Directory UMM :Data Elmu:jurnal:E:Environmental and Experimental Botany:Vol43.Issue1.Feb2000:
Mycosporine-like amino acids in the marine red alga
Gracilaria cornea
— effects of UV and heat
Rajeshwar P. Sinha, Manfred Klisch, Almut Gro¨niger, Donat-P. Ha¨der *
Institut fu¨r Botanik und Pharmazeutische Biologie,Friedrich-Alexander-Uni6ersita¨t,Staudtstr.5,D-91058Erlangen,Germany
Received 29 October 1998; received in revised form 2 September 1999; accepted 2 September 1999
Abstract
Ultraviolet (UV)-absorbing mycosporine-like amino acids (MAAs) were separated from a marine red alga
Gracilaria corneausing HPLC. The isolated MAAs were identified as porphyra-334 and/or shinorine by comparing them with various standards. No in vivo induction of MAAs was detected inG.corneaeven when the organism was grown for 4 – 5 days either in the presence of UV-A and UV-B only or in combination with photosynthetically active radiation. In vitro absorption properties of MAAs were unaffected when irradiated with UV-B or subjected to heat treatment (7592°C) for up to 6 h. In comparison to MAAs, other pigments such as chlorophyll a (436 and 665 nm), carotenoids (475 nm) and phycocyanin (618 nm) were severely affected by UV-B irradiation. The results indicate a highly stable nature of MAAs against the environmental stress factors like UV-B and heat. The SDS-PAGE protein profile ofG. cornea showed a gradual decrease in the intensity of protein bands at 20 kDa (a and b subunits of phycocyanin) but at the same time a gradual increase in the intensity of protein bands at 26 kDa (phycoerythrin), showing the phenomenon of chromatic adaptation (changes in pigmentation in photosynthetic organisms in response to light quality), when the organism was grown in the presence of UV plus PAR. © 2000 Elsevier Science B.V. All rights reserved.
Keywords:Gracilaria; Mycosporine-like amino acids (MAAs); UV irradiation; Heat treatment; Pigmentation; Protein profile www.elsevier.com/locate/envexpbot
1. Introduction
Continued depletion of the stratospheric ozone layer, mainly due to anthropogenically released atmospheric pollutants such as chlorofluorocar-bons (CFCs) is responsible for the increase in
solar ultraviolet-B (UV-B; 280 – 315 nm) radiation reaching the Earth’s surface (Blumthaler and Am-bach, 1990; Crutzen, 1992; Kerr and McElroy, 1993; Lubin and Jensen, 1995). In addition to the Antarctic ozone hole where UV radiation has been detected down to a depth of 70 m (Smith et al., 1992), ozone depletion has also been reported in the north polar region (Hoffman and Deshler, 1991). Biologically effective doses of UV-B radia-tion penetrate deep into the water column (Smith and Baker, 1979) and may thus affect the aquatic
* Corresponding author. Tel.: +49-9131-8528216; fax: + 49-9131-8528215.
E-mail address: [email protected] (D.-P. Ha¨der)
S0098-8472/00/$ - see front matter © 2000 Elsevier Science B.V. All rights reserved. PII: S 0 0 9 8 - 8 4 7 2 ( 9 9 ) 0 0 0 4 3 - X
(2)
ecosystems (Ha¨der et al., 1995). The penetration of UV-B strongly depends on the optical proper-ties of the water column. The depth of water required to remove 90% of the solar radiation at 310 nm varies from about 20 m in the clearest oceanic waters to a few centimeters in brown humic lakes and rivers (Kirk, 1994). All plant, animal and microbial groups appear to be sus-ceptible to UV-B, but to a highly variable ex-tent. UV-B is a small (B1% of total energy) but highly active component of the solar spectrum which has the potential to cause wide ranging effects, including destruction of proteins, DNA and other biologically relevant molecules, chronic depression of key physiological pro-cesses, acute physiological stress, and conse-quently the productivity of ecosystems (Karentz et al., 1991a; Vincent and Roy, 1993; Bothwell et al., 1994; Williamson, 1995; Sinha and Ha¨der, 1996).
Certain organisms have developed mechanisms counteracting the damaging effects of UV-B. Be-sides repair of UV-induced damage of DNA by photoreactivation and excision repair (Britt, 1995; Kim and Sancar, 1995) and accumulation of carotenoids and detoxifying enzymes or radi-cal quenchers and antioxidants that provide pro-tection by scavenging harmful radicals or oxygen species (Mittler and Tel-Or, 1991; Middleton and Teramura, 1993), an important mechanism to prevent UV-B-induced photodamage is the syn-thesis of UV-absorbing compounds.
Phenylpropanoids, mainly flavonoid deriva-tives, located in the epidermis have been re-ported to protect higher plants by absorbing harmful UV radiation (Tevini et al., 1991;
Koot-stra, 1994). Mycosporine-like amino acids
(MAAs) and the cyanobacterial sheath pigment, scytonemin, are thought to accomplish a similar function in lower organisms (Garcia-Pichel and Castenholz, 1991; Karentz et al., 1991b; Garcia-Pichel et al., 1993; Ehling-Schulz et al., 1997; Xiong et al., 1997). MAAs are water soluble substances characterized by a cyclohexenone or cyclohexenimine chromophore conjugated with the nitrogen substituent of an amino acid or its imino alcohol, having absorption maxima rang-ing from 310 to 360 nm (Nakamura et al., 1982).
MAAs have been identified in a number of taxo-nomically diverse organisms such as fungi (Fa-vre-Bonvin et al., 1976), marine heterotrophic bacteria (Arai et al., 1992), cyanobacteria (Gar-cia-Pichel et al., 1993; Karsten and Garcia-Pichel, 1996), eukaryotic algae (Carreto et al., 1990; Karentz et al., 1991a; Karsten et al., 1998), marine invertebrates (Karentz et al., 1991b; Shick et al., 1992), fish (Dunlap et al., 1989) and
a wide variety of other marine organisms
(Karentz et al., 1991a; Dunlap and Yamamoto, 1995; McClintock and Karentz, 1997; Carefoot et al., 1998; Dunlap and Shick, 1998).
Since macroalgae are sessile, they are restricted to their growth site and simultaneously exposed to elevated levels of PAR and UV radiation in their natural habitat. They can not avoid radia-tion stress by migraradia-tion to less affected areas like some microalgae. We tested the hypothesis that macroalgal communities might have devel-oped mechanisms to counteract the damaging ef-fects of radiation stress. Further the hypothesis that UV-B radiation at doses comparable to those in natural radiation has a significant im-pact on pigmentation and protein of this organ-ism was tested.
