while the major increase in zooflagellate abundance occurs between 0200 and 1000 hours. We postulate that grazing and excretion by the zooflagellates occur simultaneously, but that a lag exists between maximal grazing activity and the increase in zooflagellate numbers. Although the length of the cell division period has not been reported for zooflagellates, Heinbokel (1988) has found that oceanic ciliates have a division period of about 8 h and that cell division usually occurs around midnight. The oceanic subarctic Pacific appears to 1032 Wheeler et al. R. W. EPPLEY, A. HAGSTR~M, AND F. AZAM. 1985. 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The presence of low and nearly constant phytoplankton biomass supports characterization of this ecosystem as being close to equilibrium or in “steady state.” Hence, our detection of strong diel periodicity in NH4+ cycling, bacterial production, and abundance of autotrophic and heterotrophic plankton of these waters is significant. Detailed analysis of the interactions among the heterotrophic and autotrophic organisms in such environments will require more frequent sampling than has been attempted in the past. --, NH,+ uptake and regeneration microplankton in an upwelling environment. Mar. Ecol. Prog. Ser. 37: 53-64. -, AND M. I. LUCAS. 1987. Ammonium and phosphorus flux through the microplankton community in Agulhas Bank waters. S. Afr. J. Mar. Sci. 5: 209-22 1. RIEMANN, B., AND M. SONDERGAARD. 1984. Measurements of diel rates of bacterial secondary production in aquatic environments. Appl. Environ. Microbial. 47: 632-638. SELMER, J.-S., AND F. S~RENSSON. 1986. New procedure for extraction of ammonium from natural waters for nitrogen- 15 isotopic ratio determinations. Appl. Environ. Microbial. 52: 577-579. 1033 STRICKLAND, J.D.H., AND T. R. PARSONS. 1972. A practical handbook of seawater analysis, 2nd ed. Bull. Fish. Res. Bd. Can. 167. WHEELER, P. A. 1985. Nitrogen dynamics in the subarctic Pacific. Eos 66: 1274. AND D. L. KIRCHMAN. 1986. Utilization of inorganic and organic forms of nitrogen by bacteria in marine systems. Limnol. Oceanogr. 31: 998-1009. Submitted: 21 June 1988 Accepted: I7 ‘April 1989 Revised: 7 June 1989