N A T I O N A L P E N S I O N C O M M I S S I O N Plot 2774, Shehu Shagari Way, Maitam a District Tel: +234-9-4138736 - 40, 09-6720091, 6720094, 4133398, 4133363 PENCOM/DG/ADM/016/VOL.I 4th September 2006 C I R C U L A R The Chief of Staff to the President The Deputy Chief of Staff to the Vice President Honourable Ministers The Secretary to the Government of the Federation Head of
Bardzo tanie apteki z dostawą w całej Polsce kupic cialis i ogromny wybór pigułek.
Mcconnaughey, ted a., walter h. adey, and allegra m. small community and environmental influences on reef coral calcificationLimnol. Oceanogr., 45(7), 2000, 1667–1671 ᭧ 2000, by the American Society of Limnology and Oceanography, Inc.
Community and environmental influences on reef coral calcification Abstract—Reef corals calcify faster in the presence of non- 1E), the calcifier should fix carbon almost twice as efficient- calcareous algae. Ratios of calcification to photosynthesis ap- ly. Figure 2B and C explore how photosynthesis, calcifica- pear to be affected by the ratio of alkalinity to acidity, which tion, and diffusion interact to control chemistry at the au- controls how efficiently the protons from calcification convert totroph’s absorptive surface. With reduced diffusion bicarbonate to carbon dioxide. By forcing calcifiers to calcify problems, calcareous plants and algae–invertebrate symbio- faster, algal proliferation on nutrient-enriched reefs may ad- ses often adopt massive morphologies.
Gattuso et al. (2000) argued that calcification does not help photosynthesis, based on observations that a coral in-cubated at reduced Ca2ϩ concentrations (2.85 mMol kgϪ1) Reef corals and calcareous algae usually calcify fastest maintained normal photosynthesis but calcified less. Calcium during the daytime and often fix carbon into calcium car- transport inhibitors and Ca2ϩ concentrations below 0.5 mM bonate and biomass at similar rates. Light-enhanced calcifi- have, however, inhibited photosynthesis in other experiments cation has long been recognized (Kawaguti and Sakumoto (reviewed by McConnaughey and Whelan 1997). The dis- 1949; Goreau 1959) but still poses a chicken-and-egg dilem- parity may depend on how strongly the treatment inhibits ma: Does photosynthesis stimulate calcification by raising the proton flux from the calcifying space. This Hϩ flux ap- CO ϭ concentrations and the CaCO saturation state of the pears to be coupled to Ca2ϩ fluxes through Ca2ϩ/2Hϩ ex- change catalyzed by the enzyme Ca2ϩ adenosine triphospha- thereby stimulate photosynthesis? Does photosynthesis pro- tase (ATPase), as illustrated in Fig. 1C. Gattuso’s Ca2ϩ vide metabolic energy to power calcification? We examine concentrations were adequate to support this coupling; these questions and their extension from the organismal to hence, Hϩ fluxes probably continued, supported temporarily by OHϪ and CO ϭ accumulation within the calcifying space.
CO diffusion through the boundary layer surrounding an Gattuso’s experiments therefore demonstrate that photosyn- aquatic autotroph (Fig. 1A) can support photosynthetic rates thesis does not depend on CaCO precipitation, but they do of about 0.2 mol mϪ2 sϪ1, calculated using Fick’s first law, not rule out stimulation by the Hϩ (and Ca2ϩ ) fluxes that with a dissolved molecular CO concentration of 10 Mol produce calcification under normal conditions. In light of kgϪ1, a 50-m–thick boundary layer, and 50% depletion of typical Michaelis curves for photosynthesis (Fig. 1E) and CO level at the autotroph’s absorptive surface. Algae and calcification’s ability to counteract CO depletion (Fig. 2), it corals often have photosynthetic rates that are several times would be surprising if calcification did not sometimes benefit that fast, indicating that they use mainly bicarbonate. How- ever, bicarbonate utilization requires additional protons (Hϩ Calcification and photosynthesis become coupled through ϩ HCO Ϫ ϭ CH O ϩ O ). The protons may derive from H O and HCO Ϫ, with a corresponding efflux of OHϪ and CO ϭ (Fig. 1B). Large OHϪ and CO ϭ effluxes imply alka- linization and therefore CO depletion at the absorptive sur- face. This process reduces photosynthetic efficiency because of the Michaelis kinetics of CO fixation by the enzyme Rub- isco (ribulose bisphosphate carboxylase oxygenase) (Fig.
