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Biogeosciences, 13, 2016www.biogeosciences.net/13/2715/2016/doi:10.5194/bg-13-2715-2016 Author(s) 2016. CC Attribution 3.0 License.
Effect of light on photosynthetic efficiency of sequestered
chloroplasts in intertidal benthic foraminifera
(Haynesina germanica and Ammonia tepida)
Thierry JBruno JEdouard Metzger, Jean-Luc Mouget, Frans Jorissen, and
Emmanuelle Geslin
1UMR CNRS 6112 LPG-BIAF, Bio-Indicateurs Actuels et Fossiles, Université d'Angers, 2 Boulevard Lavoisier,49045 Angers CEDEX 1, France2EA2160, Laboratoire Mer Molécules Santé, 2 rue de la Houssinière, Université de Nantes, 44322 Nantes CEDEX 3, France3BioISI – Biosystems & Integrative Sciences Institute, Campo Grande University of Lisboa, Faculty of Sciences,1749-016 Lisboa, Portugal4EA2160, Laboratoire Mer Molécules Santé, Université du Maine, Ave O. Messiaen, 72085 Le Mans CEDEX 9, France*These authors contributed equally to this work.
Correspondence to: Thierry Jauffrais ([email protected])
Received: 21 December 2015 – Published in Biogeosciences Discuss.: 18 January 2016Revised: 22 April 2016 – Accepted: 25 April 2016 – Published: 10 May 2016
Abstract. Some benthic foraminifera have the ability to
account light history. Additionally, this study showed that the
incorporate functional chloroplasts from diatoms (klepto-
kleptoplasts are unlikely to be completely functional, thus
plasty). Our objective was to investigate chloroplast func-
requiring continuous chloroplast resupply from foraminifera
tionality of two benthic foraminifera (Haynesina german-
food source. The advantages of keeping functional chloro-
ica and Ammonia tepida) exposed to different irradiance
plasts are discussed but more information is needed to better
levels (0, 25, 70 µmol photon m−2 s−1) using spectral re-
understand foraminifera feeding strategies.
flectance, epifluorescence observations, oxygen evolutionand pulse amplitude modulated (PAM) fluorometry (maxi-mum photosystem II quantum efficiency (Fv/Fm) and rapidlight curves (RLC)). Our results clearly showed that H.
germanica was capable of using its kleptoplasts for morethan 1 week while A. tepida showed very limited klep-
Benthic foraminifera colonize a wide variety of sediments
toplastic ability with maximum photosystem II quantum
from brackish waters to deep-sea environments and can be
efficiency (Fv/Fm = 0.4), much lower than H. german-
the dominant meiofauna in these ecosystems (Gooday, 1986;
ica and decreasing to zero in only 1 day. Only H. ger-
Pascal et al., 2009). They may play a relevant role in the
manica showed net oxygen production with a compensa-
carbon cycle in sediments from deep sea (Moodley et al.,
tion point at 24 µmol photon m−2 s−1 and a production up
2002) to brackish environments (Thibault de Chanvalon et
to 1000 pmol O2 cell−1 day−1 at 300 µmol photon m−2 s−1.
al., 2015). Their minor role in organic carbon cycling in aer-
Haynesina germanica Fv/Fm slowly decreased from 0.65 to
obic sediments, compared to bacteria, contrasts with their
0.55 in 7 days when kept in darkness; however, it quickly de-
strong contribution to anaerobic organic matter mineralisa-
creased to 0.2 under high light. Kleptoplast functional time
tion (Geslin et al., 2011) and they can be responsible for up
was thus estimated between 11 and 21 days in darkness and
to 80 % of benthic denitrification (Pina-Ochoa et al., 2010;
between 7 and 8 days at high light. These results emphasize
Risgaard-Petersen et al., 2006).
that studies about foraminifera kleptoplasty must take into
Some benthic foraminiferal species are known to sequester
chloroplasts from their food source and store them in their
Published by Copernicus Publications on behalf of the European Geosciences Union.
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
cytoplasm (Lopez, 1979; Bernhard and Bowser, 1999) in a
tion is poorly known but longer kleptoplast retention times
process known as kleptoplasty (Clark et al., 1990). A klepto-
were found in dark treatments (Lopez, 1979; Correia and
plast is thus a chloroplast, functional or not, that was "stolen"
Lee, 2002b), thus suggesting an effect of light exposure, sim-
and integrated by an organism. Kleptoplastic foraminifera
ilar to what is observed in kleptoplastic sacoglossans (Trench
are found in intertidal sediments (e.g. Haynesina, Elphid-
et al., 1972; Clark et al., 1990; Evertsen et al., 2007; Vieira
ium and Xiphophaga) (Lopez, 1979; Correia and Lee, 2000,
et al., 2009), possibly related to the absence of some compo-
2002a, b; Goldstein et al., 2010; Pillet et al., 2011), low
nents of the kleptoplast photosynthetic protein complexes in
oxygenated aphotic environments (Nonionella, Nonionel-
the host (Eberhard et al., 2008).
lina, Stainforthia) (Bernhard and Bowser, 1999; Grzymski
Most recent studies on kleptoplastic foraminifera focused
et al., 2002) and shallow-water sediments (Bulimina elegan-
on feeding, genetics and microscopic observation related to
tissima) (Bernhard and Bowser, 1999). The role of chloro-
chloroplast acquisition (e.g., Austin et al., 2005; Pillet et al.,
plasts sequestered by benthic foraminifera is poorly known
2011; Pillet and Pawlowski, 2013). To our knowledge lit-
and photosynthetic functions have only been studied in a
tle is known about the effects of abiotic factors on photo-
few mudflat species (Elphidium williamsoni, Elphidium ex-
synthetic efficiency of sequestered chloroplasts in benthic
cavatum and Haynesina germanica) (Lopez, 1979; Correia
foraminifera, particularly on the effect of light intensity on
and Lee, 2000, 2002a, b; F. Cesbron, personal communica-
kleptoplast functionality. Non-invasive techniques are ideal
tion, 2015). Amongst the deep-sea benthic foraminifer living
to follow photosynthesis and some have already been used to
in the aphotic zone, only Nonionella stella has been stud-
study foraminifera respiration and photosynthesis, e.g. oxy-
ied (Grzymski et al., 2002). The authors suggest that the se-
gen evolution by microelectrodes (Rink et al., 1998; Geslin et
questered chloroplasts in this species may play a role in the
al., 2011) or 14C radiotracer (Lopez, 1979). Recently, pulse
assimilation of inorganic nitrogen, even when light is absent.
amplitude modulated (PAM) fluorometry has been used ex-
It has also been hypothesised that chloroplast retention may
tensively in the study of kleptoplastic sacoglossans (Vieira
play a major role in foraminiferal survival when facing star-
et al., 2009; Costa et al., 2012; Jesus et al., 2010; Serodio
vation periods or in anoxic environments (F. Cesbron, per-
et al., 2010; Curtis et al., 2013; Ventura et al., 2013). This
sonal communication, 2015). Under these conditions, klepto-
non-invasive technique has the advantage of estimating rela-
plasts could potentially be used as a carbohydrate source, and
tive electron transport rates (rETR) using rapid light curves
participate in inorganic nitrogen assimilation (Falkowski and
(RLC) and photosystem II (PSII) maximum quantum effi-
Raven, 2007) or, when exposed to light, to produce oxygen
ciencies (Fv/Fm) very quickly and without incubation peri-
needed in foraminiferal aerobic respiration (Lopez, 1979).
ods. The latter parameter has been shown to be a good param-
Foraminifera pigment and plastid ultrastructure studies
eter to estimate PSII functionality (e.g. Vieira et al., 2009;
have shown that the chloroplasts are sequestered from their
Jesus et al., 2010; Serodio et al., 2010; Costa et al., 2012;
food source, i.e. mainly from diatoms (Lopez, 1979; Knight
Curtis et al., 2013; Ventura et al., 2013).