2. Materials and methods 2.1. The organism
The test organism Gracilaria cornea J. Agardh (Rhodophyta) was brought from Gran Canaria, Spain, where it has been routinely cultivated for the last 6 – 7 years. In nature, it normally grows free or attached to small rocks and coral frag-ments at low tide levels. The algae is light red/ rust colored, up to 30 cm tall and very rubbery. It does not have leaves and tends to divide by fragmentation. The organism was grown in ar-tificial sea-water (33 ppt; Instant Ocean,
Sarre-bourg, France and Mentor, Ohio, USA)
supplemented with nitrate (9.8 mM l−1) and phosphate (3.1 mM l−1) and illuminated with fluorescent light (1292 W m−2
) at a tempera-ture of 2092°C for a 12 h photoperiod.
(3)
2.2. Radiation source
The organisms were transferred to a transpar-ent container (20×20×8.5 cm) filled up to 3.5 cm with artificial sea water and placed on a rotary shaker to warrant uniform exposure. The algae were irradiated simultaneously under artificial ra-diation of ultraviolet-B (UV-B; 280 – 315 nm), ul-traviolet-A (UV-A; 315 – 400 nm) and fluorescent light (PAR; 400 – 700 nm), in the following re-ferred to as UV+PAR (Fig. 1). UV-C irradiation was eliminated with 295 nm cut-off filters (Ultra-phan, Digefra, Munich, Germany). UV-B irradia-tion was provided by a Philips Ultraviolet-B TL 40 W/12 (Holland) tube with its main output at 312 nm. The irradiation was adjusted to 1.0 W m−2
. UV-A irradiation was provided by a UV-A-340 tube (Q-Panel, Cleveland, Ohio, USA) with its main output at 340 nm. The irradiation was fixed at 1.0 W m−2. The source of visible light were OSRAM L 36 W/32 Lumilux de luxe warm white and Radium NL 36 W/26 Universal white (Germany) tubes, the irradiance of which was
fixed at 12 W m−2. When required, either a 395 nm (Ultraphan, UV Opak, Digefra, Munich, Ger-many) or a 320 nm (Montagefolie No. 10155099, Folex, Dreieich, Munich, Germany) UV filter was used to produce only the PAR and UV-A+PAR waveband, respectively. Alternatively, experiments were carried out with a transilluminator (Ba-chofer, Reutlingen, Germany) producing exclu-sively UV-B and UV-A (no PAR), with its main output at 312 nm (Fig. 1); the irradiance of this light source was fixed at 2.0 W m−2
(referred to as UV). The irradiances of the light sources were measured with a double monochromator spectro-radiometer (OL 754, Optronic Laboratories, Or-lando, FL, USA).
2.3. Extraction and partial purification of mycosporine-like amino acids(MAAs)
Aliquots of 0.5 g (fresh weight) of G. cornea
were homogenized and extracted in 5 ml of 20% (v/v) aqueous methanol (HPLC grade) by incu-bating at 45°C for 2.5 h. After centrifugation at
Fig. 1. Spectral characteristics of the light source. 1, transilluminator (UV-B plus UV-A;lmax=312 nm, ca. 2.0 W m−2for both UV-B and UV-A) with 295 nm cut-off filter; 2, UV-B TL 40 tube (lmax=312 nm, ca. 1.0 W m−2) plus UV-A-340 tube (l
max=340 nm, ca. 1.0 W m−2) plus OSRAM L 36 and Radium NL 36 fluorescent tubes (PAR; 400 – 700 nm, ca. 12 W m−2) with 295 nm cut-off filter; 3, same as in 2 with 320 nm cut-off filter.
(4)
5000 g; the supernatant was lyophilized and redis-solved in 2 ml of 100% methanol, vortexed for 2 – 3 min and centrifuged at 10 000×gfor 10 min. Thereafter the supernatant was evaporated to dry-ness at 45°C and the extract redissolved in 2 ml of 0.2% acetic acid. The samples were filtered through 0.2 mm pore-sized mikro-spin filters in order to partially purify the MAAs. These par-tially purified MAAs were separated by HPLC.
2.4. Extraction of crude pigments
FreshG.cornea(0.5 g) was homogenized with a mortar and pestle in 5 ml of 100% methanol and kept overnight in a refrigerator at 4°C. The result-ing suspension was centrifuged, and the superna-tant was used for the in vitro UV irradiation experiments.
2.5. High performance liquid chromatography (HPLC)
HPLC analysis of partially purified MAAs was performed with a HPLC (Merck Hitachi; Inter-face D-7000, UV-Detector L-7400, Pump L-7100, Darmstadt, Germany) equipped with a LiCro-spher RP 18 column and guard (5 mm packing; 250×4 mm I.D.). The sample was injected with a Hamilton syringe into the HPLC column through a Rheodyne injection valve equipped with a sam-ple loop. The wavelength for detection was 330 nm at a flow rate of 1.0 ml min−1 and a mobile phase of 0.2% acetic acid. Identification of MAAs was done by comparing the absorption spectra and retention times of several standards such as
De6alearea ramentacea, Porphyra saldanhae,
Bostrychia radicansand a supralitoral lichen.
2.6. UV and heat treatment
Purified MAAs or crude pigment extracts ofG.
cornea were transferred into a quartz cuvette (an optical path length of 10 mm, 2 mm thickness) and irradiated under UV. Absorption and fluores-cence spectra of the samples were recorded at regular time intervals. For heat treatment, MAAs were transferred in a 2 ml Eppendorf tube, incu-bated in a water bath at 7592°C, and absorption spectra were recorded at defined time intervals.
2.7. Absorption and fluorescence spectroscopy
Absorption spectra of samples were measured at regular intervals in a single beam spectrophoto-meter (DU 70, Beckman, Palo Alto, USA). The raw spectra were transferred to a microcomputer and treated mathematically and statistically using the software provided by the manufacturer. Fluo-rescence emission spectra were recorded simulta-neously with a spectrofluorometer (RF-5000, Shimadzu, Kyoto, Japan) at room temperature.
2.8. Sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE)
SDS-PAGE ofG.cornea, irradiated with UV+ PAR for up to four days was carried out in a vertical system (2001, Pharmacia) with gels of 155×130 mm, 1.5 mm thick, using the method described by Laemmli (1970), with a gradient (5 – 20% T) in the resolving gel. The electrophore-sis was run initially at 300 V and 30 mA for 1 h. The power was increased to 500 V and 60 mA as soon as the samples had run into the resolving gel. Gels were stained with Coomassie brilliant blue R 250 and dried in a gel dryer (Bio-Rad). Samples were run along with standard SDS molecular weight (SDS-7; approx. mol. wt. ranging from 14.2 to 66 kDa) markers (Sigma Technical Bul-letin, 1996). The protein concentration was deter-mined by the method of Bradford (1976). Bovine serum albumin was used as a standard.
2.9. Statistics
Results are expressed as the mean values of three replicates where appropriate and the statisti-cal significance of the means was tested with two-way ANOVA with a significance level of
PB0.05.