1E). Calcification (Fig. 1C) provides an alternative proton source and potentially allows autotrophs to avoid most of the alkalinization and CO depletion that otherwise accom- Figure 2A illustrates how photosynthesis and calcification affect the aragonite saturation state (⍀) and molecular CO (reaction 1) was originally postulated to account for 18O and content of tropical surface seawater. Block arrows labeled 13C deficiencies in coral skeletons, which appeared to be ‘‘C’’ and ‘‘NC’’ represent hypothetical calcareous and non- caused by kinetic discrimination against the heavy isotopes calcareous autotrophs that photosynthetically remove 20% of hydroxylation and hydration reactions (Mc- the dissolved inorganic carbon (DIC) initially found in the Connaughey 1989). The conversion of HCO Ϫ to CO (re- seawater. The calcifier has a molar ratio of calcification to action 2) is often catalyzed and can theoretically occur either net photosynthesis (C : P ) of 1.3, which is about average for within the extracellular boundary layer or intracellularly af- reef corals (Gattuso et al. 1999). Although the calcifier and ter importation of HCO Ϫ, Hϩ combinations. Alkaline and noncalcifier have equal photosynthetic rates, the calcifier de- acidic conditions favor reactions 1 and 2, respectively, and pletes molecular CO about one-half as much—by 43%, most calcareous organisms develop recognizable, highly al- compared to the 81% rate associated with the noncalcifier.
kaline calcareous zones that contrast with the noncalcareous, If both obey the same Michaelis curve for CO fixation (Fig.
absorptive regions in which HCO Ϫ assimilation occurs.
Carbon assimilation strategies. (A) CO uptake. (B) HCO Ϫ assimilation using proton equivalents from solution. (C) HCO Ϫ assimilation using protons from calcification. (D) Phos- Photosynthesis, calcification, and seawater chemistry.
phate-proton cotransport. (E) Michaelis curve, illustrating kinetics (A) Effects of photosynthesis (Y axis) and calcification (X axis) on of CO fixation by the enzyme Rubisco. ‘‘C’’ and ‘‘NC’’ refer to molecular CO concentrations (dotted lines, in Mol kgϪ1) and the the hypothetical calcifier and noncalcifier, respectively, in Fig. 2A.
aragonite saturation state (⍀, solid lines with shading) of tropicalsurface seawater. Initial conditions at origin are described in meth-ods. Block arrows ‘‘C’’ and ‘‘NC’’ represent hypothetical calcareousand noncalcareous autotrophs, respectively. (B) CO concentrations These are represented by the lower and upper surfaces, re- at an autotroph’s absorptive surface for C : P ratios of 0, 1.0, 1.3, and 2.0, plotted as a function of the boundary-layer thickness. Pn To successfully couple reactions 1–4, the autotroph bal- ϭ 1 Mol C mϪ2 sϪ1. (C) CO and pH at the autotroph’s absorptive ances the photosynthetic benefits of higher CO concentra- surface for a boundary-layer thickness of 50 tions (Fig. 1E) against the costs of calcification. Calcification ϭ 1 Mol C mϪ2 sϪ1 are plotted as dots along the curves.
