Compartmentation of Phenolic Compounds and Phenylalanine AmmoniaLyase in Leaves of Phyllanthus...

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Compartmentation of Phenolic Compounds and Phenylalanine Ammonia-Lyase in Leaves of Phyllanthus tenellus Roxb. and their Induction by Copper Sulphate LAURA JANE M. SANTIAGO* {, RICARDO P. LOURO { and DULCE E. DE OLIVEIRA } {Laborato ´rio de Biotecnologia, Centro de Biocieˆncias e Biotecnologia, Centro de Biocieˆncias e Biotecnologia, Universidade Estadual do Norte Fluminense, Av. Alberto Lamego 2000, Horto, Campos dos Goytacazes, Rio de Janeiro, CEP 28015-620, Brazil, {Laborato ´rio de Ultraestrutura Vegetal, Departamento de Bota ˆnica, Instituto de Biologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro, Brazil and }Laborato ´rio de Gene´tica Molecular Vegetal, Departamento de Gene´tica, Instituto de Biologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro, Brazil Received: 9 May 2000 Returned for revision: 9 June 2000 Accepted: 29 July 2000 The compartmentation of phenolic compounds in mature leaves of Phyllanthus tenellus and their induction by copper sulphate were analysed at histological and subcellular levels. Light and electron microscopy studies demonstrated that the vacuoles of spongy cells were the main sites of phenolic accumulation. Spraying plants with copper sulphate induced punctated lesions formed by groups of necrotic cells which accumulated brownish substances. Histochemical tests and fluorescence microscopyanalysis of the sprayed leaves indicated that the phenolic compounds increased in spongy cells within the lesions. Ultrastructural analyses showed that 3 h after elicitation, the organelles of the cells within the lesion started to collapse and the content of phenolic substances increased in the vacuole of spongy cells. Antibody against phenylalanine ammonia-lyase (PAL) from parsley cross-reacted with the crude extract of P. tenellus leaves. Two isoforms, one of 65 kD and the other of 66 kD, were identified. Immunocytochemical studies showed that PAL was synthesized in the palisade and spongy cells, mainly in the cytoplasm and chloroplasts. The phytotoxicity of Cu 2 ions induced the accumulation of PAL in sub-cellular compartments of palisade cells. PAL accumulation started to increase 3 h after elicitation and reached a maximum after 6 h, decreasing 12 h post- induction. The increase of PAL was more evident in cells within the necrotic punctated regions than in surrounding cells. Since the vacuole of palisade cells did not accumulate phenolic compounds, the in situ studies suggested that the end products of PAL synthesis play a role in palisade cell wall reinforcement or might accumulate in other tissues. The symptoms induced by copper sulphate suggest that this abiotic elicitor may be a useful tool in the understanding of the regulation of biosynthetic phenolic pathways in P. tenellus. # 2000 Annals of Botany Company Key words: Cell death, copper sulphate, heavy metal, immunolabelling, phenolic compounds, phenylalanine ammonia-lyase, Phyllanthus, transmission electron microscopy, ultrastructure. INTRODUCTION Plant secondary metabolites are formed from glucose metabolism intermediated by the shikimic, acetate and aminoacid pathways (Geissman and Crout, 1969). A range of physiological and ecological functions have been reported for these natural products, such as hormone regulation, organogenesis, plant defence against biotic and abiotic agents, chemical signalling to guide pollinators or fruit dispersers and plant–microorganism symbiosis (Curir et al., 1990; van Tunen and Mol, 1991; Vogt et al., 1994; Turlings et al., 1995). The understanding and manipulation of plant secondary metabolite biosynthesis is a major challenge in plant physiology. These substances are chemically diverse with heterogeneous distribution in dierent taxonomic groups and dierent plant organs and tissues (Gottlieb, 1982). The regulation of the enzymes involved in their synthesis is influenced by plant develop- ment as well as by external factors (van Tunen and Mol, 1991; Eckey-Kaltembach et al., 1994). Biotic and abiotic stress activate complex defence mechanisms in plant cells, altering both primary and secondary metabolism in a coordinated fashion (Marques and Brodelius, 1988; Dalkin et al., 1990). Elicitors have been employed to induce the biosynthetic pathways of important secondary metabolites in order to elucidate the mechanisms that underlie the steps of their synthesis, distribution and accumulation (Marques and Brodelius, 1988; Aertis et al., 1994; Dornenburg and Knorr, 1995). The role of abiotic stress in plant cell organization and its relation to the induction of dierent secondary metabolites has been the subject of extensive investigations (Santos et al., 1993; Lummerzhein et al., 1995). However, little is known about the influence of abiotic elicitors on specific pathways of secondary metabolite biosynthesis. Phenolic compounds are aromatic secondary metabolites formed essentially via the shikimic and/or malonic path- ways (Geissman and Crout, 1969). Modifications in their basic structure such as oxidation, hydroxylation, glyco- sylation and methylation have led to a large range of phenolic substances with dierent biological functions (Gottlieb, 1982; van Tunen and Mol, 1991; Nicholson Annals of Botany 86: 1023–1032, 2000 doi:10.1006/anbo.2000.1271, available online at http://www.idealibrary.com on 0305-7364/00/111023+10 $35.00/00 # 2000 Annals of Botany Company * For correspondence. Fax 00 55 24 7263720, e-mail laura@cbb. uenf.br

Transcript of Compartmentation of Phenolic Compounds and Phenylalanine AmmoniaLyase in Leaves of Phyllanthus...

Annals of Botany 86: 1023±1032, 2000doi:10.1006/anbo.2000.1271, available online at http://www.idealibrary.com on

Compartmentation of Phenolic Compounds and Phenylalanine Ammonia-Lyase in Leavesof Phyllanthus tenellus Roxb. and their Induction by Copper Sulphate

LAURA JANE M. SANTIAGO*{, RICARDO P. LOURO{ and DULCE E. DE OLIVEIRA}

{LaboratoÂrio de Biotecnologia, Centro de BiocieÃncias e Biotecnologia, Centro de BiocieÃncias e Biotecnologia,Universidade Estadual do Norte Fluminense, Av. Alberto Lamego 2000, Horto, Campos dos Goytacazes, Rio deJaneiro, CEP 28015-620, Brazil, {LaboratoÂrio de Ultraestrutura Vegetal, Departamento de BotaÃnica, Instituto deBiologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro, Brazil and }LaboratoÂrio de GeneÂtica MolecularVegetal, Departamento de GeneÂtica, Instituto de Biologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro,

Brazil

Received: 9 May 2000 Returned for revision: 9 June 2000 Accepted: 29 July 2000

1991; Eckey

0305-7364/0

* For corruenf.br

The compartmentation of phenolic compounds in mature leaves of Phyllanthus tenellus and their induction by coppersulphate were analysed at histological and subcellular levels. Light and electron microscopy studies demonstrated thatthe vacuoles of spongy cells were the main sites of phenolic accumulation. Spraying plants with copper sulphateinduced punctated lesions formed by groups of necrotic cells which accumulated brownish substances. Histochemicaltests and ¯uorescence microscopy analysis of the sprayed leaves indicated that the phenolic compounds increased inspongy cells within the lesions. Ultrastructural analyses showed that 3 h after elicitation, the organelles of the cellswithin the lesion started to collapse and the content of phenolic substances increased in the vacuole of spongy cells.Antibody against phenylalanine ammonia-lyase (PAL) from parsley cross-reacted with the crude extract of P. tenellusleaves. Two isoforms, one of 65 kD and the other of 66 kD, were identi®ed. Immunocytochemical studies showedthat PAL was synthesized in the palisade and spongy cells, mainly in the cytoplasm and chloroplasts. Thephytotoxicity of Cu2� ions induced the accumulation of PAL in sub-cellular compartments of palisade cells. PALaccumulation started to increase 3 h after elicitation and reached a maximum after 6 h, decreasing 12 h post-induction. The increase of PAL was more evident in cells within the necrotic punctated regions than in surroundingcells. Since the vacuole of palisade cells did not accumulate phenolic compounds, the in situ studies suggested that theend products of PAL synthesis play a role in palisade cell wall reinforcement or might accumulate in other tissues. Thesymptoms induced by copper sulphate suggest that this abiotic elicitor may be a useful tool in the understanding ofthe regulation of biosynthetic phenolic pathways in P. tenellus. # 2000 Annals of Botany Company

Key words: Cell death, copper sulphate, heavy metal, immunolabelling, phenolic compounds, phenylalanineammonia-lyase, Phyllanthus, transmission electron microscopy, ultrastructure.

INTRODUCTION

Plant secondary metabolites are formed from glucosemetabolism intermediated by the shikimic, acetate andaminoacid pathways (Geissman and Crout, 1969). A rangeof physiological and ecological functions have beenreported for these natural products, such as hormoneregulation, organogenesis, plant defence against biotic andabiotic agents, chemical signalling to guide pollinators orfruit dispersers and plant±microorganism symbiosis (Curiret al., 1990; van Tunen and Mol, 1991; Vogt et al., 1994;Turlings et al., 1995). The understanding and manipulationof plant secondary metabolite biosynthesis is a majorchallenge in plant physiology. These substances arechemically diverse with heterogeneous distribution indi�erent taxonomic groups and di�erent plant organs andtissues (Gottlieb, 1982). The regulation of the enzymesinvolved in their synthesis is in¯uenced by plant develop-ment as well as by external factors (van Tunen and Mol,

-Kaltembach et al., 1994).

0/111023+10 $35.00/00

espondence. Fax 00 55 24 7263720, e-mail laura@cbb.

Biotic and abiotic stress activate complex defencemechanisms in plant cells, altering both primary andsecondary metabolism in a coordinated fashion (Marquesand Brodelius, 1988; Dalkin et al., 1990). Elicitors havebeen employed to induce the biosynthetic pathways ofimportant secondary metabolites in order to elucidate themechanisms that underlie the steps of their synthesis,distribution and accumulation (Marques and Brodelius,1988; Aertis et al., 1994; Dornenburg and Knorr, 1995).The role of abiotic stress in plant cell organization and itsrelation to the induction of di�erent secondary metaboliteshas been the subject of extensive investigations (Santoset al., 1993; Lummerzhein et al., 1995). However, little isknown about the in¯uence of abiotic elicitors on speci®cpathways of secondary metabolite biosynthesis.

Phenolic compounds are aromatic secondary metabolitesformed essentially via the shikimic and/or malonic path-ways (Geissman and Crout, 1969). Modi®cations in theirbasic structure such as oxidation, hydroxylation, glyco-sylation and methylation have led to a large range ofphenolic substances with di�erent biological functions

(Gottlieb, 1982; van Tunen and Mol, 1991; Nicholson

# 2000 Annals of Botany Company

ley PAL.

collected from di�erent plants.

¯uorescent compounds.

o

and Hammerschmidt, 1992). The rigidi®cation of the cellwall by lignin is both an e�ective adaptation to the terres-trial environment and a�ords protection against invasion ofphytopathogens (Gottlieb, 1982; Halhbrock and Schell,1989; Nicholson and Hammerschmidt, 1992). The acti-vation of the Rhizobium nod genes involved in root nodula-tion is mediated by ¯avonoids such as 7,4-dihydroxy¯avone(Coronado et al., 1995) and iso¯avonoids may act as signalmolecules during plant±mycorrhiza interaction (Paiva et al.,1994). The speci®c location of anthocyanins in the plantepidermal layer may protect internal cell layers against UV-B radiation (Braun and Tevini, 1993) and an increase infuranocoumarins leads to plant protection against highlevels of ozone (Eckey-Kaltenbach et al., 1994). Diverseantimicrobial phenolics such as daidzein, genistein andpsoralen are synthesized and accumulated during phyto-pathogen invasion (Graham, 1991; Nicholson and Ham-merschmidt, 1992). Also the regulation of polar auxintransport is considered to be modulated by ¯avonoids(Jacobs and Rubery, 1988).

Besides their importance in plant biology, many second-ary metabolites have been employed in human phytother-apy. Phenolic compounds synthesized by Phyllanthus L.species are potent antineoplasic agents and inhibitors of theDNA polymerase of the hepatitis B virus (Venkateswaranet al., 1987; Blumberg et al., 1989). The phenolic com-pounds of Phyllanthus emblica are inhibitors of immuno-de®ciency virus replication, with only a few side e�ects(Pettit et al., 1990; El-Mekkawy et al., 1995). Also, metha-nolic extracts of some species have been shown to be potentantiophidic and analgesic agents (Kuster et al., 1994;Santos et al., 1994; Calixto et al., 1997).

The ®rst reaction in the phenylpropanoid pathway iscatalysed by phenylalanine ammonia-lyase (PAL; EC4.3.1.5.) converting L-phenylalanine to trans-cinnamic acid(Hanson and Havir, 1981). It has been shown that de novosynthesis of PAL isoforms is induced by biotic and abioticelicitors and that the di�erential expression of PAL genesleads to the synthesis and accumulation of PAL isoformsand phenolic compounds in di�erent tissue and subcellularcompartments (Jahnen and Hahlbrock, 1988; Schmelzeret al., 1988).

Structural and immunolocalization studies of normal andstressed plants have identi®ed the main sites of synthesisand accumulation of biosynthetic enzymes (Karwatzki et al.,1993; Duke et al., 1994). Furthermore, temporal and spatialstudies into the synthesis and induction of phenoliccompounds and their biosynthetic enzymes have helped inthe understanding of the regulation and distribution of thesteps of their metabolic pathways. With this purpose inmind we used heavy metals as abiotic elicitors to inducephenolic compounds in Phyllanthus tenellus Roxb., anannual herb known in Brazilian folk medicine as ervapombinha or quebra-pedra (stone-breaker). According toPio-Correà a (1974), P. tenellus plants have been used inkidney disease as a diuretic and to dissolve renal stones.Calixto et al. (1998) also proposed that the phenoliccompounds of these plants have antinociceptive properties.Heavy metals are chemically better de®ned than biotic

1024 Santiago et al.ÐCompartmentation

elicitors, and can activate the phenylpropanoid pathway

(Kessmann et al., 1990; Parry et al., 1994). Among theelicitors tested, spraying with copper sulphate led to theformation of microlesions and the synthesis of phytoalexinsin punctated regions, a type of hypersensitive reaction (HR)symptom induced by pathogen attack.

In the present investigation, in situ studies were employedto localize, at the histological and subcellular level, the sitesof synthesis and accumulation of phenolic compounds inmature leaves of P. tenellus induced by the abiotic elicitorcopper sulphate. To elucidate further the earlier steps ofregulation of phenolic biosynthesis, compartmentation ofphenylalanine ammonia-lysase (PAL) was evaluated byimmunocytochemical assays using antibodies against pars-

f Phenolics and PAL in Phyllanthus

MATERIALS AND METHODS

Biological material

Plants of Phyllanthus tenellus were grown in a greenhouse at358C. Fifty to 60-d-old plants were sprayed with anaqueous solution of 0.5 M copper sulphate and 0.05% (v/v) Tween-20, and 1.5 cm long leaves were collected at 0, 0.5,1.5, 3, 6 and 12 h for further analysis. Control plants weretreated with 0.05% (v/v) Tween-20 in sterile distilled waterand the leaves were collected at the same time points. Formicroscopy analyses, the experiments were performed ®vetimes using about 30 sections of ®ve leaves randomly

Light and ¯uorescence microscopy

Light microscopy studies were performed on frozen20 mm thick cross-sections cut with a Micron cryostat(Walldors, Germany). To analyse phenolic compounds,samples were treated with alcoholic FeCl3 (Johansen, 1940).The leaf surface and the frozen cross-sections were analysedusing a Zeiss Axioplan epi¯uorescence microscope (GoÈ ttin-gen, Germany) equipped with a 480 nm ®lter to detect

Electron microscopy

For ultrastructural analysis, tissue was ®xed for 2 h atroom temperature, with 2.5% glutaraldehyde (v/v) and 4%paraformaldehyde (w/v) in 0.05 M sodium cacodylate bu�er(pH 7.3). Samples were post®xed for 1 h with 1% (w/v)osmium tetroxide in sodium cacodylate bu�er, dehydratedin a graded acetone series and embedded in Spurr's resin(Spurr, 1969). Ultrathin sections (80 nm) were cut with adiamond knife on a Reichert Ultracut S microtome(Vienna, Austria) and post-stained with 1% uranyl acetate(w/v) in absolute ethanol and lead citrate (Reynolds, 1963).

For the immunocytochemical assays, leaf samples were®xed with 0.2% glutaraldehyde (v/v) and 4% (w/v)paraformaldehyde in the same bu�er, dehydrated in agraded ethanol series and embedded in LRWhite resin(Polysciences, Warrington, PA, USA) at room temperature.

The in®ltrated samples were embedded in gelatine capsules,

o

and polymerized for 2 d at 378C. Ultrathin sections were

Santiago et al.ÐCompartmentation

collected on nickel grids.

(Sigma, St. Louis, MO, USA).

Antibody labelling

For immunogold labelling, nickel grids containingultrathin sections were incubated in a blocking solution of1% (w/v) bovine serum albumin (Sigma, St. Louis, MO,USA) in PBST [10 mM sodium phosphate bu�er, pH 7.2(Sigma, MO, St. Louis, USA), 500 mM NaCl and 0.1%Tween-20] for 20 min. After blocking, the samples wereincubated for 3 h with the anti-PAL antiserum from parsley(Petroselium crispum) diluted 1 : 200 in PBST. This anti-body was donated by Dr Klaus Hahlbrock (Max-Plank-Institut fuÈ r Zuchtungsforschung, KoÈ ln). The material wasthen washed in PBST for 30 min ( four times), andincubated in a solution of secondary anti-rabbit IgG anti-body conjugated with 10 nm gold particles (E.Y. Labs. Inc.,San Mateo, USA) diluted 1 : 100. Excess secondaryantibody was removed by rinsing with PBST, followed bydistilled water. After immunolabelling, sections werestained with 2% (w/v) aqueous uranyl acetate for 20 minand with lead citrate (Reynolds, 1963) for 3 min. All stepswere carried out at room temperature. For controls, theprimary antibody was omitted. Material was observed witha Zeiss 900 transmission electron microscope (Oberkochen,Germany). The number of gold particles on palisade cellswas evaluated from the 30 cells of ®ve leaves from ®ve

experiments.

abundant.

Protein extraction

Frozen mature leaves were powdered in liquid N2 using amortar and pestle and suspended in extraction bu�er with0.0625 M Tris±HCl pH 6.8, 100 mM DTT and 2% SDS.After removal of cell debris by centrifugation (15 000 g,10 min, 48C) proteins were precipitated in 5 vol of acetoneat 208C for 2 h and resuspended in the same bu�er. Totalprotein content was determined with a bicinchroninic acid

protein assay kit (Sigma, St. Louis, MO, USA).

Electrophoresis and Western blotting

For electrophoretic analyses, loading bu�er containing100 mM Tris-HCl pH 6.8, 4% SDS, 20% (v/v) glycerol,0.004% bromophenol blue and 200 mM DTT was added to80 mg proteins and heated at 1008C for 4 min. Proteins wereseparated by SDS/PAGE (Laemmli, 1970) with a 4%stacking gel and 12.5% running gel and electroblotted to anitrocellulose membrane in 50 mM Tris and 50 mM boricacid bu�er pH 8.8 at a constant 25 V for 16 h. Detection oftotal protein on the membrane was by Ponceau-S staining(0.2% (w/v) Ponceau-S in 3% trichloracetic acid) anddestaining with distilled water. The membrane was thenincubated in 5% powdered milk in PBS pH 7.4, washed inPBST for 10 min, and incubated for 4 h in PBSTA (PBS,0.5% (v/v) Tween-20, 1% (w/v) BSA) with the antibodyagainst PAL diluted 1 : 500. Membranes were then washedin PBST for 10 min, incubated for 2 h in PSTA with the

secondary antibody conjugated with alkaline phosphatase

(Sigma, St. Louis, MO, USA) diluted 1 : 5000, and rinsedagain with PBST. The antibody-protein complex wasdeveloped with the Alkaline Phosfatase Western Kit

f Phenolics and PAL in Phyllanthus 1025

RESULTS

Leaf anatomy and ultrastructure

The leaves of Phyllanthus tenellus are glabrous anddorsiventral, formed by one epidermal layer and mesophyllconsisting of one layer of palisade cells and two layers ofspongy cells. Histochemical assays with FeCl3 on transversesections of the leaf blade demonstrated that phenolic com-pounds accumulated in isolated or in clustered, randomlydispersed spongy cells. These cells were similar in size andshape to the other cells of spongy tissue.

Ultrastructural analysis showed that palisade cells haddense cytoplasm, a small vacuole, numerous mitochondriaand chloroplasts with large starch grains, and smallplastoglobules (Fig. 1). The spongy cells develop a densecytoplasm and a large and central vacuole most of whichmay accumulate electronopaque deposits characteristic ofphenolic compounds (Figs 2±4). The chloroplasts accumu-late fewer and smaller starch grains than those observed inthe chloroplasts of palisade cells (Fig. 2). The concentrationof electronopaque substances is heterogeneous in di�erentcells. Isolated or clustered cells may not accumulate thesesubstances (Fig. 2), but phenolic compounds were observedat low (Fig. 3) or high concentration (Fig. 4) in other cells.In the latter case, the stored material had a granularappearance. Spongy cells with or without phenolic sub-stances were ultrastructurally similar. Both cells types wererandomly distributed, however the ®rst cell type was more

Changes promoted by Cu2� ions

Between 1.5±2 h after spraying with copper sulphate,brown lesions appeared on the leaf surfaces. The colour ofthe lesions turned darker after 3±4 h of elicitation (Fig. 5).Light microscopy analyses of the leaf surface showed thatthe cells localized within the lesion were depressed.However, scanning and transmission electron microscopyrevealed that the wax deposits and stoma structure were notaltered (data not shown). Light microscopy of cross-sections showed that the spongy cells accumulated brown-ish substances (Fig. 6). Fluorescence microscopy of the leafsurface and transverse sections showed an accumulation ofyellow-green auto¯uorescent substances, thought to bephytoalexins, mainly in the cells in the necrotic region.The auto¯uorescent substances were observed 3±4 h afterelicitation, reaching a maximum at 12 h (Fig. 7). Histo-chemical staining of transverse sections of the leaf bladewith FeCl3 showed that these substances corresponded tophenolic compounds. The increase of these substances wasobserved only in the spongy cells within the lesion (Fig. 8).

Three hours after spraying with copper sulphate, theorganelles of the palisade cells within the lesion started

to collapse (Fig. 9). A gradual increase of phenolic

1 2

3 4

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PG

SG

SG

SG

SG

CL

CL CL

M

MSG

SG

PG

SG

SG

PG

CL

SG

CL

PG

V

PC

EP

SP

PP

EP

1026 Santiago et al.ÐCompartmentation of Phenolics and PAL in Phyllanthus

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of Phenolics and PAL in Phyllanthus 1027

compounds was observed in the vacuole of all the spongycells within the lesion. In earlier stages of elicitation, thesephenolic contents showed a granular aspect similar to thatobserved in the cells with the largest content of phenolicsubstances. Six hours after spraying, most of the organellesin the protoplasts of palisade and spongy cells hadcollapsed, although some chloroplasts were still preserved.The phenolic compounds gradually occupied the wholevacuole (Fig. 10). After 12 h of elicitation, the protoplasmand the organelles of all palisade cells within the necroticregion had collapsed fully (Fig. 11), and the spongy cellswere ®lled with higher concentrations of phenolic com-pounds (Fig. 12). Both events resulted in localized celldeath. Despite the structural changes in the cells within thelesions, the cellular organization of the tissues outside the

Santiago et al.ÐCompartmentation

lesion was preserved.

8

PP

EP

SP

EP

FIG. 7. Cross-section of a leaf blade 6 h after elicitation showingthe accumulation of auto¯uorescent substances in spongy cells.

Bar � 20 mm.FIG. 8. Histochemical test with ferric chloride showing the accumu-lation of phenolic compounds in spongy cells (arrows). Bar � 10 mm.

Immunocytochemical analysis

To better understand the metabolic compartmentation ofphenolic biosynthesis in P. tenellus the primary sites ofphenolic biosynthesis were also investigated. The antiserumagainst PAL from parsley cross-reacted with two isoforms,one of 65 kD and the other 66 kD, in the crude extract ofcontrol and elicited P. tenellus plants (Fig. 13). Immuno-cytochemical analysis showed that PAL was synthesized inthe palisade and spongy cells. The ®xation techniques usedin the experiments did not allow the preservation oforganelles in the epidermal cells. At the subcellular level,clusters of gold particles were distributed throughout thecytoplasm and more abundantly in the chloroplasts ofpalisade (Fig. 14) and spongy cells. Because of the largervolume occupied by the vacuole in spongy cells, onlypalisade cells were used for quantitative analysis. PALaccumulation started to increase 3 h after spraying withCu2� ions in these cells. The increase in immunolabellingoccurred in palisade cells outside (Fig. 15) and inside(Fig. 16) the lesion, being more signi®cant in the cellswithin the lesion, especially in the chloroplasts. Labellingwas maximal around 6 h post-induction (Fig. 17), decreas-ing after 12 h (Fig. 18). The stress induced by Cu2� ions didnot alter the compartmentation of the gold particles at the

histological and subcellular level.

DISCUSSION AND CONCLUSIONS

Plant secondary metabolites are compartmented atthe tissue and subcellular level and this distribution

and accumulation is regulated by environmental and

FIG. 1. Cross-section of control leaf showing palisade cell with dense cygrains (SG) and small plastog

FIG. 2. Cross-section of control leaf showing spongy cells with chloroplasvacuole (V) without phenolic

FIG. 3. Cross-section of control leaf showing spongy cells withFIG. 4. Cross-section of control leaf showing spongy cells with a high

Bar � 2.

FIG. 5. Surface view of a leaf blade showingFIG. 6. Cross-section of a leaf blade 6 h after elicitation showing the a

accumulate brown substances (arrows). Bar � 20 mm. EP, Epi

developmental cues. Histochemical assays demonstratedthat in mature leaves of P. tenellus the spongy cells are themain source of phenolic compounds and that thesesubstances accumulated in randomly located cells. At theultrastructural level, there was no di�erence betweenspongy cells that did or did not accumulate phenolicsubstances. A great number of such phenolic substances aresynthesized by Phyllanthus species (Calixto et al., 1998).The phenolic substances accumulated in spongy cells ofP. tenellus are currently under investigation in our

laboratory.

toplasm, mitochondria (M), chloroplasts (CL) with numerous starchlobules (PG). Bar � 2 mm.ts accumulating a few starch grains and small plastoglobules as well as acompounds. Bar � 2 mm.low concentration of phenolic compounds (PC). Bar � 5 mm.er concentration of phenolic substances with a granular appearance.5 mm.lesions 6 h after elicitation. Bar � 1.5 mm.reas inside and outside the lesion. Inside the lesion, the spongy cellsdermis; PP, palisade parenchyma; SP, spongy parenchyma.

9 10

11 12

PC

PC

SP

PPEP

EP

PPSP

SGSG

PC

SG

SGSG

SG

CL

PG

MSG

SG

SGSG

SG

CL PG

M CL

SGSG

CL

PP

SP

SG

PC

SG

FIG. 9. Cross-section of a leaf blade 3 h after elicitation, showing the beginning of the collapse of organelles in palisade cells. Bar � 2 mm.FIG. 10. Cross-section of a leaf blade 6 h after elicitation, showing the collapse of the organelles in palisade and spongy cells as well as the increase

in phenolic compounds. Bar � 5 mm.FIG. 11. Cross-section of a leaf blade 12 h after elicitation, showing collapsed parenchyma cells and the highest concentration of phenolic

compounds in spongy cells. Bar � 5 mm.FIG. 12. View of organelles in totally collapsed palisade and spongy cells, and spongy cells with high concentrations of phenolic substances, 12 h

after elicitation. Bar � 5 mm.

1028 Santiago et al.ÐCompartmentation of Phenolics and PAL in Phyllanthus

kD

6665

FIG. 13. Western immunoblot analysis showing the cross-reaction ofanti-PAL parsley antibody with P. tenellus crude extract.

Santiago et al.ÐCompartmentation o

The crude extract of P. tenellus leaves cross-reacted withanti-PAL from parsley, and two isoforms of 65 and 66 kDwere identi®ed. The cytoplasm and chloroplasts ofpalisade and spongy cells were the main sites of PALsynthesis. Previous studies reported the occurrence of PALisoforms in epidermal cells of Petroselium crispumleaves (Jahnen and Hahlbrock, 1988) and in parenchy-matic cells adjacent to the xylem of Phaseolus vulgarishypocotyl (Smith et al., 1994). In the current study,the di�erent ®xation method did not preserve theP. tenellus epidermal tissue and the parenchymatic cellsof the xylem were not analysed. The synchronousaccumulation of both PAL and phenolic substances,observed in spongy cells of P. tenellus, was also observedin epidermal tissue of parsley leaves (Schmelzer et al.,1988; Neumann et al., 1991). However, this occurrencemay not be totally correlated, since in P. tenellus, palisadecells and some spongy cells accumulating PAL did notstore phenolic substances. This led to the supposition thatPAL isoforms might have been synthesized, but remainedinactive in these cells, or if they were active, that they tookpart in the synthesis of precursors which would betransported to the cell wall and/or to other cells later, asproposed for UV-irradiated oat leaves (Knooge andWeissenbock, 1986). Previous work suggested that PALisoforms localized in palisade cells play a role in thesynthesis of anthocyanins and ¯avonol glycosides inepidermal Pisum sativum cells (Hrazdina et al., 1982).However, histochemical tests on fresh tissue of P. tenellusleaves indicated that phenolic substances are restricted tospongy cells.

The phytotoxicity of copper sulphate induced thesimultaneous increase of PAL and auto¯uorescent phenoliccompounds characteristic of phytoalexins (Dixon, 1986;

Nicholson and Hammerschmidt, 1992) in spongy cells,

producing necrotic lesions. It is known that tannins and¯avonoids are amongst the main phenolic substancesinduced in a plant's defence response to abiotic stress(van Tunen and Mol, 1991; Booker et al., 1996). Despitethis, high concentrations of these substances are toxic andlethal to the plant cell, leading to the occurrence ofmicrolesions (Dixon, 1986; Chessin and Zipf, 1990).

Microlesions, as well as the increase of PAL and phyto-alexins have also been shown in Arabidopsis leaves sprayedwith lead nitrate (Lummerzheim et al., 1995). However,the plant response to the phytotoxicity of heavy metalsseems to be heterogeneous since microlesions were alsoinduced in P. tenellus leaves after spraying with CdCl2 ,but not after spraying with 0.01±0.05% PbNO3 or HgCl2(data not shown). In contrast to Cu2� ions, these metalions promoted plant defoliation a few minutes afterelicitation. The di�erence in the e�ects of metal ions onplant cells remains to be explained, but it seems to berelated to their binding to di�erent membrane proteins(Woolhouse, 1983; Renwrantz et al., 1998; Zhang et al.,1999).

Both the increases of phenolic compounds andthe formation of punctated lesions in P. tenellus aresimilar to the hypersensitive response (HR) when localizedcell death occurs in response to pathogen infection(Collinge and Slusarenko, 1987; Baker and Orlandi,1995). Cytological studies have shown that cell death mayresult in necrotic or apoptotic cells during HR (Lamband Dixon, 1997).

The loss of compartmentation, also reported as one ofthe ®rst events in cell death induced by Cu2� ions (Meyerand Heath, 1988), and the synthesis of phytoalexins wererelated to the alteration in the plasma membrane(Atkinsons et al., 1990; Atkinsons, 1993). This may be aconsequence of the phytotoxicity of heavy metals, whichmay also induce oxidative stress in plants and activate theincrease of lipoxygenases involved in lipid peroxidation(Price et al., 1994; Gallego et al., 1996). The in¯uence ofCuSO4 on the generation of active oxygen species, such asH2O2 in plants has been suggested by Luna et al. (1994)and the HR is thought to be in¯uenced by H2O2production (Levine et al., 1994). The oxygenated fattyacids produced by the activity of peroxidases, phospho-lipases and lipoxygenases were considered endogenouselicitors induced during the plant defence responseassociated with phytoalexins (Kodama and Akatsuka,1991; Goodman and Novacky, 1994). This led to thesuggestion that the oxidative burst induced by bothpathogen attack and the in¯uence of metal ions mayactivate a common route during the signalling pathway ofcell death that leads to necrosis. Dypburkt et al. (1994)suggested that lower levels of active oxygen species lead toapoptosis, while severe oxidative stress may inducenecrosis.

According to our results, the palisade and spongytissues of P. tenellus are the main sites of the PAL enzyme,but phenolic compounds only accumulated in spongycells. Furthermore, it was demonstrated that Cu2� ionsinduced an increase in PAL in palisade cells while

f Phenolics and PAL in Phyllanthus 1029

phenolic compounds increased in spongy cells, giving

1514

1716

FIG. 14. Immunocytochemical analysis of PAL in the palisade cells of control leaves, showing labelling (arrows) mainly in the cytosol and in thechloroplasts. Bar � 0.5 mm.

FIG. 15. Immunolabelling of PAL in palisade cells 3 h after elicitation. The increase in labelling (arrows) outside the lesion was slight.Bar � 0.75 mm.

FIG. 16. Immunolabelling of PAL in palisade cells 3 h after elicitation. The increase in labelling (arrows) was higher inside the lesion, mostly inthe chloroplasts. Bar � 0.5 mm.

FIG. 17. Increased PAL accumulation (arrows) in chloroplasts of palisade cells inside the lesion 6 h after elicitation. Bar � 0.5 mm.

1030 Santiago et al.ÐCompartmentation of Phenolics and PAL in Phyllanthus

rise to necrotic punctate regions, leading to `HR-like'symptoms. This elicitor may be a useful tool in theunderstanding of the regulation of biosynthetic phe-nolic pathways in Phyllanthus tenellus and the diver-sity of plant defence responses against biotic and abiotic

stress.

ACKNOWLEDGEMENTS

The authors are very grateful to Dr Klaus Hahlbrock, Max-Plank-Institut fuÈ r Zuchtungsforschung, KoÈ ln, Germany,for supplying anti-PAL antiserum from parsley (Petro-

selium crispum). Financial support: Conselho Nacional

Control 3 h 6 h 12 h

60

50

40

30

20

10

0

Nu

mbe

r of

gol

d pa

rtic

les

per

µm2

outside lesioninside lesion

FIG. 18. Number of colloidal gold particles per mm2 (relating to theconcentration of PAL enzyme) in palisade cells of normal and inducedleaves (n � 30) of Phyllanthus tenellus using parsley anti-PAL antibody

Santiago et al.ÐCompartmentation o

de Desenvolvimento Cientõ ®co e Tecnolo gico (CNPq),FundacË aÄ o Estadual do Norte Fluminense (FENORTE)

diluted 1 : 200. The vertical bars indicate standard deviations.

and FundacË aÄ o Universita ria Jose Bonifa cio (FUJB).

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