Physiol. Plant. 47: 223-228. 1979 223 Effects of Sulphur Dioxide on Sugar and Free Amino Acid Content of Pine Seedlings By S. S. MALHOTRA and S. K. SARKAR' Northern Forest Research Centre, Canadian Forestry Service, Fisheries and Environment Canada, 5320 — 122 Street, Edmonton, Alberta T6H 3S5 Canada (Received 5 March, 1979; revised 25 June, 1979) detection of air pollution injury to vegetation prior to visual Treatment of jack pine (Pinus banksiana Lamb.) seedlings with symptom development of S 0 2 phytotoxicity. It has been suggested that S 0 2 causes a reduction in plant gaseous SO, resulted in a shift between the reducing and nonreducing sugars. Increasing concentrations of gaseous S0 2 caused photosynthesis (Ziegler 1973); such a change may cause a an increase in reducing sugars and a decline in the non-reducing reduction in the formation of serine (Tanaka et al. 1972). sugars, suggesting a conversion from the latter to the former at high Sulphur dioxide has also been shown to affect glutamic acid S0 2 concentrations. The total amino acid content of the intact and glutamine content of pea seedlings (Jager and Pahlich tissues also increased with increasing concentrations of gaseous 1972) and asparagine, glutamine, glutamic acid, serine, S0 2 . Gas-liquid chromatographic analyses of the amino acids glycine, alanine, arginine, ornithine, and proline content of indicated that S0 2 (1.34 mg • m~3 for 96 h) resulted in an increase in spruce needles (Jager and Grill 1975). However, the the content of alanine, valine, glycine, isoleucine, leucine, threonine, information available on the effect of S0 2 on different aspartic acid tyrosine, lysine, and arginine, and a decrease in the content of serine and glutamic acid. The enzymatic and other impli- families of free amino acids is still quite scanty. The present study was carried out to determine whether different concencations of such changes are discussed. trations of gaseous S 0 2 (under controlled conditions) have any effect on the level of pine needle metabolites such as free Introduction amino acids and sugars and to explore the possibility of The growth of plants is the direct result of physiological developing a biochemical technique for the detection of S0 2 and biochemical activities within the tissues. Environmental injury to vegetation prior to visual symptom development. factors such as temperature, moisture, nutrients, C 0 2 , and Abbreviation: PVP, polyvinyl pyrrolidone. light play an important role in determining the rate of metabolic activity. Air pollutants such as S 0 2 , released from certain industrial operations, can also affect plant metaMaterials and Methods bolism either temporarily or permanently depending upon the concentration and the length of exposure (Brandt and Growth conditions Heck 1968, Saunders and Wood 1973, Ziegler 1975, Jack pine (Pinus banksiana Lamb.) seeds were planted in Malhotra and Hocking 1976). the greenhouse as described previously (Malhotra 1976). It is generally believed that vegetation must exhibit visual Approximately 5- to 6-month-old seedlings were used as symptoms for S 0 2 injury to occur, but this may be misexperimental material. leading. Several controlled environmental studies have indicated that previsual disturbances such as changes in the ultrastructural organization (Malhotra 1976) and bioGaseous S02 treatment chemical functions (Malhotra 1977, Khan and Malhotra Initially an attempt was made to compare the biochemical 1977) brought about by S0 2 can affect the growth and yield effects of aqueous S0 2 on excised pine needle tissues with of vegetation (Bleasdale 1952, Tingey et al. 1971). It is therethose of gaseous S0 2 on intact needles. The excised needles fore of considerable importance to develop techniques for the were incubated in an aqueous medium with and without 1 Present address: Department of Food Science, University of dissolved S0 2 . The preliminary results indicated that during incubation, even in the S02-free aqueous medium, there was Alberta, Edmonton, Alberta, Canada. Abstract 0031-9317/79/120223-06 $03.00/0 © 1979 Physiologia Plantarum 224 S. S. MALHOTRA AND S. K. SARKAR a substantial leakage of low molecular weight compounds such as sugars out of the excised needles, it was therefore decided that studies on the effect of S0 2 on low molecular weight plant metabolites should use only gaseous SO, and intact tissues. Fumigations were carried out in small acrylic cuvettes using a continuous flow-through system. Flow rates for air and S0 2 were metered and controlled using rotameters and valves before the gases were mixed and introduced into the cuvettes. Further mixing within the cuvettes was achieved by internally mounted fans near the injection ports. The concentrations of S0 2 at the input and output were monitored by means of a Philips PW9700 S0 2 analyzer. Pine seedlings were gently pulled out of the styrofoam trays and inserted into vertically slitted neoprene stoppers so that the foliage extended through the top of the stopper and the sphagnum plugs containing the roots extended through the bottom. The stoppers holding the seedlings were inserted through holes cut in the bottom of the cuvette so that the slit closed firmly around the stem and sealed the hole. The cuvette was placed over a tank filled with enough water to keep the sphagnum plugs moist during the experiment. The access ports of the cuvettes were sealed to avoid any leakage. The air flow was set at 10 1 • min~'; S 0 2 flow was adjusted to give the desired concentration at the output of the cuvette. The cuvettes were placed inside a controlled environmental chamber to maintain uniform light and temperature conditions. Fumigations were carried out for 96 h at a temperature of 22°C under 0.80 W-m^ 2 light source (Sylvania high-pressure sodium and mercury halide lamps). Relative humidity measured in the output gas stream varied between 60 and 80%. Extraction of the plant material After treatment with S 0 2 , the needles were washed with distilled water, dried, and transferred to 100 ml of boiling 95% ethanol. After boiling for 5 min, the liquid was allowed to cool and was filtered into a large flask. The tissue was transferred to 50 ml of 60% ethanol and ground for 5 min (Virtis 23 homogenizer). The homogenate was filtered through a Biichner funnel under vacuum, and the residue was washed twice with 60% ethanol. The pigments were removed from the combined 60 and 95% ethanol extracts by double extraction with petroleum ether. The pigment-free extract was evaporated to dryness using a rotary evaporator. The dried residue was then dissolved in about 50 ml of distilled water and centrifuged for 10 min at 27,000 g. The residue was washed in 10 ml of distilled water and centrifuged again. The supernatant layers from the two centrifugations were combined, centrifuged once more to obtain a clear supernatant layer, evaporated to dryness, and dissolved in 10 ml of distilled water (crude extract). The phenolic compounds were then removed from the crude extract by treatment with purified insoluble PVP, which was purified according to McFarlane and Vader (1962). The mixture was Physiol. Plant. 47. 1979 filtered through a 0.8 ,um Millipore filter under vacuum to obtain a clear solution. Purification of amino acids and sugars The above clear solution was passed through a Dowex 50W x 8, H + form (20-50 mesh) cation exchange resin column. Before the column was loaded with the sample, the resin in the column was thoroughly washed with water until the pH of the effluent was close to neutrality. The flow rate was adjusted to approximately 20 drops per minute. For easier operation, the cation exchange resin column was fixed on top of another column with anion exchange resin (Dowex 1 x 8, CI" form, 20-50 mesh) so that every drop flowing from the former would fall into the latter. The organic acids were held by the anion exchange column, and the effluent which passed through the anion column was the neutral fraction containing sugars. After the cation exchange column was washed with water, the elution of amino acids was carried out with 50 ml of 2 M NH 4 OH. The eluate was evaporated to dryness until no NH 3 odor could be detected. The residue was dissolved in 5 ml of distilled water, and the pH of the solution was adjusted to 2.5 with 4 M formic acid to release any remaining ammonia. The solution was once again evaporated to dryness, and the residue was dissolved in water to give a final volume of 5 ml. The neutral fraction containing sugars was reduced to a volume of 10 ml on a rotary evaporator. Amino acid determination The amino acid content of the purified amino acid fraction was determined by ninhydrin assay as described by Rosen (1957). Determination of reducing and non-reducing sugars The reducing sugar content in the neutral fraction was determined according to Bell (1955). For non-reducing sugars, an appropriate aliquot of the neutral fraction was mixed with formic acid to a final concentration of 6 M formic acid. The mixture was then refluxed for 2 h to convert non-reducing sugars to their monosaccharide components (reducing sugars) before quantitation according to the above method. The difference between the total sugars and the reducing sugars thus corresponds to the non-reducing sugars. Preparation of amino acid derivatives for gas-liquid chromatography The derivatization was carried out as suggested by Cancalon and Klingman (1974) with a slight modification. An aliquot of an aqueous sample containing 0.5 mg amino acids was evaporated to dryness in a silylation tube under a stream of dry nitrogen at 60° C. Any trace of moisture was Physiol Plant 47 1979 SO, EFFECTS ON PINE SUGARS AND AMINO ACIDS removed azeotropically with methylene chlonde. The residue was dissolved in i 5 ml ot 3 M butanohc HC1 by sonication for 30 mm. For the butylation reaction, tubes were capped and heated in an oil bath at 100° C for 15 min, after which the caps were removed and the contents evaporated to dryness at 60° C under a stream of dry nitrogen. Methylene chloride was added to the residue and evaporated to dryness to ensure the complete removal of moisture. The residue was dissolved m 0.9 ml methylene chlonde and 0.1 ml tnfluoroacetic anhydride by sonication. The tubes were cooled, and the solution was analyzed by gas-liquid chromatography. Known amounts of standard amino acids were treated in the same manner as above. Butyl stearate was used as the internal standard. Gas liquid chromatography The complete separation of 20 amino acids was carried out on two glass columns (1.8 x 2 mm) with different packings: 'Tabsorb' and -Tabsorb H A C (both obtained from Regis Chemical Co., Chicago, Illinois). 'Tabsorb H A C facilitated the separation of histidme, arginine, and cystine; 'Tabsorb' separated the remainder of the ammo acids. Regis Chemical Co. has used these packings for successful separation of all 20 ammo acids. The columns were mounted in the gas chromatograph oven and conditioned for 24 h at 200°C with a N 2 flow of 15 ml-min-' Amino acid analyses were carried out with a Hewlett Packard Model 5834A gas chromatograph equipped with dual flame ionization detector and built in data processor. The N, carrier flow rate was adjusted to 30 ml •mm - 1 . The H 2 and air pressure were set at 140 and 190 kPa, respectively. High pressure liquid chromatography The analysis of ammo acids was carried out using a standard Durrum column on a D-500 amino acid analyzer according to Benson (1973). Neither the gas-liquid chromatography nor the high pressure liquid chromatography was versatile enough to analyze and estimate the levels of glutamine and asparagine in pine needle extracts. The limitations of these methods were, however, imposed by different factors. The column and the buffer system used in the high pressure liquid chromatography were not capable of resolving the mixture of threonine, serine, glutamine, and asparagine. Although the method provided a measure of glutamic and aspartic acids, no measurement of glutamine and asparagine could be made. On the other hand, the gasliquid chromatography method was unable to resolve glutamic acid from glutamine and aspartic acid from asparagine. This occurred because of hydrolysis during denvatization of glutamine and asparagine to glutamic acid and aspartic acid, respectively. Paper chromatography was therefore employed for the estimation of glutamine and asparagine. 225 Paper chromatography The quantitative estimation of glutamine and asparagine in ammo acid fractions from control and S0 2 treated plant tissues was achieved by applying the sample as a band on 3 mm Whatman paper and developing it in H-butanol acetic acid-H,0 (12 3 5, v/v) as described by Smith (1969) Standard ammo acids were used for identification and quantitation After development, the paper was dried and sprayed with a reagent containing 0.2 g nmhydnn, 5 ml acetic acid, and 95 ml rc-butanol saturated with water. The paper was then heated at 75 °C for 30 mm. The bands corre spondmg to glutamine, asparagine, glutamic acid, and aspartic acid were cut out, and the color was eluted in 5 ml of methanol as described by Jager et al. (1972). The absorbance at 500 nm for each eluent was measured by a spectrophotometer. Results and Discussion All experiments reported herein were repeated at least three times with qualitatively similar results. Effects ofS02 on sugars Increasing concentration of gaseous S 0 2 resulted in an increase (p < 0.05) in reducing sugars (Table 1), the increase was much more pronounced at 1 34 mg-m~ 3 S0 2 concentration than at 0.89 mg m~3 At the same time, S0 2 at 1 34 mg m~3 concentration produced a considerable drop (p < 0.05) in non reducing sugars (Table 1). Another pollutant. ozone, has also been shown to increase the reducing sugar content and decrease the starch content in rough lemon seedlings (Dugger and Palmer 1969). Recently, Koziol and Jordan (1978) reported that there is an increase in free sugar levels after exposure of red kidney bean seedlings, at least up to a concentration of 2 mg • ITT3 S0 2 . Our results on pine needle tissues are in good agreement with theirs. However, Koziol and Jordan (1978) had to use a much higher S0 2 concentration than the 1 34 mg m~3 used in our experiments to observe an appreciable reduction in starch content The increased concentration of reducing sugars after Table 1 The effect of gaseous S02 on reducing and non reducing sugar content of jack pine seedlings Each reading is from one experiment with triplicate extractions (12-15 plants) Values bearing the same letter do not differ significantly (p < 0 05) in Duncan's multiple range test (Steel and Tome 1960) Reducing sugar content SO, mg m 3 Control 0 89 134 Non reducing sugar content umol g ' fr wt ,umol g ' dry wt fimo\ g ' fr wt 36 0 48 8 68 8 116 9a 163 5 b 187 0 c 68 74 10 fjmoi g_1 dry wt 22 1 a 25 0 a 2 8b 226 S S MALHOTRA AND S K SARKAR Physiol Plant 47 1979 fumigation with S0 2 (Table 1) may be due either to their increased biosynthesis or to the breakdown of reserve polysaccharides rich in reducing sugars The decline in non reducing sugars may be an inhibitory effect of S 0 2 on their biosynthesis. Another plausible explanation for such a response would be the partial breakdown of non-reducing carbohydrates into simple reducing sugars. Fumigation of seedlings with 0.89 mg • m~3 S 0 2 concentration produced no change in the non-reducing sugar content (Table 1) and no visual symptoms of toxicity. However, at the higher concentration of 1.34 mg • m~3 S 0 2 there was a pronounced drop in non-reducing sugar content, and needle tips of older foliage exhibited chlorosis. This suggests that extreme changes in cellular metabolites may have a direct beanng on visual symptom expression. The content of alanine, glycine, threonine, lysine, and methionine in pine seedlings increased with increasing con centration of gaseous S0 2 (Table 3). A maximum increase was observed for alanine, followed by a somewhat smaller increase in lysine, glycine, and threonine at a concentration of 1.34 mg-m~ 3 S 0 2 (p < 0.05). It is suggested that S0 2 caused an increase in the amount of these amino acids by stimulating the breakdown of membrane and other proteins. Sulphur dioxide has previously been shown to cause breakdown of chloroplast membranes in pine needles (Malhotra 1976). At 0.89 mg • irr 3 concentration, S 0 2 caused a decrease (p < 0.05) in the levels of valine and leucine, but at 1.34 mg • m~3 (p < 0.05) an increase. It appears that S0 2 at a low concentration (0.89 mg-m~ 3 ) inhibits the synthesis of valine and leucine, and at a higher concentration of 1.34 mg • m~3 may bring about protein breakdown. If the protein Effect ofS02 on totalfree amino acids hydrolysis hypothesis is correct, one would expect to find an The data in Table 2 show an increase ( p < 0.05) in the increase in amino acids such as proline, serine, and phenyltotal free amino acid content of pine needles after treatment alanine; instead, their content declines at 1.34 mg • m~3 S0 . 2 with gaseous SO z similar to that presented for reducing Under these conditions, such a response can be explained by sugars m Table 1 increased conversion of proline, serine, and phenylalanine The initial increase in ammo acid content preceded visible into related amino acids within their families; for example, symptoms of injury, which only occurred after fumigation at serine may have been converted into glycine. 1.34 mg • m~3 S 0 2 concentration. The increase in free amino The ammo acids related to the aspartate family, namely acid content at the higher S 0 2 concentration was probably lysine, methionine, threonine, and isoleucine, either increased brought about by protein hydrolysis, which can eventually or remained unchanged with S 0 2 (Table 3). This may be a lead to tissue senescence (Fischer 1971). result of S 0 2 effect on increased biosynthesis or on breakWorking with Phaseolus vulgaris, Trifoltum repens, and a down of membrane and other proteins, or both. Since plants mixture of grasses, Arndt (1970) also found that S 0 2 exposed to 1.34 mg m~~3 S 0 2 for 96 h showed some fumigations at 0.63 mg-m" 3 caused an increase in the content of free ammo acids. Similar changes in total ammo acid content of spruce needles from high industrial emission Table 3 The effect of gaseous S02 on jack pine ammo acids _1 regions have been reported by Jager and Grill (1975). In separated by gas liquid chromatography Data expressed in p% g dry wt Each reading is from one experiment with triplicate order to explain such S0 2 effects on total free ammo acids, extractions (12-15 plants) Values bearing the same letter do not we studied changes in the levels of individual amino acids by differ significantly (p < 0 05) in Duncan's multiple range test means of gas-liquid chromatography. (Steel and Tome 1960) Gas-liquid chromatographic analysis of ammo acids All amino acid fractions from the control and S 0 2 treated tissues were also analyzed by high pressure liquid chromatography Because the results were similar to those obtained by gas-liquid chromotography, only the latter are discussed. Amino acid Alanine Valine Glycine Isoleucine Table 2 The effect of gaseous S02 on the total amino acid contentLeucine of jack pine seedlings Each reading is from one experiment with Proline triplicate extractions (12-15 plants) Values bearing the same letter Threonine do not differ significantly (p < 0 05) in Duncan's multiple range test Serine (Steel and Tome 1960) Cysteine Methionine Ammo acid Ammo acid Phenylalanine _1 S0 2 //mol g fimol g ' Aspartic acid 3 mg m~ fr wt dry wt Glutamic acid Tyrosine Control 40 13 0 a Lysine 0 89 58 19 5 b Tryptophan 1 34 74 20 2 b Arginine Control 0 89mg m"3 1 34 mg m~3 984 a 67 a 23 a 75 a 90 a 144 a 88 a 360 a 0 14 a 40 a 191a 849 a 32 a 18a 1837 b 35 b 30 a 64 a 13b 74 b 108 a 325 a 16 17a 26 a 374 b 1091b 26 a 28 a 191 611b 3248 c 107 c 54 b 96 b 169 c 123 a 177b 266 b 16 21a 34 a 244 c 721c 86 b 49 b 0 558 b 0a 436 a Physiol. Plant. 47. 1979 SO, EFFECTS ON PINE SUGARS AND AMINO ACIDS 227 symptoms of S0 2 phytotoxicity, it is possible that the cant (p < 0.05) change in phenylalanine. The tyrosine level, -3 increase in these amino acids was mainly due to protein on the other hand, increased dramatically at 1.34 mg-m (p < 0.05); again this may be due to protein hydrolysis. hydrolysis. Fischer (1971) reported that chlorosis of Vicia The amino acids related to glycerate-3-phosphate, namely faba and Nicotiana tabacum leaves caused by exposure to gaseous S 0 2 resulted in a substantial reduction of the protein serine and glycine, responded to S0 2 differently. The serine content declined (p < 0.05) after S 0 2 fumigation at 1.34 content of these leaves. 3 Aspartic acid also exhibited a considerable increase at mg-m~ concentration, whereas glycine increased (p < 3 0.89 m g - n r S 0 2 ( p < 0.05): however, this increase was 0.05) under the same conditions. While studying the effects substantially reduced at 1.34 mg • m~3 (p < 0.05), suggesting of S 0 2 on wheat plants, Tanaka et al. (1972) observed a a conversion of aspartic acid to asparagine at higher similar decline in serine content, but failed to detect any S0 2 concentrations. Paper chromatographic analyses of glycine in their preparation. Possibly a conversion of serine asparagine in the above fractions confirmed that S 0 2 at 1.34 into glycine accounts for the decline in serine vis-a-vis an mg-mr 3 concentration produced more asparagine than increase in glycine. Even at a low concentration (0.89 mg • m~3) that did not aspartic acid, indicating a conversion of aspartic acid to asparagine, probably mediated through asparagine syn- produce any visual symptoms on the foliage, S 0 2 had a thetase. Changes similar to these were also observed for drastic effect on the levels of the most essential metabolites, glutamic acid and glutamine. Studies on the effect of S 0 2 on such as sugars and amino acids. The analyses of such metabolites may provide an effective tool to determine the extent glutamine and asparagine synthetase are under way. Jager and Grill (1975) reported a change in the glutamic of hidden S 0 2 injury to vegetation. The mechanisms by acid content of spruce similar to the one demonstrated in this which some of the changes in metabolites are brought about paper. At the same time, they showed a decline in the glycine cannot yet be fully explained. Some of the enzymatic procontent under the influence of S0 2 , which is contrary to our cesses that we speculate are involved in these changes and findings. However, Jager and Grill (1975) worked with are currently under investigation. spruce tissues collected from a region damaged by industrial We thank Mr. J. Shuya and Miss E. Hargesheimer for technical exhaust, which may have contained a variety of emission assistance and Mr. P. Hurdle for construction and operation of S0 2 elements in addition to S 0 2 , whereas all our work was fumigation facilities. We are grateful to the Alberta Oil Sands carried out under controlled environmental and S 0 2 Environmental Research Program forfinancialassistance. fumigation conditions. The effects of S 0 2 on amino acids belonging to the glutamate family, such as arginine and proline, were not References similar. The arginine level increased considerably at 0.89 3 3 mg-mr S 0 2 and then dropped slightly at 1.34 mg-m~ ; Arndt, U. 1970. Konzentrationsanderungen bei freien Aminosauren in Pflanzen unter dem Eintluss von Fluorwasserstoff und however, the decline was not significant ( p < 0.05). Proline Schwefeldioxid. — Staub Reinhalt. Luft 30: 256-259. content, on the other hand, declined at 0.89 mg-m~3 Bell, D. J. 1955. Mono- and oligosaccharides and acidic monoS0 2 (p < 0.05). Glutamic acid content initially increased saccharide derivatives. — In Modern Methods of Plant Analysis slightly at 0.89 mg-m- 3 S 0 2 ( p < 0.05), followed by a (K. Peach and M. V. Tracey, eds.) 2: 1-54. Springer-Verlag, 3 Berlin. decrease at 1.34 mg-m" ( p < 0.05). The drop in glutamic acid content at the high S 0 2 concentration was probably Bleasdale, J. K. A. 1952. Atmospheric pollution and plant growth. — Nature 169: 376-377. brought about by pollutant effect on glutamine synthetase. Benson, J. R. 1973. Single column analyses of protein hydrolyzates Jager and Pahlich (1972) have reported a stimulatory effect in two hours. — Durrum Report No. 4. Durrum Chemical of S 0 2 on glutamine synthetase from pea seedlings. Corp. Palo Alto, CA (U.S.A.). The amino acids of the pyruvate family, such as alanine, Brandt, C. S. & Heck, W. W. 1968. Effects of air pollutants on vegetation. — In Air Pollution (A. C. Stern, ed.) 1: 401-443. leucine, valine, and isoleucine, all increased at 1.34 mg • m - 3 Academic Press, New York. S 0 2 concentration ( p < 0.05). Alanine increased at both Cancalon, P. & Klingman, J. D. 1974. An improved procedure for concentrations ( p < 0.05); however, leucine and valine preparing the n-butyl-trifluoroacetyl amino acid derivatives and its application in the study of radioactive amino acids from biodropped at 0.89 mg • m - 3 SO z (p < 0.05) before exhibiting a logical sources. — J. Chromatogr. Sci. 12: 349-355. major increase at 1.34 mg-m~ 3 (p < 0.05). Isoleucine also Dugger, W. M. & Palmer, R. L. 1969. Carbohydrate metabolism in increased at 1.34 m g - m - 3 S 0 2 concentration ( p < 0.05). leaves of rough lemon as influenced by ozone. — Int. Proc. The increase in these amino acids may have been a result of Citrus Symp. 2:711-714. protein hydrolysis accompanying chlorosis (Fischer 1971) at Fischer, K. 1971. Methoden zur Erkennung und Beurteilung forstschadlicher Luftverunreinigungen. Chemische und physikalische high S 0 2 concentrations, as was suggested by development Reaktionen S02-begaster Pflanzen und Blatter. — Mitt. Forstl. of visual symptoms at the end of the 96-h fumigation Bundes-Versuchsanst. Wien 92: 209-231. period. Jager, H. & Grill, D. 1975. Einfluss von S0 2 und HF auf AminoPhenylalanine and tryosine belong to the phospho-enolsauren der Fichte (Picea abies [L.j Karsten). — Eur. J. For. Pathol. 5:279-286. pyruvate family. Sulphur dioxide did not cause any signifi- 228 S S MALHOTRA AND S K SARKAR — & Pahlich, E 1972 Einfluss von SO, auf den Aminosaur estoffwechsel von Erbsenkeimlingen — Oecologia (Berl.) 9 1^-140 & Steubmg, L 1972 Die Wirkung von Schwefeldioxid auf den Aminosaure- und Protemgehalt von Erbsenkeimlingen. — Angew. Bot 46- 199-211 Khan. A A. & Malhotra. S. 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SO, in the environment. its production, dispersal and fate. — In Air Pollution and Lichens (B. W Ferry, M. S. Baddeley and D. L. Hawksworth, eds.), p. 6 Athlone Press. London Smith. 1 1969 Amino acids, amines and related compounds. — In Chromatographic and Electrophoretic Techniques (1. Smith, ed.) 1 104-147. Interscience Publishers. New York Steel, R. G. D & Tome, J H. 1960. Principles and Procedures of Statistics. — McGraw-Hill Book Company Inc., New York. Tanaka, H., Takanashi, T.. Kadota, M. & Yatazawa, M 1972 Experimental studies on sulfur dioxide injuries in higher plants. — Water. Air. Soil Pollut 1 343-346 Tmgey. D T . Heck. W. W & Reinert. R A 1971. Effect of low concentrations of O, and SOj on foliage growth and yield of radish. — J. Am. Soc. Hortic Sci. 96. 369-371. Ziegler, 1 1973. Effects of sulphite on phosphoenolpyruvate carboxylase and malate formation in extracts of Zea mays. — Phytochemistry 12 1027-1030 — 1975. The effects of SO, pollution on plant metabolism. — Residue Rev. 56:79-105 '
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