Connaughey and Whelan 1997). Each ‘‘CH O’’ unit pro- duced during photosynthesis generates about 6 ATP upon ences calcification rates by individual organisms that stim- respiration, so the cost : benefit ratio of coupling calcification ulate photosynthesis through calcification.
and gross photosynthesis is about (C ϫ 2)/(P ϫ 6) ϭ 1/3 C : P . C : P ratios above 3 appear to be energetically unpro- Materials and methods—Experiments were carried out in a coral reef microcosm located at the Marine Systems Lab- As the protons from calcification are discharged into am- oratory of the Smithsonian Institution of Natural History bient waters (or the boundary layer adjacent to the absorp- (Adey 1983; Small et al. 1998). The microcosm’s main tank tive surface; Fig. 1C), not all react with HCO Ϫ to produce held 400 liters, and associated algal turf scrubbers contained CO . Some protons leak from the absorptive to the calcifying an additional 1,280 liters. Natural sunshine supplied about surface, and more importantly, some are soaked up by bases one-third of the total light, and metal halide bulbs provided such as OHϪ, CO ϭ, and B(OH) OϪ rather than HCO Ϫ. The the remainder. Photosynthetic calcifiers included green algae, alkalinity of solution, which measures the concentration of coralline reds, foraminifera, stony corals, and giant clams.
all bases, therefore affects how much CO can be produced Calcium and bicarbonate were replenished daily to maintain through calcification. Conversely, acids in solution supple- Ca2ϩ Ͼ 10.5 mM LϪ1 and total alkalinity Ͼ 2.40 mEq LϪ1 ment the protons from calcification. Community metabolism during the period when measurements were made in the mi- affects seawater alkalinity and acidity and potentially influ- Changes in water chemistry during daytime incubations of algae and corals. (A) pH.
(B) Total alkalinity. (C) Calculated changes in CO and aragonite saturation states. (D) Coral ϩ Chondria incubations. Dashed lines, microcosm; M ϭ Montipora, squares; A ϭ Acropora, triangles;C ϭ Chondria, circles; Ht and Ho ϭ Halimeda tuna (open diamonds) and H. opuntia (filled dia-monds), respectively. n ϭ 5 Replicates, except Chondria and H. tuna, for which n ϭ 2; standarddeviations are somewhat larger than markers.
For various experiments, corals and algae were placed in cium concentrations were assigned seawater values (B ϭ 1- and 3-liter chambers that were suspended within the mi- 416 ϫ S/35; Ca2ϩ ϭ 10280 ϫ S/35 M kgϪ1) (Millero crocosm. Water-filled chambers provided controls. Pumps 1995). Chemical modeling not tied to the microcosm as- circulated water within the chambers. Incubations lasted 10 sumed that t ϭ 25ЊC and S ϭ 35‰, initially with 10.2 M h, with sampling for O and pH every 2 h and sampling for kgϪ1 dissolved molecular CO ; 1,962 M kgϪ1 total DIC; alkalinity every 4 h. Five replicates were conducted for Ac- 2,300 Eq kgϪ1 alkalinity; and pH 8.0697. Millero’s (1995) ropora, Montipora, and Halimeda tuna and for combinations carbonate system thermodynamics were used throughout.
of Acropora or Montipora with Chondria. Three replicateswere conducted with Chondria and two were conducted for Results—The noncalcareous alga Chondria sp. increased pH but did not change alkalinity, whereas highly calcareous Dissolved oxygen was measured by Winkler titrations, species reduced in terms of alkalinity and did not elevate with a precision based on two to three titrations per sample pH as much (Fig. 3A,B). Chondria reduced molecular CO2 of Ϯ0.94 M LϪ1 (n ϭ 15). Titration alkalinity was deter- concentrations by 73% and increased the aragonite saturation mined with a precision for three replicates of Ϯ0.03 mEq state from ⍀ ഠ3 to 6.2 (Fig. 3C). The corals Acropora and LϪ1 (n ϭ 15). Prior to obtaining measurements, pH elec- Montipora reduced CO by only 22 and 21%, respectively, trodes were calibrated in Fisher-brand buffers (pH, 7.00 and and reduced ⍀ by 11 and 17%, respectively. The lightly 10.00; NIST scale) with a precision of Ϯ0.02, and pH elec- calcareous H. tuna behaved somewhat like the noncalcareous trodes were later recalibrated to the seawater scale (Millero Chondria, whereas the more calcareous H. opuntia behaved 1995) through measurements of a seawater carbon standard provided by Andrew Dixon (Scripps Institution of Ocean- Calcification and photosynthesis generally correlated over ography). DIC, CO concentration, and aragonite saturation the course of the day. Acropora and sometimes H. opuntia state were calculated from pH and alkalinity data.