3. Results
Mycosporine-like amino acids extracted from
G. cornea were purified by HPLC and identified according to their retention times, absorption spectra and cochromatography with standards.
(5)
Fig. 2. High performance liquid chromatographic separation of the mycosporine-like amino acids (MAAs) from G. cornea. LiCrospher RP 18 column and guard; mobile phase 0.2% acetic acid; flow rate 1.0 ml min−1; detection by absorbance at 330 nm. 1 and 2, mycosporines with a retention time of 2.6 and 4.9, respectively, spectra of which are presented in Fig. 3.
Fig. 3. Absorption spectra of the purified MAAs ofG.cornea. 1 and 2, as separated by HPLC presented in Fig. 2.
nm (Fig. 3), respectively. were identified as por-phyra-334 and/or shinorine. There was no in vivo Two MAAs with retention times of 2.6 and 4.9
(6)
induction/retardation of the MAAs in G. cornea
even after 4 – 5 days of irradiation with any of the light sources either alone or in combination. The effect of heat was assayed by incubating MAAs in a water bath at 7592°C. Absorption spectra were taken at regular intervals of 1 h. Absorption properties of the MAAs were not significantly different (PB0.05) from that of the control even after 6 h of heat treatment (Fig. 4).
Absorption spectra of crude extracts of G.
cornea showed 6 main peaks at 265 (unknown compound), 334 (MAAs), 436 (chlorophylla) 475 (carotenoids), 618 (phycocyanin) and 665 nm (chlorophyll a) (Fig. 5). There was a significant decrease (PB0.05) in the absorbance at all peaks except at 334 nm after only 1 h of UV irradiation and a further bleaching with increasing UV irradi-ation time. After 6 h of irradiirradi-ation all peaks, except at 334 nm had more or less disappeared. There was no effect on the 334 nm (MAAs) peak even after 6 h of UV irradiation. A significant decrease (PB0.01) in the absorbance of MAAs could be recorded only after 24 h of continuous UV irradiation, but the complete elimination of the MAAs peak did not occur even after 72 h of
UV irradiation (Fig. 5).
Fluorescence excitation at the 436 nm peak of the crude extract of G. cornea resulted in an emission at 670 nm, which first showed an in-crease (PB0.05) in fluorescence and subsequently a slight shift towards shorter wavelengths after 0.5 h of UV irradiation (Fig. 6). A gradual increase (PB0.05) in fluorescence with a further shift to-wards shorter wavelengths continued up to 3 h of UV irradiation. The fluorescence returned to its initial level but with an obvious shift (PB0.01) towards shorter wavelengths after 4 h of UV irradiation. Thereafter, there was a gradual and steady decline (PB0.01) in fluorescence followed by a further shift towards shorter wavelengths with increasing duration of UV irradiation (Fig. 6). Fluorescence excitation at the 618 nm peak of the crude extract of G. cornea resulted in an emission at around 668 nm, which also first showed an increase (PB0.05) in fluorescence and subsequently a slight shift towards shorter wave-lengths after 0.5 h of UV irradiation (Fig. 7). Thereafter, there was a gradual and steady decline in fluorescence (PB0.01) followed by a further
(7)
Fig. 5. Absorption spectra of the methanolic extract of G. cornea with increasing UV exposure time. Note the predominant mycosporine-like amino acids peak at 334 nm.
Fig. 6. Fluorescence emission spectra of theG.corneafollowing increasing exposure time to UV when excited at 436 nm.
shift towards shorter wavelengths with increasing UV irradiation time (Fig. 7).
Changes in the total protein profile ofG.cornea
(8)
Fig. 7. Fluorescence emission spectra of theG.corneafollowing increasing exposure time to UV when excited at 618 nm.
ing increasing irradiation times to UV+PAR (Fig. 8). There was a gradual decrease in the intensity of protein bands at 20 kDa (a and b
subunits of phycocyanin) with increasing irradia-tion of UV+PAR; this band was more or less completely eliminated after 4 days of irradiation, but at the same time there was an increase in the intensity of protein bands at 26 kDa (phycoery-thrin) after the same duration of irradiation. Also the protein bands between 36 and 66 kDa initially showed an increase in intensity till 3 days of irradiation but thereafter remained constant.
4. Discussion
The data obtained in the present study support the hypothesis stated in the introduction and showed the presence of UV-absorbing com-pounds, MAAs, in the test organism G. cornea, which are highly persistent to UV and heat stress and thus may play a vital role as a first line of defense against these environmental stress factors in their natural habitats. Many organisms isolated from marine, freshwater or terrestrial habitats
contain MAAs. A few of them have been iden-tified while most still have to be characterized chemically. MAAs such as asterina-330, por-phyra-334, shinorine and mycosporine-gly are
Fig. 8. Vertical SDS-PAGE (gradient 5 – 20% T) protein profile ofG.corneafollowing UV plus PAR irradiation for 4 days. Lanes 1 and 7: marker proteins (66.0, albumin bovine; 45.0, albumin egg; 36.0, glyceraldehyde-3 phosphate; 29.0, carbonic anhydrase; 24.0, trypsinogen; 20.1, trypsin inhibitor; 14.2,
a-lactalbumin), lane 2: unirradiated control; lane 3: 1 day; lane 4: 2 days; lane 5: 3 days and lane 6: 4 days of UV plus PAR irradiation. Equal amount of proteins were loaded in each well.
(9)
common in diverse type of organisms (Karentz et al., 1991b). It is evident from the present investi-gation that the organism possesses fairly high amounts of UV-absorbing MAAs even without UV induction. While in the present study we did not attempt to chemically characterize the MAAs isolated from G. cornea, its spectral and other characteristics are fully comparable to those of porphyra-334 and/or shinorine. The occurrence of high concentrations of MAAs in marine organ-isms exposed to high levels of solar radiation has been proposed to provide protection as a UV-ab-sorbing sunscreen (Dunlap and Yamamoto, 1995; Karsten et al., 1998), but there is no conclusive evidence for the exclusive role of MAAs as sun-screen. It is possible that they play more than one role in the cellular metabolism of all or some organisms (Castenholz, 1997).
Studies with cyanobacteria have shown that MAAs prevent 3 out of 10 photons from hitting cytoplasmic targets. Cells with high concentra-tions of MAAs are :25% more resistant to UV radiation centered at 320 nm than those with no or low concentrations (Garcia-Pichel et al., 1993). Our results indicate that MAAs inG. cornea are highly stable against UV and heat stress. But they failed to provide complete protection to the pho-tosynthetic pigments, chlorophyll and the
acces-sory light harvesting pigments such as
phycocyanin, from UV induced photobleaching when the crude pigment extract containing high concentrations of MAAs were subjected to UV irradiation. It is pertinent to mention that the bleaching of chlorophyll and carotenoids is caused by photooxidation processes initiated by UV and visible light absorption of endogenous chromophores. The persistence of MAAs to oxi-dative processes as observed in the present study may be due to the fact that only oxo-carbonyl MAAs have antioxidant properties whereas the
imino-MAAs (porphyra-334 and shinorine)
present in G. cornea are oxidatively inert. The MAAs inNostoc communehave been shown to be extracellular and linked to oligosaccharides in the sheath (Bo¨hm et al., 1995). These glycosylated MAAs represent perhaps the only known example of MAAs that are actively excreted and accumu-lated extracellularly and therefore act as a true
screen (Ehling-Schulz et al., 1997). There may be physiological limitations to the accumulation of osmotically active compounds such as MAAs within the cell, and it seems probable that the maximal specific content of MAAs in the cell is
regulated by osmotic mechanisms which is
reflected by the fact that field populations of halotolerant cyanobacteria contain unusually high concentration of MAAs (Oren, 1997).
The results on changes in the absorption and fluorescence properties of chlorophyll and phyco-cyanin, following UV irradiation, are in accor-dance with earlier reports (Gerber and Ha¨der, 1995; Sinha et al., 1997). The initial increase in the fluorescence of chlorophyll following UV irradia-tion might be due to an accumulairradia-tion of excita-tion energy in the antenna pigments caused by a decrease of PS II activity. The shift in the fluores-cence emission of chlorophyll seems to be due to a decrease in the fluorescence of chlorophyll molecules which emit at longer wavelengths and an increase in the fluorescence of the substances such as the antenna pigments or pigments from the core complex which emit at shorter wave-lengths (Gerber and Ha¨der, 1995). Similarly, UV-induced changes in the fluorescence properties of phycocyanin followed by a shift towards shorter wavelengths are indicative of an impaired energy transfer from the phycobiliproteins to photosys-tems. The results indicate that pigmented proteins are one of the main targets of UV (Sinha et al., 1997). The SDS-PAGE protein profile of G.
cornea after UV+PAR irradiation shows a loss in the 20 kDa (phycocyanin) and simultaneously an increase in the 26 kDa (phycoerythrin) proteins. This could be attributed to a
phe-nomenon known as chromatic adaptation
(changes in pigmentation in photosynthetic organ-isms in response to light quality) by which an organism tries to cope with changes in its light environment (Tandeau de Marsac, 1977). The change in character of the light harvesting com-plex in response to the different wavelengths of light allows the cells to use the incident light efficiently (Grossman et al., 1994). The accessory light harvesting pigments phycocyanin and phyco-erythrin may operate as a second line of defense against photodamage and help the organism
(10)
sur-vive in highly irradiated environments. Phycobil-isomes are designed to funnel radiant energy spe-cifically to PS II at wavelengths where Chl a
molecules do not absorb, hence optimizing the energy capture and the colonization of environ-ments with different light regimes (Tandeau de Marsac, 1977).
We conclude that the studied macroalga G.
corneahas certain properties such as the presence of UV-absorbing compound, MAAs, and the ca-pacity to vary its phycobiliprotein ratio that may enable it to survive excessive irradiances in the natural habitats. Irrespective of the question whether the UV-B protective properties of MAAs and phycobiliproteins are a novel function or whether they are synthesized or accumulated due to UV-B irradiation, the presence of these com-pounds in an organism may provide protection to the internal organelles and components from the full impact of incident UV-B radiation.
Acknowledgements
This work was financially supported by the C.S.I.R. (9/13(795)/96-EMR-I(RK)213108), New Delhi, India to R.P. Sinha and by the European Union (DGXII, Environment programme, ENV4-CT97-0580) to D.-P. Ha¨der. We gratefully ac-knowledge Dr. Garcı´a-Reina, Instituto Algologia Aplicada, Gran Canaria, Spain, who provided the
G. corneastrain and Dr. Ulf Karsten,
Alfred-We-gener-Institut, Bremerhaven, Germany, for
providing MAAs standards. We thank M. Schus-ter for excellent technical assistance.
References
Arai, T., Nishijima, M., Adachi, K., Sano, H., 1992. Isolation and structure of a UV absorbing substance from the marine bacteriumMicrococcus sp. AK-334. MBI Report. Marine Biotechnology Institute, 2-35-10 Hongo, Bunkyo-ku, Tokyo 113, Japan, pp. 88 – 94.
Blumthaler, M., Ambach, W., 1990. Indication of increasing solar ultraviolet-B radiation flux in alpine regions. Science 248, 206 – 208.
Bo¨hm, G.A., Pfleiderer, W., Bo¨ger, P., Scherer, S., 1995. Structure of a novel oligosaccharide-mycosporine-amino
acid ultraviolet A/B sunscreen pigment from the terrestrial cyanobacterium Nostoc commune. J. Biol. Chem. 270, 8536 – 8539.
Bothwell, M.L., Sherbot, D.M.J., Pollock, C.M., 1994. Ecosystem response to solar ultraviolet-B radiation: influ-ence of trophic-level interactions. Sciinflu-ence 265, 97 – 100. Bradford, M.M., 1976. A rapid and sensitive method for the
quantification of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 72, 248 – 254.
Britt, A.B., 1995. Repair of DNA damage induced by ultravi-olet radiation. Plant Physiol. 108, 891 – 896.
Carefoot, T.H., Harris, M., Taylor, B.E., Donovan, D., Karentz, D., 1998. Mycosporine-like amino acids: possible UV protection in eggs of the sea hareAplysia dactylomela. Mar. Biol. 130, 389 – 396.
Carreto, J.I., Carignan, M.O., Daleo, G., De Marco, S.G., 1990. Occurrence of mycosporine-like amino acids in the red tide dinoflagellateAlexandrium exca6atum: UV-protec-tive compounds? J. Plankton Res. 12, 909 – 921.
Castenholz, R.W., 1997. Multiple strategies for UV tolerance in cyanobacteria. Spectrum 10, 10 – 16.
Crutzen, P.J., 1992. Ultraviolet on the increase. Nature 356, 104 – 105.
Dunlap, W.C., Yamamoto, Y., 1995. Small-molecule antioxi-dants in marine organisms: antioxidant activity of my-cosporine-glycine. Comp. Biochem. Physiol. 112, 105 – 114. Dunlap, W.C., Shick, J.M., 1998. Ultraviolet radiation-ab-sorbing mycosporine-like amino acids in coral reef organ-isms: a biochemical and environmental perspective. J. Phycol. 34, 418 – 430.
Dunlap, W.C., Williams, D.M., Chalker, B.E., Banaszak, A.T., 1989. Biochemical photoadaptations in vision: UV-absorbing pigments in fish eye tissues. Comp. Biochem. Physiol. 93, 601 – 607.
Ehling-Schulz, M., Bilger, W., Scherer, S., 1997. UV-B-in-duced synthesis of photoprotective pigments and extracel-lular polysaccharides in the terrestrial cyanobacterium Nostoc commune. J. Bacteriol. 179, 1940 – 1945.
Favre-Bonvin, J., Arpin, N., Brevard, C., 1976. Structure de la mycosporine (P 310). Can. J. Chem. 54, 1105 – 1113. Garcia-Pichel, F., Castenholz, R.W., 1991. Characterization
and biological impliations of scytonemin, a cyanobacterial sheath pigment. J. Phycol. 27, 395 – 409.
Garcia-Pichel, F., Wingard, C.E., Castenholz, R.W., 1993. Evidence regarding the UV sunscreen role of a my-cosporine-like compound in the cyanobacterium Gloeocapsasp.. Appl. Environ. Microbiol. 59, 170 – 176. Gerber, S., Ha¨der, D.-P., 1995. Effects of artificial UV-B and
simulated solar radiation on the flagellateEuglena gracilis: physiological, spectroscopical and biochemical investiga-tions. Acta Protozool. 34, 13 – 20.
Grossman, A.R., Schaefer, M.R., Chiang, G.G., Collier, J.L., 1994. The responses of cyanobacteria to environmental conditions: light and nutrients. In: Bryant, D.A. (Ed.), The Molecular Biology of Cyanobacteria. Kluwer Academic Publishers, Dordrecht, pp. 641 – 675.
(11)
Ha¨der, D.-P., Worrest, R.C., Kumar, H.D., Smith, R.C., 1995. Effects of increased solar ultraviolet radiation on aquatic ecosystems. Ambio 24, 174 – 180.
Hoffman, D.J., Deshler, T., 1991. Evidence from balloon measurements for chemical depletion of stratospheric ozone in the Arctic winter of 1989 – 90. Nature 349, 300 – 305.
Karentz, D., Cleaver, J.E., Mitchell, D.L., 1991a. Cell survival characteristics and molecular responses of Antarctic phyto-plankton to ultraviolet-B radiation. J. Phycol. 27, 326 – 341. Karentz, D., McEuen, F.S., Land, M.C., Dunlap, W.C., 1991b. Survey of mycosporine-like amino acid compounds in Antarctic marine organism: potential protection from ultraviolet exposure. Mar. Biol. 108, 157 – 166.
Karsten, U., Garcia-Pichel, F., 1996. Carotenoids and my-cosporine-like amino acid compounds in members of the genus Microcoleus (Cyanobacteria): a chemosystematic study. Syst. Appl. Microbiol. 19, 285 – 294.
Karsten, U., Franklin, L.A., Lu¨ning, K., Wiencke, C., 1998. Natural ultraviolet radiation and photosynthetically active radiation induce formation of mycosporine-like amino acids in the marine macroalgaChondrus crispus (Rhodo-phyta). Planta 205, 257 – 262.
Kerr, J.B., McElroy, C.T., 1993. Evidence for large upward trends of ultraviolet-B radiation linked to ozone depletion. Science 262, 1032 – 1034.
Kim, S.-T., Sancar, A., 1995. Photorepair of nonadjacent pyrimidine dimers by DNA photolyase. Photochem. Pho-tobiol. 61, 171 – 174.
Kirk, J.T.O., 1994. Optics of UV-B radiation in natural wa-ters. Arch. Hydrobiol. 43, 1 – 16.
Kootstra, A., 1994. Protection from UV-B induced DNA damage by flavonoids. Plant Mol. Biol. 26, 771 – 774. Laemmli, U.K., 1970. Cleavage of structural proteins during
the assembly of the head of bacteriophage T4. Nature 227, 680 – 685.
Lubin, D., Jensen, E.H., 1995. Effects of clouds and strato-spheric ozone depletion on ultraviolet radiation trends. Nature 377, 710 – 713.
McClintock, J.B., Karentz, D., 1997. Mycosporine-like amino acids in 38 species of subtidal marine organisms from McMurdo Sound, Antarctica. Antarc. Sci. 9, 392 – 398. Middleton, E.M., Teramura, A.H., 1993. The role of flavonol
glycosides and carotenoids in protecting soybean from ultraviolet-B damage. Plant Physiol. 103, 741 – 752.
Mittler, R., Tel-Or, E., 1991. Oxidative stress responses in the unicellular cyanobacteriumSynechococcusPCC7942. Free Radical Res. Commun. 12, 845 – 850.
Nakamura, H., Kobayashi, J., Hirata, Y., 1982. Separation of micosporine-like amino acids in marine organisms using reverse-phase high performance liquid chromatography. J. Chromatogr. 250, 113 – 118.
Oren, A., 1997. Mycosporine-like amino acids as osmotic solutes in a community of halophilic cyanobacteria. Geo-microbiol. J. 14, 231 – 240.
Shick, J.M., Dunlap, W.C., Chalker, B.E., Banaszak, A.T., Rosenzweig, T.K., 1992. Survey of ultraviolet radiation absorbing mycosporine-like amino acids in organs of coral reef holothuroids. Mar. Ecol. Prog. Ser. 90, 139 – 148. Sigma Technical Bulletin No. MWS-877L, 1996. Dalton Mark
VII-L for SDS Gel Electrophoresis. Sigma Chemical Com-pany, St. Louis, MO, USA.
Sinha, R.P., Ha¨der, D.-P., 1996. Photobiology and ecophysiol-ogy of rice field cyanobacteria. Photochem. Photobiol. 64, 887 – 896.
Sinha, R.P., Singh, N., Kumar, A., Kumar, H.D., Ha¨der, D.-P., 1997. Impacts of ultraviolet-B irradiation on nitro-gen-fixing cyanobacteria of rice paddy fields. J. Plant Phys-iol. 150, 188 – 193.
Smith, R.C., Baker, K.S., 1979. Penetration of UV-B and biologically effective dose-rates in natural waters. Pho-tochem. Photobiol. 29, 311 – 323.
Smith, R.C., Prezelin, B.B., Baker, K.S., et al., 1992. Ozone depletion: ultraviolet radiation and phytoplankton biology in Antarctic waters. Science 255, 952 – 959.
Tandeau de Marsac, N., 1977. Occurrence and nature of chromatic adaptation in cyanobacteria. J. Bacteriol. 130, 82 – 91.
Tevini, M., Braun, J., Fieser, G., 1991. The protective function of the epidermal layer of rye seedlings against ultraviolet-B radiation. Photochem. Photobiol. 53, 329 – 333.
Vincent, W.F., Roy, S., 1993. Solar ultraviolet-B radiation and aquatic primary production: damage, protection, and re-covery. Env. Rev. 1, 1 – 12.
Williamson, C.E., 1995. What role does UVB radiation play in freshwater ecosystems? Limnol. Oceanogr. 40, 386 – 392. Xiong, F., Komenda, J., Kopecky, J., Nedbal, L., 1997.
Strategies of ultraviolet-B protection in microscopic algae. Physiol. Plant. 100, 378 – 388.
(1)
R.P.Sinha et al./En6ironmental and Experimental Botany43 (2000) 33 – 43
38
induction/retardation of the MAAs in G. cornea
even after 4 – 5 days of irradiation with any of the light sources either alone or in combination. The effect of heat was assayed by incubating MAAs in a water bath at 7592°C. Absorption spectra were taken at regular intervals of 1 h. Absorption properties of the MAAs were not significantly different (PB0.05) from that of the control even after 6 h of heat treatment (Fig. 4).
Absorption spectra of crude extracts of G.
cornea showed 6 main peaks at 265 (unknown compound), 334 (MAAs), 436 (chlorophylla) 475 (carotenoids), 618 (phycocyanin) and 665 nm (chlorophyll a) (Fig. 5). There was a significant decrease (PB0.05) in the absorbance at all peaks except at 334 nm after only 1 h of UV irradiation and a further bleaching with increasing UV irradi-ation time. After 6 h of irradiirradi-ation all peaks, except at 334 nm had more or less disappeared. There was no effect on the 334 nm (MAAs) peak even after 6 h of UV irradiation. A significant decrease (PB0.01) in the absorbance of MAAs could be recorded only after 24 h of continuous UV irradiation, but the complete elimination of the MAAs peak did not occur even after 72 h of
UV irradiation (Fig. 5).
Fluorescence excitation at the 436 nm peak of the crude extract of G. cornea resulted in an emission at 670 nm, which first showed an in-crease (PB0.05) in fluorescence and subsequently a slight shift towards shorter wavelengths after 0.5 h of UV irradiation (Fig. 6). A gradual increase (PB0.05) in fluorescence with a further shift to-wards shorter wavelengths continued up to 3 h of UV irradiation. The fluorescence returned to its initial level but with an obvious shift (PB0.01) towards shorter wavelengths after 4 h of UV irradiation. Thereafter, there was a gradual and steady decline (PB0.01) in fluorescence followed by a further shift towards shorter wavelengths with increasing duration of UV irradiation (Fig. 6). Fluorescence excitation at the 618 nm peak of the crude extract of G. cornea resulted in an emission at around 668 nm, which also first showed an increase (PB0.05) in fluorescence and subsequently a slight shift towards shorter wave-lengths after 0.5 h of UV irradiation (Fig. 7). Thereafter, there was a gradual and steady decline in fluorescence (PB0.01) followed by a further
(2)
Fig. 5. Absorption spectra of the methanolic extract of G. cornea with increasing UV exposure time. Note the predominant mycosporine-like amino acids peak at 334 nm.
Fig. 6. Fluorescence emission spectra of theG.corneafollowing increasing exposure time to UV when excited at 436 nm.
shift towards shorter wavelengths with increasing UV irradiation time (Fig. 7).
Changes in the total protein profile ofG.cornea
(3)
R.P.Sinha et al./En6ironmental and Experimental Botany43 (2000) 33 – 43
40
Fig. 7. Fluorescence emission spectra of theG.corneafollowing increasing exposure time to UV when excited at 618 nm.
ing increasing irradiation times to UV+PAR (Fig. 8). There was a gradual decrease in the intensity of protein bands at 20 kDa (a and b subunits of phycocyanin) with increasing irradia-tion of UV+PAR; this band was more or less completely eliminated after 4 days of irradiation, but at the same time there was an increase in the intensity of protein bands at 26 kDa (phycoery-thrin) after the same duration of irradiation. Also the protein bands between 36 and 66 kDa initially showed an increase in intensity till 3 days of irradiation but thereafter remained constant.
4. Discussion
The data obtained in the present study support the hypothesis stated in the introduction and showed the presence of UV-absorbing com-pounds, MAAs, in the test organism G. cornea, which are highly persistent to UV and heat stress and thus may play a vital role as a first line of defense against these environmental stress factors in their natural habitats. Many organisms isolated from marine, freshwater or terrestrial habitats
contain MAAs. A few of them have been iden-tified while most still have to be characterized chemically. MAAs such as asterina-330, por-phyra-334, shinorine and mycosporine-gly are
Fig. 8. Vertical SDS-PAGE (gradient 5 – 20% T) protein profile ofG.corneafollowing UV plus PAR irradiation for 4 days. Lanes 1 and 7: marker proteins (66.0, albumin bovine; 45.0, albumin egg; 36.0, glyceraldehyde-3 phosphate; 29.0, carbonic anhydrase; 24.0, trypsinogen; 20.1, trypsin inhibitor; 14.2, a-lactalbumin), lane 2: unirradiated control; lane 3: 1 day; lane 4: 2 days; lane 5: 3 days and lane 6: 4 days of UV plus PAR irradiation. Equal amount of proteins were loaded in each well.
(4)
common in diverse type of organisms (Karentz et al., 1991b). It is evident from the present investi-gation that the organism possesses fairly high amounts of UV-absorbing MAAs even without UV induction. While in the present study we did not attempt to chemically characterize the MAAs isolated from G. cornea, its spectral and other characteristics are fully comparable to those of porphyra-334 and/or shinorine. The occurrence of high concentrations of MAAs in marine organ-isms exposed to high levels of solar radiation has been proposed to provide protection as a UV-ab-sorbing sunscreen (Dunlap and Yamamoto, 1995; Karsten et al., 1998), but there is no conclusive evidence for the exclusive role of MAAs as sun-screen. It is possible that they play more than one role in the cellular metabolism of all or some organisms (Castenholz, 1997).
Studies with cyanobacteria have shown that MAAs prevent 3 out of 10 photons from hitting cytoplasmic targets. Cells with high concentra-tions of MAAs are :25% more resistant to UV radiation centered at 320 nm than those with no or low concentrations (Garcia-Pichel et al., 1993). Our results indicate that MAAs inG. cornea are highly stable against UV and heat stress. But they failed to provide complete protection to the pho-tosynthetic pigments, chlorophyll and the acces-sory light harvesting pigments such as phycocyanin, from UV induced photobleaching when the crude pigment extract containing high concentrations of MAAs were subjected to UV irradiation. It is pertinent to mention that the bleaching of chlorophyll and carotenoids is caused by photooxidation processes initiated by UV and visible light absorption of endogenous chromophores. The persistence of MAAs to oxi-dative processes as observed in the present study may be due to the fact that only oxo-carbonyl MAAs have antioxidant properties whereas the imino-MAAs (porphyra-334 and shinorine) present in G. cornea are oxidatively inert. The MAAs inNostoc communehave been shown to be extracellular and linked to oligosaccharides in the sheath (Bo¨hm et al., 1995). These glycosylated MAAs represent perhaps the only known example of MAAs that are actively excreted and accumu-lated extracellularly and therefore act as a true
screen (Ehling-Schulz et al., 1997). There may be physiological limitations to the accumulation of osmotically active compounds such as MAAs within the cell, and it seems probable that the maximal specific content of MAAs in the cell is regulated by osmotic mechanisms which is reflected by the fact that field populations of halotolerant cyanobacteria contain unusually high concentration of MAAs (Oren, 1997).
The results on changes in the absorption and fluorescence properties of chlorophyll and phyco-cyanin, following UV irradiation, are in accor-dance with earlier reports (Gerber and Ha¨der, 1995; Sinha et al., 1997). The initial increase in the fluorescence of chlorophyll following UV irradia-tion might be due to an accumulairradia-tion of excita-tion energy in the antenna pigments caused by a decrease of PS II activity. The shift in the fluores-cence emission of chlorophyll seems to be due to a decrease in the fluorescence of chlorophyll molecules which emit at longer wavelengths and an increase in the fluorescence of the substances such as the antenna pigments or pigments from the core complex which emit at shorter wave-lengths (Gerber and Ha¨der, 1995). Similarly, UV-induced changes in the fluorescence properties of phycocyanin followed by a shift towards shorter wavelengths are indicative of an impaired energy transfer from the phycobiliproteins to photosys-tems. The results indicate that pigmented proteins are one of the main targets of UV (Sinha et al., 1997). The SDS-PAGE protein profile of G.
cornea after UV+PAR irradiation shows a loss in the 20 kDa (phycocyanin) and simultaneously an increase in the 26 kDa (phycoerythrin) proteins. This could be attributed to a phe-nomenon known as chromatic adaptation (changes in pigmentation in photosynthetic organ-isms in response to light quality) by which an organism tries to cope with changes in its light environment (Tandeau de Marsac, 1977). The change in character of the light harvesting com-plex in response to the different wavelengths of light allows the cells to use the incident light efficiently (Grossman et al., 1994). The accessory light harvesting pigments phycocyanin and phyco-erythrin may operate as a second line of defense against photodamage and help the organism
(5)
sur-R.P.Sinha et al./En6ironmental and Experimental Botany43 (2000) 33 – 43
42
vive in highly irradiated environments. Phycobil-isomes are designed to funnel radiant energy spe-cifically to PS II at wavelengths where Chl a
molecules do not absorb, hence optimizing the energy capture and the colonization of environ-ments with different light regimes (Tandeau de Marsac, 1977).
We conclude that the studied macroalga G.
corneahas certain properties such as the presence of UV-absorbing compound, MAAs, and the ca-pacity to vary its phycobiliprotein ratio that may enable it to survive excessive irradiances in the natural habitats. Irrespective of the question whether the UV-B protective properties of MAAs and phycobiliproteins are a novel function or whether they are synthesized or accumulated due to UV-B irradiation, the presence of these com-pounds in an organism may provide protection to the internal organelles and components from the full impact of incident UV-B radiation.
Acknowledgements
This work was financially supported by the C.S.I.R. (9/13(795)/96-EMR-I(RK)213108), New Delhi, India to R.P. Sinha and by the European Union (DGXII, Environment programme, ENV4-CT97-0580) to D.-P. Ha¨der. We gratefully ac-knowledge Dr. Garcı´a-Reina, Instituto Algologia Aplicada, Gran Canaria, Spain, who provided the
G. corneastrain and Dr. Ulf Karsten, Alfred-We-gener-Institut, Bremerhaven, Germany, for providing MAAs standards. We thank M. Schus-ter for excellent technical assistance.
References
Arai, T., Nishijima, M., Adachi, K., Sano, H., 1992. Isolation and structure of a UV absorbing substance from the marine bacteriumMicrococcus sp. AK-334. MBI Report. Marine Biotechnology Institute, 2-35-10 Hongo, Bunkyo-ku, Tokyo 113, Japan, pp. 88 – 94.
Blumthaler, M., Ambach, W., 1990. Indication of increasing solar ultraviolet-B radiation flux in alpine regions. Science 248, 206 – 208.
Bo¨hm, G.A., Pfleiderer, W., Bo¨ger, P., Scherer, S., 1995. Structure of a novel oligosaccharide-mycosporine-amino
acid ultraviolet A/B sunscreen pigment from the terrestrial cyanobacterium Nostoc commune. J. Biol. Chem. 270, 8536 – 8539.
Bothwell, M.L., Sherbot, D.M.J., Pollock, C.M., 1994. Ecosystem response to solar ultraviolet-B radiation: influ-ence of trophic-level interactions. Sciinflu-ence 265, 97 – 100. Bradford, M.M., 1976. A rapid and sensitive method for the
quantification of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 72, 248 – 254.
Britt, A.B., 1995. Repair of DNA damage induced by ultravi-olet radiation. Plant Physiol. 108, 891 – 896.
Carefoot, T.H., Harris, M., Taylor, B.E., Donovan, D., Karentz, D., 1998. Mycosporine-like amino acids: possible UV protection in eggs of the sea hareAplysia dactylomela. Mar. Biol. 130, 389 – 396.
Carreto, J.I., Carignan, M.O., Daleo, G., De Marco, S.G., 1990. Occurrence of mycosporine-like amino acids in the red tide dinoflagellateAlexandrium exca6atum:
UV-protec-tive compounds? J. Plankton Res. 12, 909 – 921.
Castenholz, R.W., 1997. Multiple strategies for UV tolerance in cyanobacteria. Spectrum 10, 10 – 16.
Crutzen, P.J., 1992. Ultraviolet on the increase. Nature 356, 104 – 105.
Dunlap, W.C., Yamamoto, Y., 1995. Small-molecule antioxi-dants in marine organisms: antioxidant activity of my-cosporine-glycine. Comp. Biochem. Physiol. 112, 105 – 114. Dunlap, W.C., Shick, J.M., 1998. Ultraviolet radiation-ab-sorbing mycosporine-like amino acids in coral reef organ-isms: a biochemical and environmental perspective. J. Phycol. 34, 418 – 430.
Dunlap, W.C., Williams, D.M., Chalker, B.E., Banaszak, A.T., 1989. Biochemical photoadaptations in vision: UV-absorbing pigments in fish eye tissues. Comp. Biochem. Physiol. 93, 601 – 607.
Ehling-Schulz, M., Bilger, W., Scherer, S., 1997. UV-B-in-duced synthesis of photoprotective pigments and extracel-lular polysaccharides in the terrestrial cyanobacterium
Nostoc commune. J. Bacteriol. 179, 1940 – 1945.
Favre-Bonvin, J., Arpin, N., Brevard, C., 1976. Structure de la mycosporine (P 310). Can. J. Chem. 54, 1105 – 1113. Garcia-Pichel, F., Castenholz, R.W., 1991. Characterization
and biological impliations of scytonemin, a cyanobacterial sheath pigment. J. Phycol. 27, 395 – 409.
Garcia-Pichel, F., Wingard, C.E., Castenholz, R.W., 1993. Evidence regarding the UV sunscreen role of a my-cosporine-like compound in the cyanobacterium
Gloeocapsasp.. Appl. Environ. Microbiol. 59, 170 – 176. Gerber, S., Ha¨der, D.-P., 1995. Effects of artificial UV-B and
simulated solar radiation on the flagellateEuglena gracilis: physiological, spectroscopical and biochemical investiga-tions. Acta Protozool. 34, 13 – 20.
Grossman, A.R., Schaefer, M.R., Chiang, G.G., Collier, J.L., 1994. The responses of cyanobacteria to environmental conditions: light and nutrients. In: Bryant, D.A. (Ed.), The Molecular Biology of Cyanobacteria. Kluwer Academic Publishers, Dordrecht, pp. 641 – 675.
(6)
Ha¨der, D.-P., Worrest, R.C., Kumar, H.D., Smith, R.C., 1995. Effects of increased solar ultraviolet radiation on aquatic ecosystems. Ambio 24, 174 – 180.
Hoffman, D.J., Deshler, T., 1991. Evidence from balloon measurements for chemical depletion of stratospheric ozone in the Arctic winter of 1989 – 90. Nature 349, 300 – 305.
Karentz, D., Cleaver, J.E., Mitchell, D.L., 1991a. Cell survival characteristics and molecular responses of Antarctic phyto-plankton to ultraviolet-B radiation. J. Phycol. 27, 326 – 341. Karentz, D., McEuen, F.S., Land, M.C., Dunlap, W.C., 1991b. Survey of mycosporine-like amino acid compounds in Antarctic marine organism: potential protection from ultraviolet exposure. Mar. Biol. 108, 157 – 166.
Karsten, U., Garcia-Pichel, F., 1996. Carotenoids and my-cosporine-like amino acid compounds in members of the genus Microcoleus (Cyanobacteria): a chemosystematic study. Syst. Appl. Microbiol. 19, 285 – 294.
Karsten, U., Franklin, L.A., Lu¨ning, K., Wiencke, C., 1998. Natural ultraviolet radiation and photosynthetically active radiation induce formation of mycosporine-like amino acids in the marine macroalgaChondrus crispus (Rhodo-phyta). Planta 205, 257 – 262.
Kerr, J.B., McElroy, C.T., 1993. Evidence for large upward trends of ultraviolet-B radiation linked to ozone depletion. Science 262, 1032 – 1034.
Kim, S.-T., Sancar, A., 1995. Photorepair of nonadjacent pyrimidine dimers by DNA photolyase. Photochem. Pho-tobiol. 61, 171 – 174.
Kirk, J.T.O., 1994. Optics of UV-B radiation in natural wa-ters. Arch. Hydrobiol. 43, 1 – 16.
Kootstra, A., 1994. Protection from UV-B induced DNA damage by flavonoids. Plant Mol. Biol. 26, 771 – 774. Laemmli, U.K., 1970. Cleavage of structural proteins during
the assembly of the head of bacteriophage T4. Nature 227, 680 – 685.
Lubin, D., Jensen, E.H., 1995. Effects of clouds and strato-spheric ozone depletion on ultraviolet radiation trends. Nature 377, 710 – 713.
McClintock, J.B., Karentz, D., 1997. Mycosporine-like amino acids in 38 species of subtidal marine organisms from McMurdo Sound, Antarctica. Antarc. Sci. 9, 392 – 398. Middleton, E.M., Teramura, A.H., 1993. The role of flavonol
glycosides and carotenoids in protecting soybean from ultraviolet-B damage. Plant Physiol. 103, 741 – 752.
Mittler, R., Tel-Or, E., 1991. Oxidative stress responses in the unicellular cyanobacteriumSynechococcusPCC7942. Free Radical Res. Commun. 12, 845 – 850.
Nakamura, H., Kobayashi, J., Hirata, Y., 1982. Separation of micosporine-like amino acids in marine organisms using reverse-phase high performance liquid chromatography. J. Chromatogr. 250, 113 – 118.
Oren, A., 1997. Mycosporine-like amino acids as osmotic solutes in a community of halophilic cyanobacteria. Geo-microbiol. J. 14, 231 – 240.
Shick, J.M., Dunlap, W.C., Chalker, B.E., Banaszak, A.T., Rosenzweig, T.K., 1992. Survey of ultraviolet radiation absorbing mycosporine-like amino acids in organs of coral reef holothuroids. Mar. Ecol. Prog. Ser. 90, 139 – 148. Sigma Technical Bulletin No. MWS-877L, 1996. Dalton Mark
VII-L for SDS Gel Electrophoresis. Sigma Chemical Com-pany, St. Louis, MO, USA.
Sinha, R.P., Ha¨der, D.-P., 1996. Photobiology and ecophysiol-ogy of rice field cyanobacteria. Photochem. Photobiol. 64, 887 – 896.
Sinha, R.P., Singh, N., Kumar, A., Kumar, H.D., Ha¨der, D.-P., 1997. Impacts of ultraviolet-B irradiation on nitro-gen-fixing cyanobacteria of rice paddy fields. J. Plant Phys-iol. 150, 188 – 193.
Smith, R.C., Baker, K.S., 1979. Penetration of UV-B and biologically effective dose-rates in natural waters. Pho-tochem. Photobiol. 29, 311 – 323.
Smith, R.C., Prezelin, B.B., Baker, K.S., et al., 1992. Ozone depletion: ultraviolet radiation and phytoplankton biology in Antarctic waters. Science 255, 952 – 959.
Tandeau de Marsac, N., 1977. Occurrence and nature of chromatic adaptation in cyanobacteria. J. Bacteriol. 130, 82 – 91.
Tevini, M., Braun, J., Fieser, G., 1991. The protective function of the epidermal layer of rye seedlings against ultraviolet-B radiation. Photochem. Photobiol. 53, 329 – 333.
Vincent, W.F., Roy, S., 1993. Solar ultraviolet-B radiation and aquatic primary production: damage, protection, and re-covery. Env. Rev. 1, 1 – 12.
Williamson, C.E., 1995. What role does UVB radiation play in freshwater ecosystems? Limnol. Oceanogr. 40, 386 – 392. Xiong, F., Komenda, J., Kopecky, J., Nedbal, L., 1997.
Strategies of ultraviolet-B protection in microscopic algae. Physiol. Plant. 100, 378 – 388.