and Mantoura, 1985; Grzymski et al., 2002; Goldstein,
The objective of the current work was to investigate the
2004). This was confirmed by experimental feeding stud-
effect of irradiance levels on photosynthetic efficiency and
ies (Correia and Lee, 2002a; Austin et al., 2005) and by
chloroplast functional times of two benthic foraminifera
molecular analysis of kleptoplastic foraminifera from differ-
feeding in the same brackish areas, H. germanica, which is
ent environments (Pillet et al., 2011; Tsuchiya et al., 2015).
known to sequester chloroplasts and A. tepida, not known
Foraminifera from intertidal mudflat environments (e.g. H.
to sequester chloroplasts. These two species were exposed
germanica, A. tepida) feed mostly on pennate diatoms (Pillet
to different irradiance levels during 1 week and chloroplast
et al., 2011) which are the dominant microalgae in intertidal
efficiency was measured using epifluorescence, oxygen mi-
mudflat sediments (MacIntyre et al., 1996; Jesus et al., 2009).
crosensors and PAM fluorometry.
Furthermore, in these transitional coastal environments (e.g.
estuaries, bays, lagoons) A. tepida and H. germanica are usu-ally the dominant meiofauna species in West Atlantic French
Materials and methods
coast mudflats (Debenay et al., 2000, 2006; Morvan et al.,2006; Bouchet et al., 2009; Pascal et al., 2009; Thibault de
Chanvalon et al., 2015). Their vertical distribution in the sed-iment is characterised by a clear maximum density at the sur-
Haynesina germanica and A. tepida were sampled in January
face (Alve and Murray, 2001; Bouchet et al., 2009; Thibault
2015 in Bourgneuf Bay (47.013◦ N, 2.019◦ W), a coastal bay
de Chanvalon et al., 2015) with access to light, followed by
with a large mudflat situated south of the Loire estuary on the
a sharp decrease in the next two centimetres (Thibault de
French west coast. In this area, all specimens of A. tepida be-
Chanvalon et al., 2015).
long to genotype T6 of Hayward et al. (2004) (M. Schweizer,
Foraminiferal kleptoplast retention times can vary from
personal communication, 2015). In the field, a large amount
days to months (Lopez, 1979; Lee et al., 1988; Correia and
(∼ 20 kg) of the upper sediment layer (roughly first 5 mm)
Lee, 2002b; Grzymski et al., 2002). The source of this varia-
was sampled and sieved over 300 and 150 µm meshes us-
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
ing in situ sea water. The 150 µm fraction was collected in
values of the corresponding epifluorescence photography.
dark flasks and maintained overnight in the dark at 18 ◦C
Higher mean pixel values corresponded to foraminifera emit-
in the laboratory. No additional food was added. In the fol-
ting more fluorescence and thus, as a proxy, contain more
lowing day, sediment with foraminifera was diluted with fil-
chlorophyll. In an RGB image each channel contains pix-
tered (GF/C, 1.2 µm, Whatman) autoclaved sea-water (tem-
els between 0 and 255 values. The majority of the infor-
perature: 18 ◦C and salinity: 32) and H. germanica and A.
mation regarding chlorophyll fluorescence is encoded in the
tepida in healthy conditions (i.e. with cytoplasm inside the
red channel, therefore the green and blue channel were dis-
test) were collected with a brush using a stereomicroscope
carded and only the red channel was kept. The images from
(Leica MZ 12.5). The selected specimens were rinsed sev-
the different treatments were directly comparable as all im-
eral times using Bourgneuf bay filtered-autoclaved seawater
ages were taken using the same acquisition settings. Thus,
to minimize bacterial and microalgal contamination.
the mean red pixel values were used as a proxy for chloro-phyll fluorescence.
Size and biovolume determination
Foraminifera test mean maximal elongation (µm, the lengthof the axes going from the last chamber to the other side
Oxygen was measured using advanced Clark type oxy-
of the test and passing by the umbilicus) was measured us-
gen microelectrodes of 50 µm in diameter (Revsbech, 1989)
ing a micrometre mounted on a Leica stereomicroscope (MZ
(OXI50 – Unisense, Denmark). Electrodes were calibrated
12.5). Mean foraminiferal volume was approximated with
with a solution of sodium ascorbate at 0.1 M (0 %) and with
the equation of a half sphere, which is the best resembling
seawater saturated with oxygen by bubbling air (100 %).
geometric shape for H. germanica and A. tepida (Geslin et
Foraminiferal photosynthesis and oxygen respiration rates
al., 2011). The cytoplasmic volume (or biovolume) was then
were measured following Høgslund et al. (2008) and Geslin
estimated by assuming that the internal test volume corre-
et al. (2011). Measurements were carried out in a micro-tube
sponds to 75 % of the total foraminiferal test volume (Han-
made from glass Pasteur pipette tips with an inner diameter
nah et al., 1994).
of 1 mm. The micro-tube was fixed to a small vial, filled withfiltered autoclaved seawater from Bourgneuf Bay. The vial
was placed in an aquarium with water kept at room temper-ature (18 ◦C). A small brush was used to position a pool of
Pigment spectral reflectance was measured non-invasively
7 to 10 foraminifera in the glass micro-tube after removing
to determine and compare the relative pigment composition
air bubbles. Oxygen micro-profiles started at a distance of
on 50 fresh specimens of H. germanica, on 50 fresh speci-
200 µm above the foraminifers to avoid oxygen turbulences
mens of A. tepida and on a benthic diatom as explained in
often observed around the foraminifers. Measurements were
Jesus et al. (2008). Concisely, a USB2000 (Ocean Optics,
registered when the oxygen micro-profiles were stable; they
Dunedin, FL, USA) spectroradiometer with a VIS-NIR op-
were then repeated five time in the centre of the micro-tube,
tical configuration controlled by OObase32 software (Ocean
using 50 µm steps until 1000 µm away from the foraminifers
Optics B.V., Duiven, the Netherlands) was used. The spec-
(Geslin et al., 2011). The oxygen flux (J ) was calculated us-
troradiometer sensor was positioned so that the surface was
ing the first law of Fick:
always viewed from the nadir position. Foraminiferal re-
flectance spectra were calculated by dividing the upwelling
spectral radiance from the foraminifera (Lu) by the re-flectance of a clean polystyrene plate (Ld) for both of which
where D is the oxygen diffusion coefficient (cm2 s−1) at ex-
the machine dark noise (Dn) was subtracted (Eq. 1).
perimental temperature (18 ◦C) and salinity (32) (Li and Gre-gory, 1974), and dC/dx is the oxygen concentration gradient
2 cm−1). The O2 concentration gradients were cal-
culated with the oxygen profiles and using the R2 of the re-gression line to determine the best gradient. Total O2 con-
sumption and production rates were calculated as the prod-uct of O2 fluxes by the surface area of the micro-tube and
Foraminifera kleptoplast fluorescence was measured using
subsequently divided by the foraminifera number to finally
epifluorescence microscopy (× 200, Olympus Ax70 with
obtain the cell specific rate (pmol O2 cell−1 d−1) (Geslin et
Olympus U-RFL-T, excitation wave length 485 nm). Two
Tif images (1232 × 964 px) of each foraminifer were taken(one bright field photography and one epifluorescence pho-
tography) using LUCIA G™ software. The bright field pho-tography was used to trace the contours of the foraminifer
All pulse amplitude modulated fluorescence measurements
and an ImageJ macro was used to extract the mean pixel
were carried out with a Water PAM fluorometer (Walz, Ger-
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
many) using a blue measuring light. Chloroplast function-
fitted with a Haldane model, as modified by Papacek et
ality was estimated by monitoring PSII maximum quantum
al. (2010) and Marchetti et al. (2013) but without photoin-
efficiency (Fv/Fm) and by using P -I rapid light curve (RLC,
hibition (Eq. 3).
e.g., Perkins et al., 2006) parameters (α, initial slope of theRLC at limiting irradiance; rETRmax, maximum relative
electron transport rate; Ek, light saturation coefficient; and
Eopt, optimum light) (Platt et al., 1980). Rapid light curves
were constructed using eight incremental light steps (0, 4, 15,
(pmol O2 cell−1 d−1), I
20, 36, 48, 64, 90 and 128 µmol photons m−2 s−1), each last-
(µmol photons m−2 s−1),
ing 30 s. The PAM probe was set up on a stand holder at a
stant (µmol photons m−2 s−1) and Rd the dark respiration,
2 mm distance from a group of 10 foraminifera.
expressed as an oxygen consumption (pmol O2 cell−1 d−1).
The initial slope of the P -I (Photosynthesis–Irradiance)
(pmol O2 cell−1 day−1
(µmol photons m−2 s−1)−1) and the compensation irradiance
Haynesina germanica, a species known to sequester chloro-
Ic were calculated according to Eqs. (4) and (5).
plasts, were placed in plastic Petri dishes and starved for7 days under three different light conditions: dark (D and
Dark-RLC), low light (LL, 25 µmol photons m−2 s−1
high light (HL, 70 µmol photons m−2 s−1); whereas for com-
parison, A. tepida, a foraminifer not known to sequester
chloroplasts was starved but only exposed to the dark con-dition. A short-term experiment was thus carried out (7 days)
Oxygen measurements were repeated at 300 µmol photons
to study the effect of light on healthy specimens rather than
m−2 s−1 and in the dark at the end of the experiment
the effect of starvation. For each condition, 10 specimens
(7 days of incubation) for all different light treatments
were used per replicate and three replicates per light treat-
(D, LL, HL) using 10 specimens, to assess their produc-
ment; furthermore all plastic Petri dishes were filled with
tion or consumption of oxygen at these two light levels
Bourgneuf bay filtered-autoclaved seawater. This experiment
(300 µmol photons m−2 s−1 and in the dark) in all treatments.
was carried out in a thermo-regulated culture room at 18 ◦C,
For all conditions (D, LL, HL and Dark-RLC) Fv/Fm was
equipped with cool light fluorescent lamp (Lumix day light,
measured daily at early afternoon, after a 1-hour dark adap-
L30W/865, Osram) and using a 14:10 h (Light : Dark) pho-
tation period and measurements were done in triplicate for
toperiod. The distances between the light and the experimen-
each Petri dish.
tal conditions were assessed using a light-metre and a quan-
Rapid light curves were also carried out in all light treat-
tum sensor (ULM-500 and MQS-B of Walz) to obtain the
ments at the beginning and end of the experiment, after 1-
desirable light intensities. Concerning the dark condition, the
hour dark adaptation for the two tested species. Additionally,
Petri dishes were placed in a box covered with aluminium
RLC were carried out daily in an extra triplicate kept in the
dark (Dark-RLC) throughout the duration of the experiment.
Haynesina germanica kleptoplast fluorescence was mea-
sured using epifluorescence microscopy, as explained above,
before and after the different light treatments. At the begin-
Data are expressed as mean ± standard deviation (SD) when
ning of the experiment it was done on 30 independent speci-
n = 3 or standard error (SE) when n = 30. Statistical anal-
mens to assess the natural and initial variation of Haynesina
yses consisted of a t test to compare the foraminifera test
germanica kleptoplast fluorescence. At the end of the exper-
mean maximal elongation, a non parametric test (Kruskal
iment, the measurements were done on all foraminifera ex-
Wallis) to compare the mean chlorophyll fluorescence of
posed to the different light conditions (a total of 30 speci-
the foraminifera exposed to the different experimental con-
mens per condition). This was also measured on A. tepida,
ditions and a multifactor (experimental conditions (D, LL,
but results are not presented because no chlorophyll fluores-
HL), irradiance (0–300 µmol photons m−2 s−1)) analysis of
cence was observed at the end of the experiment.
variance (ANOVA) with a Fisher's LSD test to compare the
Haynesina germanica and A. tepida oxygen production
respiration rates at the end of the experiment. Differences
and consumption were measured at the beginning of the ex-
were considered significant at p < 0.05. Statistical analyses
periment on three independent replicates with seven spec-
were carried out using the Statgraphics Centurion XV.I (Stat-
imens in each replicate. Six different light steps were
Point Technologies, Inc.) software.
used to measure O2 production (0, 25, 50, 100, 200 and300 µmol photons m−2 s−1) for H. germanica and only twolight steps (0 and 300 µmol photons m−2 s−1) for A. tep-ida. Photosynthetic activity (P ) data of H. germanica were
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
Figure 1. Spectral reflectance signatures of Haynesina germanica,
Ammonia tepida and of a benthic diatom in relative units (x axis
legend: Wavelength (nm)).
Figure 2. Illustration of Haynesina germanica chloroplast content
at the beginning (a) and at the end of the experiment for the three ex-
perimental conditions, Dark (b), Low Light (c) and High Light (d).
Size and biovolume
Higher colour scale values correspond to foraminifera emittingmore fluorescence and likely containing more chlorophyll a; flu-
Ammonia tepida specimens were larger than H. german-
orescence in pixel values between 0 and 255, (scale bar = 50 µm).
ica with a mean maximal elongation of 390 ± 42 µm(SD, n = 34) and 366 ± 45 µm (SD, n = 122), respectively(p < 0.01, F121,33 = 1.15). This resulted in cytoplasmic bio-
lis) showing that the differences in chlorophyll a fluores-
volumes equal to 1.20 × 107 ± 3.9 × 106 µm3 (SD) and
cence were significant (p < 0.01, Df = 3, Fig. 3). It is also
1.01 × 107 ± 3.65 × 106 µm3 (SD), respectively.
noteworthy to mention that there was a large individual vari-ability within each treatment leading to large standard errors
in spite of the number of replicates (n = 30).
Fresh Haynesina germanica and A. tepida showed very dif-
ferent spectral reflectance signatures (Fig. 1). Haynesina ger-
between the two species. Ammonia tepida did not
manica showed a typical diatom spectral signature with high
show any net oxygen production although respiration
reflectance in the infrared region (> 740 nm) and clear ab-
rates measured at 300 µmol photons m−2 s−1 were lower
sorption features around 585, 630 and 675 nm; the absorption
(2485 ± 245 pmol O2 cell−1 d−1) than the ones measured
feature around 675 nm corresponds to the presence of chloro-
in the dark (3531 ± 128 pmol O2 cell−1 d−1) (F2,2 = 3.7,
phyll a; the 585 nm feature is the result of fucoxanthin and
p = 0.02). Haynesina germanica showed lower dark res-
the 630 nm absorption feature is the result of chlorophyll c
piration rates (1654 ± 785 pmol O2 cell−1 d−1) and oxygen
(arrows, Fig. 1). Ammonia tepida showed no obvious pig-
production quickly increased with irradiance, showing
ment absorption features apart from 430 nm (Fig. 1).
no evidence of photoinhibition within the light range
Epifluorescence images showed a clear effect of the dif-
used (Fig. 4). Compensation irradiance (Ic) was reached
ferent light treatments (Dark, Low Light, Hight Light) on H.
very quickly, as low as 24 µmol photons m−2 s−1 (95 %
germanica chlorophyll fluorescence (Fig. 2). Visual observa-
coefficient bound: 17–30 µmol photons m−2 s−1, values cal-
tions showed a clear decrease in chlorophyll fluorescence for
culated from the fitted model Eq. 4) and the half-saturation
the LL and HL treatments from the beginning of the experi-
constant (Ek) was also reached at very low light levels,
ment (Fig. 2a) to the end of a 7-day period of light exposure
i.e. at 17 µmol photons m−2 s−1. No photoinhibition was
(Fig. 2c and d, respectively). Samples kept in the dark did not
observed under the experimental light conditions (0 to
show an obvious decrease but showed a more patchy distribu-
300 µmol photons m−2 s−1), which resulted in an estimation
tion compared to the beginning of the experiment (Fig. 2b).
of ∼ 2800 pmol O2 cell−1 d−1 for maximum photosyn-
This was confirmed by a non-parametric test (Kruskal Wal-
thetic capacity. The P -I curve initial slope at limiting
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
Table 1. Light and dark respiration rates (pmol O2 cell−1 d−1)
± SD of Haynesina germanica in the three experimental conditions
(Dark, Low Light and High Light) at the end of the experiment (Df,
degree of freedom, PFD photon flux density).
Respiration rate (pmol O2 cell−1 d−1)
Figure 3. Mean chlorophyll a fluorescence (±SE, n = 30) at the end
ent between conditions (p < 0.001), with significantly lower
for the three experimental conditions (Dark, Low Light and High
respiration rates of specimens incubated under High Light
Light) and the beginning (T0) of the experiment using Haynesina
conditions than those under Dark and Low Light conditions
germanica. Higher mean values likely corresponded to foraminiferacontaining more chlorophyll.
(p < 0.05, Fisher's LSD test).
PAM fluorescence rapid light curve (RLC) parameters (α,
rETRmax, Ek and Eopt) showed significant differences be-tween foraminiferal species and over the duration of the ex-periment (Figs. 5 and 6). Highest rETRmax, α and Eopt werealways observed in H. germanica. After only one starvationday A. tepida RLC parameters dropped to zero or close tozero. In contrast, H. germanica RLC parameters showed aslow decrease throughout the experiment (Figs. 5 and 6) withrETRmax and α decreasing from 6 to 4 and 0.22 to 0.15,respectively (Figs. 6a and b). The parameters Ek and Eoptstayed constant over the 7 days of the experiment, with val-ues oscillating around 30 and 90, respectively (Fig. 6c andd).
PSII maximum quantum yields (Fv/Fm) were clearly af-
fected by light and time (Fig. 7). Both species showed highinitial Fv/Fm values, i.e. > 0.6 and 0.4 for H. germanica andA. tepida, respectively (Fig. 7). However, while A. tepida
Fv/Fm values quickly decreased to zero after only one starva-
(pmol O2 cell−1 d−1) as a function of the photon flux density (PFD,
tion day, H. germanica exhibited a large variability between
µmol photons m−2 s−1). The half-saturation constant, Ek, was
light conditions (D, LL, HL) throughout the duration of the
found at 17 (13–21), the dark respiration, Rd, at 1654 (1522–1786)
experiment (Fig. 7); decreasing from 0.65 to 0.55 in darkness
pmol O2 cell−1 d−1 and the maximum photosynthetic capacity,
(D), from 0.65 to 0.35 under low light (LL) conditions and
Pm, at 2845 (2672–3019) pmol O2 cell−1 d−1. The Ic, calculated
from 0.65 to 0.20 under high light (HL). Using these Fv/Fm
compensation irradiance (24 (17–30) µmol photons m−2 s−1). Theadjusted R2 of the model was equal to 0.998, n = 3.
decreases, H. germanica kleptoplast functional times wereestimated between 11 and 21 days in the dark (D), 9–12 daysin low light (LL) and 7–8 days in high light (HL), depending
irradiance (α) was estimated at 70 pmol O
on whether or not an exponential or linear model was applied.
(µmol photons m−2 s−1)−1 (95 % coefficient bound: 58–88).
Ammonia tepida chloroplast functional times were estimated
Oxygen measurements carried out at the end of the exper-
between 1 and 2 days (exponential and linear model, respec-
iment (T7) showed significant different dark and light res-
tively) and light exposure reduced the functional time to less
piration rates, with light respiration being lower than dark
than 1 day (data not shown).
respiration but not reaching net oxygen production rates (D,LL, HL) (Table 1). Moreover, respiration rates were differ-
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
ida was found to carry out aerobic respiration, but respirationrates measured at 300 µmol photons m−2 s−1 were lower thanthose measured in the dark. We thus suppose that in A. tepidaoxygen production by ingested diatom or chloroplasts mightbe possible, provided that this species is constantly suppliedwith fresh diatoms. However, another possibility to explainthis reduction in oxygen consumption could be a decrease ofits metabolism or activity under light exposure. The light anddark oxygen production or consumption values measured forboth species are in accordance with previous studies (Geslinet al., 2011).
According to Lopez (1979), measured oxygen data can be
used to estimate H. germanica carbon fixation rates. Thus,using 1000 pmol O2 cell−1 d−1 at 300 µmol photons m−2 s−1,∼ 200 to 4000 cells per 50 cm3 in the top 0.5 cm (Morvanet al., 2006; Bouchet et al., 2007) and assuming that photo-synthesis produced one mol O2 per mol of C fixed, H. ger-
Figure 5. Rapid light curves (RLC, n = 3) expressed as the relative
manica primary production would be between 1.8 × 10−5
electron transport rate (rETR) as a function of the photosynthetic
and 4.0 × 10−4 mol C m−2 d−1. This is a very low value
active radiation (PAR in µmol photons m−2 s−1) of Haynesina ger-
compared to microphytobenthos primary production in At-
manica (black lines) and Ammonia tepida (black dashed lines) dur-
lantic mudflat ecosystems, which usually range from 1.5 to
ing the 7 days of the experiment.
5.9 mol C m−2 d−1 (e.g. Brotas and Catarino, 1995, reviewedin MacIntyre et al., 1996). The estimated values representthus less than 0.1 % of microphytobenthos fixated carbon and
are in the same range of values than what has been describedby Lopez (1979) using 14C radioactive tracers. These results
should be interpreted with caution because a wide variety offactors probably affect H. germanica in situ primary produc-
Our results clearly show that only H. germanica was capable
tion, e.g. diatom availability, kleptoplast densities, nutrient
of carrying out net photosynthesis. Haynesina germanica had
supply, light exposure, sea water turbidity, local biogeochem-
typical diatom reflectance spectra (Fig. 1), showing the three
ical processes and migration capability are all factors that
major diatom pigment absorption features: chlorophyll a,
can potentially affect H. germanica kleptoplast functionality.
chlorophyll c, and fucoxanthin (Meleder et al., 2003, 2013;
Nevertheless, although carbon fixation seems not to be rele-
Jesus et al., 2008; Kazemipour et al., 2012). Conversely, in
vant at a global scale, the oxygen production could be impor-
A. tepida these absorption features were not detected, sug-
tant at a microscale and relevant in local mineralization pro-
gesting that diatom pigments ingested by this species were
cesses in/on mudflat sediments (e.g. iron, ammonium, man-
quickly digested and degraded to a degree where they were
no longer detected by spectral reflectance measurements.
At sampling time (T0) H. germanica rETR and Fv/Fm
These non-destructive reflectance measurements are thus in
values were similar to microphytobenthic species (i.e.
accordance with other studies on benthic foraminifera pig-
Fv/Fm > 0.65) (Perkins et al., 2001), suggesting that the klep-
ments by HPLC showing that H. germanica feed on benthic
toplast PSII and electron transport chain were not much af-
diatoms (Knight and Mantoura, 1985). Similarly, Knight and
fected after incorporation in the foraminifers' cytoplasm. In
Mantoura (1985) also detected higher concentrations and less
contrast, A. tepida Fv/Fm and RLC parameters were already
degraded diatom pigments in H. germanica than in A. tepida.
much lower on the sampling day and quickly decreased to
Furthermore, H. germanica has the ability to pro-
almost zero within 24 h, suggesting that plastids were not
duce oxygen from low to relatively high irradiance,
stable inside the A. tepida cytoplasm. Complete diatoms in-
as shown by the low compensation point (Ic) of
side A. tepida were already observed in feeding studies (Le
24 µmol photons m−2 s−1 and the high onset of light sat-
Kieffre, pers. com), this low Fv/Fm value might thus come
uration (> 300 µmol photons m−2 s−1) (Fig. 4). Thus, H.
from recently ingested diatoms by A. tepida. Fv/Fm has pre-
germanica seems to be well adapted to cope with
viously been used to determine kleptoplast functional times
the high light variability observed in intertidal sedi-
and to follow decrease in kleptoplast efficiency in other klep-
ments that can range from very high irradiance levels
toplastic organisms, e.g. the sea slug Elysia viridis (Vieira
(> 1000 µmol photons m−2 s−1) at the surface of the sediment
et al., 2009). Fv/Fm measurements carried out on H. ger-
during low tide to very low levels within the sediment matrix
manica at different light conditions showed that light had a
or during high tide in turbid mudflat waters. Ammonia tep-
significant effect on the estimation of kleptoplast functional
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
Figure 6. Rapid light curve (RLC, n = 3) parameters for Haynesina germanica (Dark-RLC) and Ammonia tepida maintained in the dark
during the experiment, Alpha is the initial slope of the RLC at limiting irradiance, rETRmax is the maximum relative electron transport rate,
Ek is the light saturation coefficient and Eopt is the optimum light, all of them were estimated by adjusting the experimental data to fit the
model of Platt et al. (1980).
time, with the longest functional time estimated at 21 days for
was amplified in low and high irradiance and it should
dark conditions. This time frame would qualify H. german-
be pointed out that the actual light level of the HL treat-
ica as a long-term kleptoplast retention species (Clark et al.,
ment (i.e. 70 µmol photons m−2 s−1) is very low compared
1990); however, our 7 days estimation for the high light treat-
to irradiances in their natural environment, which are easily
ment would place H. germanica in the medium-term reten-
going above 1000 µmol photons m−2 s−1, showing that the
tion group. This clearly shows that light exposure has an im-
foraminifera kleptoplasts lack the high photoregulation ca-
portant effect on this species kleptoplast functionality. Con-
pacity exhibited by the benthic diatoms that they feed upon
cerning A. tepida, the short dark diatom or chloroplast func-
(Cartaxana et al., 2013). This is consistent with the observa-
tional time (< 2 days) places this species directly in the short
tion at the end of the experiment that no net oxygen produc-
or medium-term retention group.
tion was occurring under the different light conditions. Nev-
Additionally, H. germanica kept in darkness showed a
ertheless, a small difference was still found between dark and
slow decrease of the RLC parameters, α and rETRmax,
light respiration (Table 1), suggesting that some oxygen pro-
throughout the 7 experimental days; this decrease is likely
duction was still occurring but it was not sufficient to com-
related to overall degradation of the light-harvesting com-
pensate for the respiration oxygen consumption. We also no-
plexes and of other components of the photosynthetic ap-
ticed that the respiration was higher in the foraminifera main-
paratus, which gradually induced a reduction of light har-
tained in low light and dark conditions in comparison to the
vesting efficiency and of carbon metabolism. This decrease
high light foraminifera. In the line of the lower Fv/Fm values
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
This fundamental difference could explain why kleptoplastfunctional times are much longer in N. stella, reaching up to1 year in specimens kept in darkness (Grzymski et al., 2002).
On the other hand, it has been shown that isolated chloro-plasts are able to function for several months in Sacoglossansea slugs provided with air and light in aquaria (Green etal., 2001; Rumpho et al., 2001), which demonstrates the ex-istence of interactions between the kleptoplast and the hostgenomes, and/or of mechanisms facilitating and supportingsuch long-lasting associations. In H. germanica exposed tohigh light it is also possible that reactive oxygen species(ROS) production rates of the sequestered chloroplasts mightexceed the foraminifera capacity to eliminate those ROS,thus inducing permanent damage to the foraminifera. ThisROS production could also eventually damage the klepto-plasts resulting in higher kleptoplast degradation rates.
Figure 7. Maximum quantum efficiency of the photosystem II
Possible advantages of kleptoplasty for intertidal
(Fv/Fm, n = 3) during the experiment for the different applied con-
ditions (Dark, Low Light and High Light) and species (Haynesinagermanica and Ammonia tepida).
Much is still unknown about the relationship between klep-toplastic benthic foraminifera and their sequestered chloro-
observed, this suggests that kleptoplasts and possibly other
plasts. The relevance of the photosynthetic metabolism com-
metabolic pathways might have been damaged by the excess
pared to predation or organic matter assimilation is unknown;
light. Clearly, in H. germanica light exposure had a strong
however, it would be of great interest to understand the klep-
effect on PSII maximum quantum efficiency and on the re-
toplast role in the foraminiferal total energy budget. Oxy-
tention of functional kleptoplasts (Fig. 7), which can explain
genic photosynthesis comprises multiple reactions leading
the absence of net oxygen production after the 7 days of the
to the transformation of inorganic carbon to carbohydrates.
experiments. Comparable results for H. germanica were also
However, to produce these carbohydrates all the light-driven
obtained by counting the number of chloroplasts over time
reactions have to be carried out, as well as the Calvin cy-
with cells exposed or not to light (Lopez, 1979). One of the
cle reactions. With fresh kleptoplasts this hypothesis seems
most probable explanations for the observed Fv/Fm decrease
possible (e.g. Lopez, 1979), especially if the plastid proteins
is the gradual inactivation of the protein D1 in PSII reaction
are still present and functional. However, we showed that the
centres. This protein is an essential component in the electron
maximum quantum efficiency of the PSII decreased quickly
transport chain and its turnover rate is frequently the limiting
under light exposure, suggesting that substantial direct carbo-
factor in PSII repair rates (reviewed in Campbell and Tyys-
hydrate production is unlikely without constant chloroplast
tjärvi, 2012). Normally, protein D1 is encoded in the chloro-
replacement. Conversely, the production of intermediate pho-
plast and is rapidly degraded and resynthesized under light
tosynthetate products such as adenosine triphosphate (ATP)
exposure with a turnover correlated to irradiance (Tyystjärvi
and nicotinamide adenine dinucleotide phosphate (NADPH)
and Aro, 1996). However, although D1 is encoded by the
could be possible and would be of metabolic value for the
chloroplast genome, its synthesis and concomitant PSII re-
foraminifera. It is also possible that in situ the foraminifera
covery require further proteins that are encoded by the algal
have better photoregulation capacities. Not only will they
nuclear genome (Yamaguchi et al., 2005). Thus, when D1
have easy access to fresh diatom chloroplasts, as H. german-
turnover is impaired it will induce an Fv/Fm decrease corre-
ica is mainly living in the first few millimetres of the super-
lated to irradiance (Tyystjärvi and Aro, 1996) consistent to
ficial sediment (Alve and Murray, 2001; Thibault de Chan-
what was observed in the present study. In another deep sea
valon et al., 2015), but they will also have the possibility of
benthic species (Nonionella stella) the D1 and other plastid
migrating within the sediment (Gross, 2000) using this be-
proteins (RuBisCO and FCP complex) were still present in
havioural feature to enhance their photoregulation capacity,
the foraminifer 1 year after sampling (Grzymski et al., 2002).
similar to what is observed in benthic diatoms from micro-
This shows that some foraminifera can retain both nuclear
phytobenthic biofilms (e.g. Jesus et al., 2006; Mouget et al.,
(FCP) and chloroplast (D1 and RuBisCO) encoded proteins.
2008; Perkins et al., 2010). However, below the photic limit
However, contrary to H. germanica, N. stella lives in deeper
(max 2 to 3 mm in estuarine sediments reviewed in MacIn-
environments never exposed to light and thus is unlikely to
tyre et al., 1996; Cartaxana et al., 2011) it is unlikely that
carry out oxygenic photosynthesis (Grzymski et al., 2002).
oxygenic photosynthesis will occur, even if live H. german-
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
ica are also found below this limit (Thibault de Chanvalon et
distribution of living benthic foraminifera: First insight from ax-
al., 2015; Cesbron et al., 2016).
ial tomodensitometry, J. Exp. Mar. Biol. Ecol., 371, 20–33, 2009.
Brotas, V. and Catarino, F.: Microphytobenthos primary production
of Tagus estuary intertidal flats (Portugal), Neth. J. Aquat. Ecol.,
29, 333–339, 1995.
Cartaxana, P., Ruivo, M., Hubas, C., Davidson, I., Serôdio, J., and
Comparing H. germanica with A. tepida showed that the for-
Jesus, B.: Physiological versus behavioral photoprotection in in-
mer species potentially has the capacity of retaining func-
tertidal epipelic and epipsammic benthic diatom communities, J.
tional kleptoplasts up to 21 days, much longer than A. tep-
Exp. Mar. Biol. Ecol., 405, 120–127, 2011.
ida that showed almost no PSII activity after 24 h. Neverthe-
Cartaxana, P., Domingues, N., Cruz, S., Jesus, B., Laviale, M., Serô-
dio, J., and Marques da Silva, J.: Photoinhibition in benthic di-
less, the capacity of H. germanica to keep functional klep-
atom assemblages under light stress, Aquat. Microb. Ecol., 70,
toplasts was significantly decreased by exposing it even to
87–92, 2013.
low irradiance levels, which resulted in low Fv/Fm values
Campbell, D. A. and Tyystjarvi, E.: Parameterization of photosys-
and decreased oxygen production. This shows clearly that in
tem II photoinactivation and repair, BBA-Bioenergetics, 1817,
our experimental conditions, H. germanica had reduced pho-
258–265, 2012.
toregulation capacities. These results emphasize that studies
Cesbron, F., Geslin, E., Jorissen, F. J., Delgard, M. L., Charrieau, L.,
on kleptoplast photophysiology of benthic foraminifera must
Deflandre, B., Jézéquel, D., Anschutz, P., and Metzger, E.: Ver-
be interpreted with care, as results are strongly influenced
tical distribution and respiration rates of benthic foraminifera:
by the foraminiferal light history before incubation. Addi-
Contribution to aerobic remineralization in intertidal mudflats
tionally, this study shows that the cellular machinery neces-
covered by Zostera noltei meadows, Estuar. Coast. Shelf S., in
sary for chloroplast maintenance is unlikely to be completely
press, 2016.
Clark, K. B., Jensen, K. R., and Stirts, H. M.: Survey for functional
functional, suggesting that H. germanica has to continuously
kleptoplasty among West Atlantic Ascoglossa (=Sacoglossa)
renew its chloroplasts to keep them functional. We hypothe-
(Mollusca: Opisthobranchia), Veliger, 33, 339–345, 1990.
size that kleptoplasts might have an added value by providing
Correia, M. J. and Lee, J. J.: Chloroplast retention by Elphidium
extra carbon, mainly under light exposure, but also as energy
excavatum (Terquem). Is it a selective process?, Symbiosis, 29,
stock to be digested during food impoverished periods, in
343–355, 2000.
dark or light conditions.
Correia, M. J. and Lee, J. J.: Fine structure of the plastids retained
by the foraminifer Elphidium excavatum (Terquem), Symbiosis,32, 15–26, 2002a.
Acknowledgements. This study is part of the EC2CO project
Correia, M. J. and Lee, J. J.: How long do the plastids retained by
"ForChlo" supported by the CNRS. This study is strongly sup-
Elphidium excavatum (Terquem) last in their host?, Symbiosis,
ported by the Region Pays de la Loire (Post-doc position of the first
32, 27–37, 2002b.
author and "COSELMAR" and "Fresco" projects).
Costa, J., Gimenez-Casalduero, F., Melo, R., and Jesus, B.: Colour
morphotypes of Elysia timida (Sacoglossa, Gastropoda) are de-
Edited by: J. Middelburg
termined by light acclimation in food algae, Aquat. Biol., 17,81–89, 2012.
Curtis, N. E., Middlebrooks, M. L., Schwartz, J. A., and Pierce, S.
K.: PAM analysis of 3 sacoglossan species reveals differences in
photosynthetic function and chloroplast longevity, Integr. Comp.
Biol., 53, 272–272, 2013.
Alve, E. and Murray, J. W.: Temporal variability in vertical distribu-
Debenay, J.-P., Guillou, J.-J., Redois, F., and Geslin, E.: Distribu-
tions of live (stained) intertidal foraminifera, southern England,
tion trends of foraminiferal assemblages in paralic environments,
J. Foramin. Res., 31, 12–24, 2001.
in: Environmental Micropaleontology, edited by: Martin, R. E.,
Austin, H. A., Austin, W. E., and Paterson, D. M.: Extracellular
Springer US, New York, 39–67, 2000.
cracking and content removal of the benthic diatom Pleurosigma
Debenay, J. P., Bicchi, E., Goubert, E., and du Chatelet, E. A.:
angulatum (Quekett) by the benthic foraminifera Haynesina ger-
Spatio-temporal distribution of benthic foraminifera in relation
manica (Ehrenberg), Mar. Micropaleontol., 57, 68–73, 2005.
to estuarine dynamics (Vie estuary, Vendee, W France), Estuar.
Bernhard, J. M. and Bowser, S. S.: Benthic foraminifera of dysoxic
Coast. Shelf S., 67, 181–197, 2006.
sediments: chloroplast sequestration and functional morphology,
Eberhard, S., Finazzi, G., and Wollman, F.-A.: The dynamics of
Earth-Sci. Rev., 46, 149–165, 1999.
photosynthesis, Annu. Rev. Genet., 42, 463–515, 2008.
Bouchet, V. M. P., Debenay, J.-P., Sauriau, P.-G., Radford-Knoery,
Evertsen, J., Burghardt, I., Johnsen, G., and Wagele, H.: Retention
J., and Soletchnik, P.: Effects of short-term environmental distur-
of functional chloroplasts in some sacoglossans from the Indo-
bances on living benthic foraminifera during the Pacific oyster
Pacific and Mediterranean, Mar. Biol., 151, 2159–2166, 2007.
summer mortality in the Marennes-Oleron Bay (France), Mar.
Falkowski, P. G. and Raven, J. A.: Aquatic photosynthesis, second
Environ. Res., 64, 358–383, 2007.
Edn., Princeton Universty Press, Princeton, 2007.
Bouchet, V. M. P., Sauriau, P.-G., Debenay, J.-P., Mermillod-
Geslin, E., Risgaard-Petersen, N., Lombard, F., Metzger, E., Lan-
Blondin, F., Schmidt, S., Amiard, J.-C., and Dupas, B.: Influence
glet, D., and Jorissen, F.: Oxygen respiration rates of benthic
of the mode of macrofauna-mediated bioturbation on the vertical
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
foraminifera as measured with oxygen microsensors, J. Exp.
Knight, R. and Mantoura, R. F. C.: Chlorophyll and carotenoid pig-
Mar. Biol. Ecol., 396, 108–114, 2011.
ments in foraminifera and their symbiotic algae: analysis by high
Goldstein, S. T., Habura, A., Richardson, E. A., and Bowser, S. S.:
performance liquid chromatography, Mar. Ecol.-Prog. Ser., 23,
Xiphophaga minuta, and X. allominuta, nov. gen., nov. spp., new
241–249, 1985.
monothalamid Foraminifera from coastal Georgia (USA): cryp-
Lee, J. J., Lanners, E., and Ter Kuile, B.: The retention of chloro-
tic species, gametogenesis, and an unusual form of chloroplast
plasts by the foraminifera Elphidium crispum, Symbiosis, 5, 45–
sequestration, J. Foramin. Res., 40, 3–15, 2010.
Goldstein, S. T., Bernhard, J. M., and Richardson, E. A. Chloroplast
Li, Y. H. and Gregory, S.: Diffusion of ions in sea-water and deep-
sequestration in the foraminifer Haynesina germanica: Applica-
sea sediments, Geochim. Cosmochim. Ac., 38, 703–714, 1974.
tion of high pressure freezing and freeze substitution, Microsc.
Lopez, E.: Algal chloroplasts in the protoplasm of three species
Microanal., 10, 1458–1459, 2004.
of benthic foraminifera: taxonomic affinity, viability and persis-
Gooday, A. J.: Meiofaunal foraminiferans from the bathyal Porcu-
tence, Mar. Biol., 53, 201–211, 1979.
pine Seabight (northeast Atlantic): size structure, standing stock,
MacIntyre, H. L., Geider, R. J., and Miller, D. C.: Microphytoben-
taxonomy composition, species diversity and vertical distribution
thos: The ecological role of the "secret garden" of unvegetated,
in the sediment, Deep-Sea Res. Pt. I, 33, 1345–1373, 1986.
shallow-water marine habitats .1. Distribution, abundance and
Green, B. J., Li, W.-Y., Manhart, J. R., Fox, T. C., Summer, E. J.,
primary production, Estuaries, 19, 186–201, 1996.
Kennedy, R. A., Pierce, S. K., and Rumpho, M. E.: Mollusc-
Marchetti, J., Bougaran, G., Jauffrais, T., Lefebvre, S., Rouxel, C.,
algal chloroplast endosymbiosis. Photosynthesis, thylakoid pro-
Saint-Jean, B., Lukomska, E., Robert, R., and Cadoret, J. P.: Ef-
tein maintenance, and chloroplast gene expression continue for
fects of blue light on the biochemical composition and photo-
many months in the absence of the algal nucleus, Plant Physiol.,
synthetic activity of Isochrysis sp. (T-iso), J. Appl. Phycol., 25,
124, 331–342, 2001.
109–119, 2013.
Gross, O.: Influence of temperature, oxygen and food availability on
Meleder, V., Barille, L., Launeau, P., Carrere, V., and Rince, Y.:
the migrational activity of bathyal benthic foraminifera: evidence
Spectrometric constraint in analysis of benthic diatom biomass
by microcosm experiments, Hydrobiologia, 426, 123–137, 2000.
using monospecific cultures, Remote Sens. Environ., 88, 386–
Grzymski, J., Schofield, O. M., Falkowski, P. G., and Bernhard, J.
M.: The function of plastids in the deep-sea benthic foraminifer,
Meleder, V., Laviale, M., Jesus, B., Mouget, J. L., Lavaud, J.,
Nonionella stella, Limnol. Oceanogr., 47, 1569–1580, 2002.
Kazemipour, F., Launeau, P., and Barille, L.: In vivo estima-
Hannah, F., Rogerson, A., and Laybournparry, J.: Respiration rates
tion of pigment composition and optical absorption cross-section
and biovolumes of common benthic foraminifera (Protozoa), J.
by spectroradiometry in four aquatic photosynthetic micro-
Mar. Biol. Assoc. UK, 74, 301–312, 1994.
organisms, J. Photoch. Photobio. B, 129, 115–124, 2013.
Hayward, B. W., Holzmann, M., Grenfell, H. R., Pawlowski, J., and
Moodley, L., Middelburg, J. J., Boschker, H. T. S., Duineveld, G.
Triggs, C. M.: Morphological distinction of molecular types in
C. A., Pel, R., Herman, P. M. J., and Heip, C. H. R.: Bacteria
Ammonia – towards a taxonomic revision of the world's most
and Foraminifera: key players in a short-term deep-sea benthic
commonly misidentified foraminifera, Mar. Micropaleontol., 50,
response to phytodetritus, Mar. Ecol.-Prog. Ser., 236:, 23–29,
237–271, 2004.
Høgslund, S., Revsbech, N. P., Cedhagen, T., Nielsen, L. P., and
Morvan, J., Debenay, J.-P., Jorissen, F., Redois, F., Beneteau, E.,
Gallardo, V. A.: Denitrification, nitrate turnover, and aerobic res-
Delplancke, M., and Amato, A.-S. Patchiness and life cycle of in-
piration by benthic foraminiferans in the oxygen minimum zone
tertidal foraminifera: Implication for environmental and paleoen-
off Chile, J. Exp. Mar. Biol. Ecol., 359, 85–91, 2008.
vironmental interpretation, Mar. Micropaleontol., 61, 131–154,
Jesus, B., Perkins, R. G., Consalvey, M., Brotas, V., and Paterson, D.
M.: Effects of vertical migrations by benthic microalgae on flu-
Mouget, J.-L., Perkins, R. G., Consalvey, M., and Lefebvre, S.: Mi-
orescence measurements of photophysiology, Mar. Ecol.-Prog.
gration or photoacclimation to prevent photoinhibition and UV-B
Ser., 315, 55–66, 2006.
damage in marine microphytobenthic communities, Aquat. Mi-
Jesus, B., Mouget, J.-L., and Perkins, R. G.: Detection of di-
crob. Ecol., 52, 223–232, 2008.
atom xanthophyll cycle using spectral reflectance, J. Phycol., 44,
Papacek, S., Celikovsky, S., Rehak, B., and Stys, D.: Experimen-
1349–1359, 2008.
tal design for parameter estimation of two time-scale model of
Jesus, B., Brotas, V., Ribeiro, L., Mendes, C. R., Cartaxana, P., and
photosynthesis and photoinhibition in microalgae, Math. Com-
Paterson, D. M.: Adaptations of microphytobenthos assemblages
put. Simulat., 80, 1302–1309, 2010.
to sediment type and tidal position, Cont. Shelf Res., 29, 1624–
Pascal, P.-Y., Dupuy, C., Richard, P., Mallet, C., du Chatelet, E. A.,
and Niquil, N.: Seasonal variation in consumption of benthic bac-
Jesus, B., Ventura, P., and Calado, G.: Behaviour and a functional
teria by meio- and macrofauna in an intertidal mudflat, Limnol.
xanthophyll cycle enhance photo-regulation mechanisms in the
Oceanogr., 54, 1048–1059, 2009.
solar-powered sea slug Elysia timida (Risso, 1818), J. Exp. Mar.
Perkins, R. G., Underwood, G. J. C., Brotas, V., Snow, G. C., Jesus,
Biol. Ecol., 395, 98–105, 2010.
B., and Ribeiro, L.: Responses of microphytobenthos to light:
Kazemipour, F., Launeau, P., and Méléder, V.: Microphytobenthos
primary production and carbohydrate allocation over an emer-
biomass mapping using the optical model of diatom biofilms:
sion period, Mar. Ecol.-Prog. Ser., 223, 101–112, 2001.
Application to hyperspectral images of Bourgneuf Bay, Remote
Perkins, R. G., Mouget, J.-L., Lefebvre, S., and Lavaud, J.: Light re-
Sens. Environ., 127, 1–13, 2012.
sponse curve methodology and possible implications in the appli-
Biogeosciences, 13, 2016
T. Jauffrais et al.: Effect of light on photosynthetic efficiency of sequestered chloroplasts
cation of chlorophyll fluorescence to benthic diatoms, Mar. Biol.,
Serodio, J., Pereira, S., Furtado, J., Silva, R., Coelho, H., and Cal-
149, 703–712, 2006.
ado, R.: In vivo quantification of kleptoplastic chlorophyll a con-
Perkins, R. G., Lavaud, J., Serodio, J., Mouget, J. L., Cartaxana, P.,
tent in the "solar-powered" sea slug Elysia viridis using opti-
Rosa, P., Barille, L., Brotas, V., and Jesus, B. M.: Vertical cell
cal methods: spectral reflectance analysis and PAM fluorometry,
movement is a primary response of intertidal benthic biofilms to
Photochem. Photobio. S., 9, 68–77, 2010.
increasing light dose, Mar. Ecol.-Prog. Ser., 416, 93–103, 2010.
Thibault de Chanvalon, A., Metzger, E., Mouret, A., Cesbron, F.,
Knoery, J., Rozuel, E., Launeau, P., Nardelli, M. P., Jorissen,
foraminiferan Elphidium margaritaceum questions the role
F. J., and Geslin, E.: Two-dimensional distribution of living
of gene transfer in kleptoplastidy, Mol. Biol. Evol., 30, 66–69,
benthic foraminifera in anoxic sediment layers of an estuarine
mudflat (Loire estuary, France), Biogeosciences, 12, 6219–6234,
Pillet, L., de Vargas, C., and Pawlowski, J.: Molecular identifi-
cation of sequestered diatom chloroplasts and kleptoplastidy in
Trench, R. K., Trench, M. E., and Muscatin, L.: Symbiotic chloro-
foraminifera, Protist, 162, 394–404, 2011.
plasts; their photosynthetic products and contribution to mucus
Pina-Ochoa, E., Hogslund, S., Geslin, E., Cedhagen, T., Revsbech,
synthesis in two marine slugs, Biol. Bull., 142, 335–349, 1972.
N. P., Nielsen, L. P., Schweizer, M., Jorissen, F., Rysgaard,
Tsuchiya, M., Toyofuku, T., Uematsu, K., Brüchert, V., Collen, J.,
S., and Risgaard-Petersen, N.: Widespread occurrence of nitrate
Yamamoto, H., and Kitazato, H.: Cytologic and genetic charac-
storage and denitrification among foraminifera and gromiida, P.
teristics of endobiotic bacteria and kleptoplasts of Virgulinella
Natl. Acad. Sci. USA, 107, 1148–1153, 2010.
fragilis (Foraminifera), J. Eukaryot. Microbiol., 62, 454–469,
Platt, T., Gallegos, C. L., and Harrison, W. G.: Photoinhibition of
photosynthesis in natural assemblages of marine phytoplankton,
Tyystjärvi, E. and Aro, E. M.: The rate constant of photoinhibition,
J. Mar. Res., 38, 687–701, 1980.
measured in lincomycin-treated leaves, is directly proportional to
Revsbech, N. P.: An oxygen microsensor with a guard cathode, Lim-
light intensity, P. Natl. Acad. Sci. USA, 93, 2213–2218, 1996.
nol. Oceanogr., 34, 474–478, 1989.
Ventura, P., Calado, G., and Jesus, B.: Photosynthetic efficiency and
Rink, S., Kuhl, M., Bijma, J., and Spero, H. J.: Microsensor studies
kleptoplast pigment diversity in the sea slug Thuridilla hopei
of photosynthesis and respiration in the symbiotic foraminifer
(Verany, 1853), J. Exp. Mar. Biol. Ecol., 441, 105–109, 2013.
Orbulina universa, Mar. Biol., 131, 583–595, 1998.
Vieira, S., Calado, R., Coelho, H., and Serodio, J.: Effects of light
Risgaard-Petersen, N., Langezaal, A. M., Ingvardsen, S., Schmid,
exposure on the retention of kleptoplastic photosynthetic activity
M. C., Jetten, M. S. M., Op den Camp, H. J. M., Derksen, J. W.
in the sacoglossan mollusc Elysia viridis, Mar. Biol., 156, 1007–
M., Pina-Ochoa, E., Eriksson, S. P., Nielsen, L. P., Revsbech, N.
P., Cedhagen, T., and van der Zwaan, G. J.: Evidence for com-
Yamaguchi, K., Mayfield, S., and Sugita, M.: Transcriptional and
plete denitrification in a benthic foraminifer, Nature, 443, 93–96,
Translational Regulation of Photosystem II Gene Expression, in:
Photosystem II, edited by: Wydrzynski, T., Satoh, K., and Free-
Rumpho, M. E., Summer, E. J., Green, B. J., Fox, T. C., and Man-
man, J., Springer, the Netherlands, 649–668, 2005.
hart, J. R.: Mollusc/algal chloroplast symbiosis: how can isolatedchloroplasts continue to function for months in the cytosol of asea slug in the absence of an algal nucleus?, Zoology, 104, 303–312, 2001.
Biogeosciences, 13, 2016
Source: http://www.biogeosciences.net/13/2715/2016/bg-13-2715-2016.pdf
REV ARGENT NEUROC VOL. 28, Nº 3 : 78-98 2014 REVISIÓN DE LA LITERATURA Cirugía de los trastornos del comportamiento: el estado del arte Claudio Yampolsky, Damián Bendersky Servicio de Neurocirugía, Hospital Italiano de Buenos Aires, Ciudad Autónoma de Buenos Aires, Argentina RESUmENIntroducción: la cirugía de los trastornos del comportamiento (CTC) se está convirtiendo en un tratamiento más común desde el desarrollo de la neuromodulación. Podemos dividir su historia en 3 etapas: la primera comienza en los inicios de la psicocirugía y termina con el desarrollo de las técnicas estereotácticas, cuando comienza la segunda etapa. Ésta se caracteriza por la realización de lesiones estereotácticas. Nos encontramos transitando la tercera etapa, que comienza cuando la estimulación cerebral profunda (ECP) empieza a ser usada en CTC.Objetivo: el propósito de este artículo es realizar una revisión no sistemática de la historia, indicaciones actuales, técnicas y blancos quirúrgicos de la CTC. Resultados: a pesar de los errores graves cometidos en el pasado, hoy en día, la CTC está renaciendo. Los trastornos psiquiátricos que más frecuentemente se tratan con cirugía y los blancos estereotácticos preferidos para cada uno de ellos son: cápsula interna/estriado ventral para trastorno obsesivo-compulsivo, cíngulo subgenual para depresión y complejo centromediano/parafascicular del tálamo para síndrome de Tourette. Conclusión: los resultados de la ECP en estos trastornos parecen alentadores. Sin embargo, se necesitan más estudios randomizados para establecer la efectividad de la CTC. Debe tenerse en cuenta que una apropiada selección de pacientes nos ayudará a realizar un procedimiento más seguro así como también a lograr mejores resultados quirúrgicos, conduciendo a la CTC a ser más aceptada por psiquiatras, pacientes y sus familias. Se necesita mayor investigación en varios temas como: fisiopatología de los trastornos del comportamiento, indicaciones de CTC y nuevos blancos quirúrgicos.
Available Online through www.ijpbs.com (or) www.ijpbsonline.com IJPBS Volume 3 Issue 4 OCT-DEC 2013 255-264 Research Article Pharmaceutical Sciences METHOD DEVELOPMENT AND VALIDATION OF RP-HPLC METHOD FOR SIMULTANEOUS ESTIMATION OF DICYCLOMINE HYDROCHLORIDE AND DICLOFENAC POTASSIUM IN TABLET DOSAGE FORMS