achieved ratios of calcification to net photosynthesis (C : P ) Calcification was estimated as one-half of alkalinity as high as 1. Calcification and photosynthesis generally de- change, and photosynthesis was estimated as the DIC change clined during the afternoon, with photosynthesis declining minus calcification (Smith and Kinsey 1978). Calculations more sharply. The higher photosynthetic rates in the morning based on microcosm experiments used observed tempera- coincided with higher CO concentrations and lower pH and tures (t ϳ 28ЊC) and salinities (S ϳ 36‰). Borate and cal- O concentrations. Decreased calcification in the afternoon occurred despite higher ⍀, which was, for example, 40%higher during the afternoon in the microcosm. Net calcifi-cation in the microcosm essentially ceased at night, eventhough the water remained supersaturated with respect toaragonite. Calcification and aragonite supersaturation werethus only loosely correlated. The noncalcareous Chondriaand lightly calcareous H. tuna raised ⍀ most strongly,whereas highly calcareous corals and H. opuntia left ⍀ un-changed (or even lowered ⍀) after several hours.
When Chondria and corals were incubated together, pH increased as it did with Chondria alone, but alkalinitydropped rapidly. Calcification rates increased 60% (Acro-pora) and 130% (Montipora) compared with incubations ofcorals alone (Fig. 3D) (Student’s t-test, P ϭ 0.002 and P ϭ0.00002, respectively; n ϭ 5 in both cases.) Thus, the non-calcareous alga apparently stimulated calcification in nearbycorals. Photosynthetic rates in combined incubations werealso somewhat higher than were the sums from separate in-cubations, by values of 7% (Acropora) and 18% (Montipo-ra).
Projected ratio of calcification to photosynthesis (C : Pn ϭ alkalinity : acidity; heavy line), aragonite saturation levels (⍀; Discussion—Autotrophs balance benefits and costs in var- solid line), and inorganic aragonite precipitation rate (dotted line,in ious ways. Chondria and other fleshy algae reduce metabolic mol CaCO mϪ2 sϪ1, calculated from kinetics of Burton and Walter ) in seawater as a function of pH (25ЊC, 35‰, con- costs by not calcifying. (Photosynthesis by such organisms stant total alkalinity ϭ 2,300 Eq kgϪ1).
alkalinizes the water and raises ⍀, but this does not causemuch calcification.) Corals and H. opuntia invest heavily incalcification and enjoy higher CO levels. The lightly cal- cified H. tuna uses an intermediate strategy. The corals cal- cify faster when incubated together with noncalcareous algae McConnaughey and Whelan 1997). Even nonphotosynthetic under more alkaline, CO -depleted conditions, indicating an tissues can calcify through such physiologies. The ability of active effort to forestall CO depletion.
calcifiers to locally elevate ⍀ well beyond ambient values Ambient chemistry affects how much CO is generated by contributes to the loose correlations between ambient ⍀ and a particular amount of calcification. In reaction 4, HCO Ϫ calcification rates observed in the present experiments.
