INFLUENCE OF CELL WALL COMPOSITION ON THE RESISTANCE OF TWO CHLORELLA SPECIES (CHLOROPHYTA) TO DETERGENTS 1

The influence of dodecylbenzene sulfonate (DBS) and Triton X‐100 (TX‐100) was examined on two species of Chlorella exhibiting conspicuous differences in cell wall composition. Chlorella emersonii has both a classical polysaccharidic wall and a thin trilaminar outer wall (TLS) composed of nonhydrolyzable macromolecules. Chlorella vulgaris lacks a TLS. Photosynthetic capacity was measured following short exposures (1 h) of the algae at different physiological stages to high DBS and TX‐100 concentrations, up to 1 g·L−1. Comparisons with untreated controls indicated that 1) the presence of a TLS in C. emersonii was associated with a very high resistance to the anionic (DBS) and nonionic (TX‐100) detergents at all growth stages, and net photosynthesis was not significantly affected in that species, 2) a high toxicity, particularly pronounced with TX‐100, was observed for actively growing cells of the TLS‐devoid species, C. vulgaris, and 3) aging exerted a protective influence, especially efficient against DBS, on the latter species. Additional observations, including fluorescence spectra and high‐performance liquid chromatography pigment analyses, were conducted following short exposures of actively growing cells. Fluorescence emission spectra revealed that the chlorophyll a‐protein complexes in thylakoid membranes were not substantially affected by DBS and TX‐100, even in the case of C. vulgaris. In sharp contrast, fluorescence excitation spectra on the latter species showed 1) that excitation transfer from antenna pigments to chlorophyll a in reaction centers was substantially altered with both detergents and 2) that the two detergents affected different parts of the photosynthetic system of the TLS‐devoid species. Analyses of C. vulgaris extracts indicated significant decreases in pigment content following exposure to DBS and, to a lesser extent, to TX‐100. Longer exposure experiments (1 day) were conducted with actively growing algae. The TLS‐containing species still showed a very high resistance and no important changes in photosynthetic capacity compared to cells exposed for 1 h. For the sensitive TLS‐devoid species, the detrimental influence of TX‐100, already very high after 1 h, was not increased. DBS toxicity was markedly increased and may reflect a lower uptake rate of DBS by C. vulgaris.

[1]  S. Derenne,et al.  Occurrence of non-hydrolysable amides in the macromolecular constituent of Scenedesmus quadricauda cell wall as revealed by 15N NMR: Origin of n-alkylnitriles in pyrolysates of ultralaminae-containing kerogens , 1993 .

[2]  S. Derenne,et al.  Formation of ultralaminae in marine kerogens via selective preservation of thin resistant outer walls of microalgae , 1992 .

[3]  S. Derenne,et al.  Structure of Chlorella fusca algaenan: relationships with ultralaminae in lacustrine kerogens; species- and environment-dependent variations in the composition of fossil ultralaminae , 1992 .

[4]  J. Csöllei,et al.  Effects of substituted aryloxyaminopropanols on photosynthesis and photosynthesizing organisms. , 1991, General physiology and biophysics.

[5]  S. Derenne,et al.  Chemical evidence of kerogen formation in source rocks and oil shales via selective preservation of thin resistant outer walls of microalgae: Origin of ultralaminae , 1991 .

[6]  S. Derenne,et al.  A reappraisal of kerogen formation , 1989 .

[7]  P. Viswanathan,et al.  Phycotoxicity of linear alkylbenzene sulfonate. , 1988, Ecotoxicology and environmental safety.

[8]  C. Largeau,et al.  OCCURRENCE OF A RESISTANT BIOPOLYMER IN THE OUTER WALLS OF THE PARASITIC ALGA PROTOTHECA WICKERHAMII (CHLOROCOCCALSES): ULTRASTRUCTURAL AND CHEMICAL STUDIES 1 , 1987 .

[9]  A. Schmidt,et al.  A Correlation between Detergent Tolerance and Cell Wall Structure in Green Algae , 1987 .

[10]  R. Honegger,et al.  Chemical and ultrastructural studies on the distribution of sporopolleninlike biopolymers in six genera of lichen phycobionts , 1985 .

[11]  D. Chaumont,et al.  Studies on batch and continuous cultures of Botryococcus braunii: Hydrocarbon production in relation to physiological state, cell ultrastructure, and phosphate nutrition , 1985, Biotechnology and bioengineering.

[12]  H. Nyberg,et al.  The glycolipid fatty acids of Porphyridium purpureum cultured in the presence of detergents , 1984 .

[13]  Y. Azov,et al.  Effect of Hard Detergents on Algae in a High-Rate-Oxidation Pond , 1982, Applied and environmental microbiology.

[14]  J. Neuhold,et al.  Alkyl benzene sulfonate effects on stream algae communities , 1966, Bulletin of environmental contamination and toxicology.

[15]  D. Adema,et al.  Bacteriostatic, fungistatic, and algistatic activity of fatty nitrogen compounds. , 1966, Applied microbiology.

[16]  F. Devínsky,et al.  Effect of surfactants on growth, chlorophyll content and Hill reaction activity , 1992 .

[17]  S. Derenne,et al.  Occurrence and origin of “ultralaminar” structures in “amorphous” kerogens of various source rocks and oil shales , 1990 .

[18]  P. Hermann,et al.  Effect of detergents on thylakoid membranes of chloroplasts , 1988 .

[19]  R. Ernst,et al.  Biological effects of surfactants: Part 6—effects of anionic, non-ionic and amphoteric surfactants on a green alga (Chlamydomonas) , 1983 .

[20]  W. Slooff,et al.  Substitutes for phosphate containing washing products: Their toxicity and biodegradability in the aquatic environment , 1982 .

[21]  P. Dhamelincourt,et al.  Sites of accumulation and composition of hydrocarbons in Botryococcus braunii , 1980 .

[22]  P. Lundahl,et al.  Molecular structure—biological properties relationships in anionic surface-active agents , 1978 .