Plant Physiol. (1979) 63, 142-145 0032-0089/79/63/0142/04/$00.50/0 Ethylene and Ethane Production from Sulfur Dioxide-injured Plants' Received for publication May 2, 1978 and in revised form July 14, 1978 GALEN D. PEISER AND SHANG FA YANG Department of Vegetable Crops, University of California, Davis, California 95616 ABSTRACT After alfalfa (Medicago sativa) seedlings were exposed to approximately 0.7 microliter per liter SO2 for 8 hours, elevated ethylene and ethane production was observed. Ethylene production peaked about 6 hours and returned to control levels by about 24 hours following the fumigation, while ethane production peaked about 36 hours and was still above control levels 48 hours after the fumigation. Light had an opposite effect upon the production of the two gases: ethane production rates were higher from plants held in light, whereas ethylene production rates were higher from those held in the dark. Peak ethylene and ethane production rates from SOs-treated plants were about 10 and 4 to 5 times greater, respectively, than those of the control plants. Ethylene appeared to be formed primarily from stressed yet viable leaves and ethane from visibly damaged leaves. The different time courses and light requirements for ethylene and ethane production suggest that these two gases were formed via different mechanisms. Light appears to have a dual role. It enhances S02-induced cellular damage and plays a role for repairs. Ethylene is produced from plants under normal conditions in relatively low amounts, but when plants are perturbed or injured, elevated ethylene production rates usually occur (1, 23). Stressinduced ethylene production has been reported to occur in plants exposed to air pollutants, such as ozone (5, 21) and SO2 (3, 4). Stress ethylene from ozone-injured plants reached a maximum within 2 to 4 hr, and returned to control levels by 24 hr after exposure to ozone (5, 21). Bressan et al. (3, 4) exposed leaf tissues of cucurbits to bisulfite solution or SO2 gas and found that ethylene production greatly increased in slightly injured leaves, but declined in severely injured leaves. Both ethylene and ethane can be produced from freeze-injured tissue (8). We have recently reported that both of these gases were produced in a chemical system consisting of linolenic acid hydroperoxide and bisulfite (15). In the present study we examined ethylene and ethane production from intact alfalfa plants exposed to SO2. of 160 1/hr. S02-air mixture was prepared and the flow rate was maintained by a capillary flowmeter (14). At this flow rate a considerable amount of S02 was absorbed by the plants as revealed by the drop in SO2 concentration after the plants were placed in the chambers. Typical S02 concentrations, determined at the exit chamber port immediately before and at 1 and 5 hr after the plants were placed in the chambers, were 1.5, 0.5 and 0.6 ,ul/l, respectively. Gas samples were collected in 2-liter Erlenmeyer flasks and S02 concentration was measured by the West-Gaeke method as modified by Scaringelli et al (18). The temperature and light intensity during the fumigation were the same as that at which the plants were grown. To determine the ethylene and ethane production rates, each pot of plants was enclosed periodically in a 1-liter glass chamber for 4 hr over a period both before and after the S02 fumigation. A 3-ml gas sample was withdrawn from each chamber at the beginning and end of each 4-hr period, and the gas concentrations were measured by gas chromatography employing an alumina column and a flame ionization detector. Between each 4-hr period the chambers were left open for 30 min and then reclosed for the next determination. The thiobarbituric acid assay for malonaldehyde was conducted according to Dillard and Tappel (6) with the exception that leaf samples were homogenized in 20%Yo (w/v) trichloroacetic acid, and aliquots of this crude homogenate were used in the assay. The content of thiobarbituric acid reactants (malonaldehyde) was calculated assuming that the molar absorptivity at 532 nm is 150,000 (16). RESULTS In preliminary experiments we observed that following the SO2 fumigation the production rate of ethylene was greater when plants were incubated in the dark, while the ethane production rate was greater in light. We have therefore examined the effect of light and dark on ethylene and ethane production by control and by fumigated plants. Figure 1 illustrates that both ethylene and ethane production rates increased following the SO2 fumigation. Although comparable pots of plants were fumigated in the same chamber, the plants subsequently incubated in the dark had about twice the rate of ethylene production as those incubated in continuous light (Fig. IA). For these same plants, ethane production (Fig. 1B) started earlier in light and more than twice the amount of ethane was produced in light than in darkness. In control plants, there was little difference between the rates of either ethylene or ethane production in light and dark. The important role of light in stimulating ethane production by the fumigated plants is further illustrated by the change in the ethane production rate when the plants were reversed with respect to the light-dark environment (as indicated by arrows in Fig. 1B). The dark-incubated plants transferred to light exhibited a greatly increased ethane production rate, while the light-incubated plants transferred to darkness showed a decreased production rate. Similar MATERIALS AND METHODS Alfalfa plants (Medicago sativa L.) were grown in Vermiculite in plastic pots, which were placed in a controlled temperature chamber maintained at 25 + 2 C. A 16-hr daylength, with an illuminance of about 300 ft-c, was provided by cool-white fluorescent lamps. Air was continuously renewed. When the plants were about 19 days old, two pots (15 plants per pot with a total shoot fresh weight of about 1.8 g) were fumigated with air (control) and two pots with air containing SO2 for about 8 hr, in a 9-liter cylindrical glass chamber, at a flow rate ' This work was supported by United States Public Health Service Grant ES 01045 and National Science Foundation Grant PCM 75-14444. 142 Downloaded from on June 16, 2017 - Published by www.plantphysiol.org Copyright © 1979 American Society of Plant Biologists. All rights reserved. Plant Physiol. Vol. 63, 1979 C2H4 AND C2H6 FROM SO2-INJURED PLANTS Ir 7 A l A 0. o 143 a-a ---- -- _- - CL -c z~~~ I w B z w8 -J . i~~~~~~~A . 4--- a I I A, 4 OS AA FsoA I \ \--, '<o__o0 I-- °0°-0-0- A -O, U6 10-O- C --O Z5 4 I. 3 2 A-. 0-2 A' 2-4 4-6 6-8 TIME (hrs) .4 8 16 24 8 16 TIME OF DAY (o'clock) FIG. 1. Increases in ethylene (A) and ethane (B) production by alfalfa plants following SO2 fumigation. Two pots of plants (A, A) were exposed to S02 for 7.5 hr and two pots ofcontrol plants (0, 0) were correspondingly exposed to air only. The SO2 concentration was 1.6, 0.6, and 0.8 pd/l at 0, 1, and 5 hr, respectively, during the fumigation. Fumigation began 2 hr after the beginning of light period and continued for 6 hr. At the end of the fumigation period, one S02-treated pot (A) and one control pot (0) were placed in continuous light, while the other SOrtreated pot (A) and control pot (0) were placed in the dark. Forty-five hr after fumigation, as indicated by arrow, the pot of SOrtreated plants kept in the dark (A) was transferred to light, and that in light (A) transferred to the dark. results were obtained when visibly damaged leaves excised from fumigated plants were incubated in dark or light (Fig. 2C). Leaves incubated in the light achieved ethane production rates three to six times greater than leaves incubated in the dark, and this effect was reversible by reversing the light-dark environment. When fumigated plants were exposed to continuous light, the ethylene production rate increased to a peak within 4 to 8 hr and then declined to the basal level within 16 to 20 hr following the fumigation period (Fig. IA). Similar results were observed in each of the four other experiments conducted, although there were slight variations in the time periods required for ethylene production to reach a maximum and subsequently to decline to the basal level, due to variation in exposure time and/or SO2 concentration. Following the fumigation period, plants incubated in the dark reached a peak ethylene production rate at about the same time (4-8 hr) as those in the light, but sustained this higher rate over a longer period and required 36 hr to decline to the basal level (Fig. IA). In comparison, the ethane production rate from plants in the dark peaked much later (24-36 hr after fumigation) and was sustained for a longer time than that for ethylene (Fig. 1B). When fumigated plants were exposed to continuous light, the high ethane production rate was maintained as long as the experiment was continued, about 48 hr after fumigation. FIG. 2. Ethane production rates by leaves detached from control plants (A), SOrtreated plants without visible damage (B), and SOrtreated plants with visible damage (C). Intact alfalfa plants were fumigated as described in Figure 1. Twenty-two hr after the S02 fumigation, at which time ethylene production rates from treated plants had returned to the basal level, leaves were detached and placed in vials with 1 ml of water and incubated in either light (0, A) or dark (0, A) for four consecutive 2-hr periods. At the end of the second 2-hr period, as indicated by arrow, leaves incubated in the light were transferred to the dark and those in the dark transferred to light. Under the conditions used for fumigation, some of the leaves exhibited visible damage (a water-soaked appearance) during the fumigation period. To determine which leaves were responsible for the ethane production, visibly and nonvisibly damaged leaves were excised from fumigated plants and their ethane production rates compared. This experiment was conducted when the ethane production rate was high, 22 to 32 hr after fumigation. The results demonstrate that visibly damaged leaves produced much more ethane (10 times, or more) than the nonvisibly damaged leaves from the same treated plants (Fig. 2). The nonvisibly damaged leaves produced only slightly more ethane than did the controls. By varying the length of the fumigation period in five experiments, with a total of 10 pots of treated plants, the percentage of visibly damaged leaves ranged from about 10 to 60%. Over this whole range, the ethane production rate increased as the number of leaves showing visible damage increased. This observation, together with the results obtained from excised leaves (Fig. 2), suggests that ethane production was closely related to visible damage. For the production of ethylene a similar relationship was observed only when fewer than 40 to 50%1o of the leaves had suffered visible damage; there was a decline in ethylene production rate as the visible damage increased to include more than half the number of leaves. Ethane is known to be produced during the peroxidation of linolenic acid (7, 17), and the level of thiobarbituric acid reactants (malonaldehyde) is known to serve as an index of lipid peroxidation. We have therefore compared ethane production rates with Downloaded from on June 16, 2017 - Published by www.plantphysiol.org Copyright © 1979 American Society of Plant Biologists. All rights reserved. 144 Plant Physiol. Vol. 63, 1979 PEISER AND YANG the level of thiobarbituric acid reactants in the control leaves and in fumigated leaves which were visibly or not visibly damaged. The results (Fig. 2 and Table I) indicate that both the ethane production rate and the level of thiobarbituric acid reactants were highest in leaves showing damage caused by SO2 fumigation. Following the fumigation, the condition and number of leaves showing visible damage were influenced both by the light-dark environment during incubation and by the duration of incubation. When scored visually for discoloration and desiccation 1 day after fumigation, leaves from light-incubated plants were much further deteriorated than those from the dark. Three days after the fumigation, more leaves from dark-incubated plants than from light-incubated plants showed visible damage. DISCUSSION The results indicate that the production rates of both ethylene and ethane increased after exposure of alfalfa plants to SO2 (Fig. 1). Since both gases were produced, the possibility exists that they could have been formed by the same mechanism. In chemical systems both ethylene and ethane can be produced from linolenic acid hydroperoxide (7, 17). However, the kinetics and the influence of light for ethylene and ethane production in the present system were quite different (Fig. 1), suggesting that the two gases were not produced by the same mechanism. It is generally thought that methionine is the precursor of both stress- and normally produced ethylene (1, 2, 10, 11, 23) while ethane is produced from peroxidized linolenic acid (7, 13, 17). Wilson et aL (22) reported that a rhizobitoxin analog, an inhibitor of ethylene synthesis from methionine, partially inhibited the emission of ethylene but not the emission of ethane from leaf tissues of cucurbits exposed to bisulfite solution. These observations are consistent with the view that the two gases are produced largely by the different pathways. These results do not exclude the possibility that some ethylene may arise from peroxidized linolenic acid especially in those tissues which are badly injured in light and produce large amounts of ethane. The extent of the stress or damage that tissues experience appears to determine whether they will produce ethylene or ethane. Elstner and Konze (8), working with point frozen leaf discs, observed that ethane production increased linearly as the frozen area increased from 0 to 100%1o; in contrast, ethylene production increased as the amount of frozen tissue increased from 0 to 40%, but declined as the area frozen increased beyond 50%o. They concluded that ethylene was produced from stressed yet viable tissue, while ethane was produced from decompartmented (killed) cells. Our results are consistent with this conclusion. Ethane was produced primarily from visibly damaged leaves (Fig. 2) after they were in a deteriorated condition, as indicated by their low respiration rate compared to the control rate (Table I). In the present system light was found to inhibit stress ethylene Table I. Respiration rates and malonaldehyde levels in excised leaves in relation to different degrees of SO2 injury. The excised leaves were prepared as described in Figure 2. Respiration rates were determined as CO2 production during each 2-hr period from detached leaves incubated in the dark. The values are averages from 4 incubation periods. Malonaldehyde was assayed witn thiobarbituric acid reagent after homogenization of the leaf samples at the end of the incubation period. C02 production wl/g fresh wt-hr Malonaldehyde tmol/g fresh wt Control leaves 242 ± 38 145 ± 31 Treated leaves with no visible injury 352 ± 51 188 ± 33 Treated leaves with visible injury 103 t 15 292 38 production but to stimulate ethane production from injured tissue. Tingey et al. (21) found that plants exposed to ozone produced more ethylene when they were incubated in the dark than in the light. In the excised leaf tissues of cucurbits exposed to bisulfite solution, Wilson et al. (22) reported that light enhanced both ethane and ethylene production. The causes of such variations are not clear. Ethane is thought to be produced from peroxidized linolenic acid via a free radical mechanism (7, 13, 17). Both higher amounts of thiobarbituric acid reactants and a greater production of ethane occurred in those leaves which were visibly damaged than in either nonstressed controls or in leaves which were treated but not visibly damaged (Table I). These results are in parallel with the notion that ethane could have resulted from the peroxidation of lipids. It is to be noted that during the aerobic oxidation of bisulfite in vitro, linolenic acid is cooxidized to linolenic acid hydroperoxide via a free radical mechanism (M. C. Lizada and S. F. Yang, unpublished results). Such a free radical-mediated oxidation of bisulfite can be initiated in vitro photochemically by Chl (9, 15) and result in Chl destruction (15). These observations lead to the speculation that SO2 absorbed by leaves may undergo oxidation and generate radicals which in turn may cause tissue damage, lipid peroxidation, ethane production and Chl destruction. In addition to the regulation of stomata opening by light, and the consequent SO2 absorption during exposure to SO2, light may also accelerate the radical-mediated oxidation of dissolved S02/bisulflte, and accentuate injury and ethane formation. We observed, 1 day after fumigation, that visibly damaged leaves deteriorated more rapidly when incubated in the light than in the dark. Three days after fumigation, there were more visibly damaged leaves on plants incubated in the dark than on plants incubated in light. This leads us to speculate that light must also play a role in a repair mechanism. Recovery from free radical damage and prevention of damage by free radicals are known to involve thiol compounds (20), such as GSH. Light-dependent reduction of oxidized glutathione in chloroplast is well known (12, 19). The concentration of GSH in chloroplast would increase during illumination. Light appears to have a dual though counteractive role: it enhances cellular damage by accelerating the radical-mediated oxidation of S02/bisulfite, but it also plays an important role in providing necessary metabolites for repair or recovery. The relative contribution of these two counteractive mechanisms will thus be influenced by the level of S02/bisulfite in the tissues. Further investigation is needed to test this hypothesis. LITERATURE CITED 1. ABELES FB 1973 Ethylene in Plant Biology. Academic Press, New York 2. ABELES AL, FB ABELES 1972 Biochemical pathway of stress-induced ethylene. Plant Physiol 50: 496-498 3. BRESSAN RA, LG WILSON, P FILNER 1978 Mechanisms of resistance to sulfur dioxide in the Curcurbitaceae. Plant Physiol 61: 761-767 4. BRESSAN RA, LG WILSON, L LECURaUX, P FILNER 1978 Use of ethylene and ethane emission to assay injury by S02. Plant Physiol 61: S-59 5. CRAKER L 1971 Ethylene production from ozone injured plants. Environ Poliut 1: 299-304 6. DILLARD CJ, AL TAPPEL 1971 Fluorescent products of lipid peroxidation of mitochondria and microsomes. Lipids 6: 715-721 7. DUMELIN EE, AL TAPPEL 1977 Hydrocarbon gases produced during in viero peroxidation of polyunsaturated fatty acids and decomposition of preformed hydroperoxides. Lipids 12: 894900 8. ELSTNER EF, JR KONZE 1976 Effect of point freezing on ethylene and ethane production by sugar beet leaf disks. Nature 263: 351-352 9. FRIDOVICH I, P HANDLER 1960 Detection of free radicals m illuminated dye solutions by the initiation of sulfite oxidation. J Biol Chem 235: 1835-1838 10. HANSON AD, H KENDE 1976 Biosynthesis of wound ethylene in morning-glory flower tissue. Plant Physiol 57: 538-541 11. HYODO H 1977 Ethylene production by albedo tissue of Satsuma mandarin (Citrus unshiu Marc.) fruit. Plant Physiol 59: 111-113 12. JABLONSIc PP, JW ANDERSON 1978 Light-dependent reduction of oxidized glutathione by ruptured chloroplasts. Plant Physiol 61: 221-225 13. JOHN WW, RW CURTIS 1977 Isolation and identification of the precursor of ethane in Phaseolus vulgaris L. Plant Physiol 59: 521-522 Downloaded from on June 16, 2017 - Published by www.plantphysiol.org Copyright © 1979 American Society of Plant Biologists. All rights reserved. Plant Physiol. Vol. 63, 1979 C2H4 AND C2H6 FROM S02-INJURED PLANTS 14. NELSON GO 1972 Controlled test atmospheres. Ann Arbor Science Publishers Inc, Ann Arbor, Michigan 15. PElSER GD, SF YANG 1978 Chlorophyll destruction in the presence of bisulfite and linoleic acid hydroperoxide. Phytochemistry 17: 79-84 16. PLACER ZA, LL CUSHMAN, BC JOHNSON 1966 Estimation of product of lipid peroxidation (malonyl dialdehyde) in biochemical systems. Anal Biochem 16: 359-364 17. RiELY CA, G COHEN, M LIEBERMAN 1974 Ethane evolution: a new index of lipid peroxidation. Science 183: 208-210 18. SCARINGELLI FP, BE SALTZMAN, SA FRE~Y 1967 Spectrophotometric determination of atmospheric sulfur dioxide. Anal Chem 39: 1709-1719 19. SCHAEDLE M, JA BASSHAM 1977 Chloroplast glutathionine reductase. Plant Physiol 59: 145 1011-1012 20. SLATER TF 1972 Free Radical Mechanisms in Tissue Injury. Pion Limited, London, pp 50-52 21. TINGEY DT, C STANDLEY, RW FIELD 1976 Stress ethylene evolution: a measure of ozone effects on plants. Atmos Environ 10: 969-974 22. WILSON LG, RA BRESSAN, L LECUREUX, P FILNuE 1978 Bisulfite-induced ethylene and ethane production: dependence on light and photosynthetically competent tissue. Plant Physiol 61: S-509 23. YANG SF, HK PRATT 1978 The physiology of ethylene in wounded plant tissues. In G KahlI ed, Biochemistry of Wounded Plant Storage Tissues. de Gruyter Company, Berlin, pp 595-622 Downloaded from on June 16, 2017 - Published by www.plantphysiol.org Copyright © 1979 American Society of Plant Biologists. All rights reserved.
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