supplies the autotroph with both carbon and protons, and C : Inorganic aragonite precipitation from seawater obeys rate P ratios ϭ 1. However, dissolved bases, including OHϪ, equations such as R ϭ k(⍀ Ϫ 1)1.7 (Burton and Walter 1987) B(OH) OϪ, and CO ϭ, compete with HCO Ϫ for protonation (Fig. 4). The inorganic calcification rate doubles between pH at the organism’s absorptive surface. This increases the 8.0 and 8.2, whereas the C : P ratio projected from the al- amount of calcification required to produce CO (reaction 2) kalinity : acidity ratio increases only 14%. (This assumes by the factor [alkalinity]/[HCO Ϫ]. Dissolved acids, includ- constant alkalinity. A constant DIC scenario produces sim- ing CO and B(OH) , conversely supplement the protons ilar results, whereas calcification increases more strongly from calcification, reducing the amount of calcification re- with pH under a constant CO scenario.) Calcification rates quired by the factor [HCO Ϫ]/[acidity]. The C : P ϭ 1 ratio predicted from ambient ⍀ and the alkalinity : acidity ratio are Nutrients may also affect reef calcification rates. Highly calcareous autotrophs such as corals (e.g., Marubini and Da- Figure 4 plots this predictor of C : P ratio as a function of vies 1996) and coccolithophorids (e.g., Paasche and Brubak pH. Further adjustments related to the different diffusivities 1994) calcify faster when nutrients are scarce and thrive in of various ions have only a small effect. Within the normal nutrient-deficient waters. McConnaughey and Whelan pH range of reef seawater (7.9–8.3), the C : P predictor lies (1997) therefore suggested that calcification assists nutrient between 1.0 and 1.3, a value that is similar to those values uptake. Nutrient-proton cotransport (Fig. 1D) provides one common among highly calcareous corals and algae. Sea- likely mechanism. NO Ϫ and H PO Ϫ uptake in various stud- water pH does not change when calcification and photosyn- ies appear to involve cotransport of at least 1Hϩ and 2–4Hϩ, thesis occur in a 1.2 ratio, which, according to Eq. 5, should respectively (Sakano 1990; Wollenweber 1997). Energeti- occur at a pH of 8.2. Higher pH raises the predicted C : P cally, an ion entering a cell performs the chemical work RT ratio and should stimulate calcification, nudging pH back ln a /a , where R is the gas constant, T is Kelvin temperature, down. This probably helps to maintain reef pH around 8.2.
and a and a are the activities of the chemical inside and Calcifiers tend to isolate their calcification sites, as be- outside of the cell. The electrical work is ZFV, where Z is neath the aboral epithelium of corals, and then raise ⍀ lo- the charge on the ion, F is the Faraday constant, and V is cally through ion transport. pH often exceeds 10 at the cal- the cell’s membrane potential. Adding these terms for a nu- cification site of the alga Chara, and CO ϭ accumulates to trient ion plus ‘‘n’’ protons and rearranging yields log(a /a ) ϭ n(pH Ϫ pH ) ϩ (n ϩ Z)FV/2.3RT Walter H. Adey and Allegra M. Small The final term accommodates additional energy terms such as ATP hydrolysis. V and E are shown as positive so that all terms are additive. If a cell increases (pH –pH ) by 0.5 pH units through calcification, it might therefore accumulate NO Ϫ and H PO Ϫ at least three and 10–100 times more strongly. Extracellular acidification should also improve ADEY, W. H. 1983. The microcosm: A new tool for reef research.
NH ϩ uptake slightly and slow Fe2ϩ oxidation, aiding in as- Coral Reefs 1: 193–201.
similation. Calcification’s potential for improving nutrient BURTON, E. A., AND L. M. WALTER. 1987. Relative precipitation assimilation therefore appears to be substantial. Moreover, rates of aragonite and Mg Calcite from seawater: Temperature seawater pH and alkalinity should affect this physiology or carbonate ion control? Geology 15: 111–114.
much as they affect HCO Ϫ assimilation. Photosynthesis and GATTUSO, J.-P., D. ALLEMAND, AND M. FRANKIGNOULLE. 1999.
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People increase nutrient inputs to many reefs through ag- , S. REYNAUD-VAGANAY, I. BOURGE, P. FURLA, S. ROMAINE- ricultural runoff, sewage disposal, increased erosion, and air- LIOUD, M. FRANKIGNOULLE, AND J. JAUBERT. 2000. Calcifi- borne nutrient transport. Nutrients may directly suppress cal- cation does not stimulate photosynthesis in zooxanthellate
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1304 Cedar LaneSelah, Washington 98942-1717 1Corresponding author ([email protected]).
Girl Power: Estrogen Promotes HSC Self-RenewalEsther and Susan 1Immune Receptors of the Innate and Adaptive System Team, Institut d’Investigacions Biome`diques August Pi i Sunyer, Centre EstherKoplovitz, Rossello´, 149À153, 08036 Barcelona, Spain2Arthritis and Clinical Immunology Program, Oklahoma Medical Research Foundation, 825 NE 13th Street, Oklahoma City, OK 73104, USA*Correspondence: