Page 1
Temperature is the key to altitudinal variation of phenolics 1
in Arnica montana L. cv. ARBO 2
3
4
5
Andreas Albert,1 Vipaporn Sareedenchai,2 Werner Heller,3 Harald K. Seidlitz,1 and Christian 6
Zidorn2* 7
8
9
10
1 Abteilung Experimentelle Umweltsimulation, Institut für Bodenökologie, Helmholtz 11
Zentrum München – Deutsches Forschungszentrum für Gesundheit und Umwelt, Ingolstädter 12
Landstraße 1, 85764 Neuherberg, Germany 13 2 Institut für Pharmazie, Abteilung Pharmakognosie, Universität Innsbruck, Innrain 52, Josef-14
Moeller-Haus, 6020 Innsbruck, Austria 15 3 Institut für Biochemische Pflanzenpathologie, Helmholtz Zentrum München – Deutsches 16
Forschungszentrum für Gesundheit und Umwelt, Ingolstädter Landstraße 1, 85764 17
Neuherberg, Germany 18
19
20
21
*Correspondence: Institut für Pharmazie, Universität Innsbruck, Innrain 52, A-6020 22
Innsbruck, Austria; E-Mail: [email protected] , Tel.: +43 512 5075302; Fax: +43 23
512 5072939. 24
25
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Abstract 26
27
Plants in alpine habitats are exposed to many environmental stresses, in particular temperature 28
and radiation extremes. Recent field experiments on Arnica montana L. cv. ARBO indicated 29
pronounced altitudinal variation in plant phenolics. Ortho-diphenolics increased with altitude 30
compared to other phenolic compounds, resulting in an increase of antioxidative capacity of 31
the tissues involved. Factors causing these variations were investigated by climate chamber 32
experiments focusing on temperature and UV-B radiation. Plants of Arnica montana L. cv. 33
ARBO were grown in climate chambers under realistic climatic and radiation regimes. Key 34
factors temperature and UV-B radiation were altered between different groups of plants. 35
Subsequently, flowering heads were analyzed by HPLC for their contents of flavonoids and 36
caffeic acid derivatives. Surprisingly, increased UV-B radiation did not trigger any change in 37
phenolic metabolites in Arnica. In contrast, a pronounced increase in the ratio of B-ring ortho-38
diphphenolic (quercetin) compared to B-ring monophenolic (kaempferol) flavonols resulted 39
from a decrease in temperature by 5°C in the applied climate regime. Conclusively, enhanced 40
UV-B radiation measured at higher altitudes is probably not the key factor triggering shifts in 41
the phenolic composition in Arnica grown at higher altitudes but it is rather the temperature 42
which decreases with altitude. 43
44
Keywords: Asteraceae, chemical ecology, UV-B radiation, free radicals, antioxidants. 45
46
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Introduction 47
Altitudinal variation of secondary metabolite profiles of higher plants is not well investigated 48
so far. Only a few studies deal with this subject and most of them are based on plants growing 49
in the natural habitat. In such studies major contributions of genetic differences between low 50
and high altitude plants to the observed phytochemical variation cannot be excluded. The few 51
field trials using cultivated, genetically uniform plants indicated that there was indeed 52
pronounced altitudinal variation, especially with regard to the content of phenolic compounds. 53
The observed variation encompassed higher relative yields of ortho-diphenolic compared to 54
other phenolic metabolites and higher overall levels of phenolic acids. Additionally, results 55
confirmed a higher antioxidant capacity of extracts derived from high versus low altitude 56
plants (Spitaler et al. 2006, 2008; Ganzera et al. 2008). 57
A broad range of environmental factors changes with the elevation of the natural growing 58
site. These factors include precipitation, mean temperature, soil, wind speed, temperature 59
extremes, duration of snow-cover, length of the vegetation period, and radiation intensities 60
(Körner 1999). UV-B (280–315 nm) irradiation increases under clear sky conditions by 61
approximately 18 % per 1,000 m of altitude (Blumthaler et al. 1997). Enhanced UV-B 62
radiation has most intensely been discussed to affect the plant secondary metabolism (Körner 63
1999) and only recently low temperatures were also linked with an increase of antioxidative 64
secondary metabolites in plants (Bilger et al. 2007). Enhanced biosynthesis of UV-B 65
absorbing and antioxidant phenolic compounds was interpreted as a protective response 66
against damage from excessive UV-B radiation in plants by their shielding properties 67
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4
(Markham et al. 1998b; Körner 1999), while their radical scavenging potentials also 68
contributes to their protective activity (Markham et al. 1998a; Spitaler et al. 2006, 2008). 69
The induction of UV-B protective metabolites by enhanced UV-B radiation is well 70
documented (Bornman et al. 1997; Ries et al. 2000; Ibdah et al. 2002). On the other hand, the 71
crucial factors governing the altitudinal variation in the field trials has not been thoroughly 72
investigated so far and is the objective of the present study. Like for some of the previous 73
field studies Arnica montana cv. ARBO was chosen as a model organism, a) because 74
secondary metabolites from this species are well investigated, b) because the conspicuous 75
flowering heads present a defined ontogenetic stage, which is well suited for comparative 76
investigations, and c) because findings acquired for this important medicinal plant might be 77
transferable to other medicinal plants at least from the Asteraceae family. 78
Previous experiments in the field revealed statistically significant increases of the ratio of 79
ortho-dihydroxy flavonoids to other flavonoids with the altitude of the growing site as well as 80
positive correlations of the total content of both caffeic acid derivatives and the radical 81
scavenging activity of extracts with the altitude of the growing site. These correlations were 82
observed in three successive years and they were observed in plants cultivated in the natural 83
soil as well as in plants potted in standardized soil (Spitaler et al. 2006, 2008). For the 84
altitudes simulated in this paper (600 m for the sub-montane and 1400 m for the high-85
montane site, these increases averaged 22.8 % for the ratio of ortho-dihydroxy-flavonoids to 86
other flavonoids and 19.6 % for the total amounts of caffeic acid derivatives (Spitaler et al. 87
2008 and Tables 1-3, partially derived from the data published therein). 88
89
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Materials and Methods 90
Plant Material 91
Arnica montana cultivar ARBO plants purchased (Saatzucht Steinach/Germany) in 2004 were 92
transferred to light brown quadrangular plastic pots (edge length 20 cm, depth 25 cm) filled 93
with peat and sand (1/1, v/v), and maintained in the shade in the open land at Innsbruck 94
Botanical Gardens. For the actual experiments, the plants were transferred to the CCs (climate 95
chambers) of the Helmholtz Center Munich (Döhring et al. 1996; Thiel et al. 1996) from May 96
2006 to June 2006 and from May 2007 to June 2007. After two day acclimation period 97
without any UV, UV levels were gradually (within three day) enhanced to the levels 98
described below. 99
For each CC and treatment six terminal flowering heads from different plants (one terminal 100
flowering head per plant) were collected separately at the peak of flowering (Douglas et al. 101
2004; Spitaler et al. 2006). Flowering heads were collected at the first day when all the 102
ligulate flowers and at least two rows of tubulate of the flowering head were fully opened. 103
This procedure was chosen to minimize ontogenetic effect which had been observed in an 104
earlier investigation (Douglas et al. 2004). Heads were air-dried in the shade at ambient 105
(25°C) temperature. This procedure was chosen to enable comparison with the results from 106
previous field experiments in which flowering heads were dried in the same way (Spitaler et 107
al. 2006, 2008). Air-dried heads were kept at -20 °C until analysis. 108
Flowering heads were collected on the following dates. 2006 experiment: climate chamber 109
1 ambient UV 20.05., 29.05., 01.06., 06.06. (2 heads), 11.06., climate chamber 1 enhanced 110
UV 02.06. (2 heads), 06.06. (2 heads), 11.06., 14.06., climate chamber 2 ambient UV 06.06. 111
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6
(5 heads), 13.06., climate chamber 2 enhanced UV 29.05. (3 heads), 01.06. (2 heads), 06.06.; 112
2007 experiment climate chamber 1 high montane temperature regime no UV 06.06., 16.06. 113
(2 heads), 18.06., 26.06. (2 heads), climate chamber 1 high montane temperature regime 114
ambient UV 31.05. (3 heads), 14.06. (2 heads), 18.06., climate chamber 2 submontane 115
temperature regime no UV 24.05., 29.05. (3 heads), 30.05. (2 heads), climate chamber 2 116
submontane temperature regime ambient UV 24.05. (2 heads), 25.05., 29.05., 30.05. (2 117
heads). 118
119
Climate chambers 120
The plant treatment was done in the sun simulator facilities of the Helmholtz Center Munich. 121
The natural photobiological environment was provided using a combination of four lamp 122
types (metal halide lamps, quartz halogen lamps, blue fluorescent tubes and UV-B fluorescent 123
tubes) to obtain a natural balance of simulated global radiation throughout the ultraviolet to 124
infrared spectrum. The lamp types are arranged in several groups to realise the natural diurnal 125
variations of the solar irradiance by switching appropriate group of lamps on and off. The 126
short-wave cut-off was shaped by selected borosilicate and soda-lime glass filters (Döhring et 127
al. 1996; Thiel et al. 1996). 128
129
Climate chamber parameters 130
CC settings 2006: both CCs day temperature (high montane): 20.0°C; night temperature: 131
7.5°C; same amount of sufficient irrigation (not quantified); and same relative humidity: day 132
40%, night 70%. CCs were separated by UV-B absorbing acrylic glass into a zone exposed to 133
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7
a radiation regime equaling midsummer conditions for Innsbruck (N 47°15’, E 11°23’, 580 m 134
a.s.l.) under clear sky [mean daily dose: 58.4 mol m-2 PAR (Photosynthetic Active Radiation, 135
400–700 nm), 658 kJ m-2 d-1 UV-A with a noon maximum of photosynthetic active radiation 136
(PAR 400-700 nm) of 1500 µmol m-2 s-1, and 6.3 kJ m-2 d-1 UV-BBE (biologically effective 137
UV-B dose normalized at 300 nm; Caldwell, 1971)] and a second zone with threefold 138
enhanced UV-BBE (17.8 kJ m-2 d-1). PAR Radiation exposure from 5:00 to 21:00 h and UV 139
radiation from 9:00 to 17:00 h. CC settings 2007: CC-1 day temperature 20.0°C, night 140
temperature 7.5°C (high montane); CC-2 day temperature 25.0°C, night temperature 12.5°C 141
(sub-montane). CCs were delimited by UV absorbing acrylic glass into two subsections one 142
with ambient UV-B and one with no UV-B radiation. CC-1 and CC-2 ambient: 53.0 mol m-2 143
PAR, 635 kJ m-2 d-1 UV-A, and 8.0 kJ m-2 d-1 UV-BBE; UV-minus subsections: no UV-B 144
radiation. Other parameters were as in 2006. Horizontal variations of the applied radiation 145
were less than 15% in the CCs in both experiments. 146
147
Extract preparation 148
Each air-dried flowering head was ground and phenolics were analyzed by HPLC/DAD 149
analogous to the procedure described previously (Spitaler et al. 2006). In detail, after adding 150
1.00 mg of the internal standard compound cynarin as a stock solution in MeOH, (CH3)2CO, 151
and H2O (3/1/1, v/v/v), exactly weight ground flowering heads (weighing approximately 200 152
mg each) were sonicated twice for 30 min with a mixture of MeOH, (CH3)2CO, and H2O 153
(3/1/1, v/v/v) and once for 30 min with a mixture of MeOH and H2O (1/1, v/v) (total 154
extraction volume 25 ml for each cycle). The extracts were filtered, the remaining plant 155
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material rinsed with 20 ml of a mixture of MeOH, (CH3)2CO, and H2O (3/1/1, v/v/v) and the 156
combined extracts were filled up to 100.0 ml with a mixture of MeOH, (CH3)2CO, and H2O 157
(3/1/1, v/v/v); 30.0 ml of this solution were brought to dryness in vacuo and redissolved in 158
2.00 ml of a mixture of MeOH, (CH3)2CO, and H2O (3/1/1, v/v/v). After filtration, this 159
solution was used for HPLC analysis. Comparative investigations using different extraction 160
media and longer times of sonication, and a larger number of sonication cycles proved that the 161
chosen procedure led to an exhaustive extraction. All quantitative analyses were run in 162
triplicate. 163
164
HPLC analyses 165
HPLC analyses of phenolics were performed as described previously (Spitaler et al. 2006). In 166
detail, a HP-1090 ChemStation equipped with DAD detectors was employed and the 167
following parameters were applied: column, Phenomenex Synergi Hydro-Rp 80A 168
150 x 4.6 mm (4 m material); guard column, Phenomenex Security Guard C18 (ODS, 169
Octadecyl) 4.0 mm x 3.0 mm; mobile phase A, H2O/HCOOH/CH3COOH (99/0.9/0.1, v/v/v); 170
phase B, MeCN/MeOH/HCOOH/CH3COOH (89/10/0.9/0.1, v/v/v/v); flow rate, 1.00 ml/min; 171
injection volume 10 l; detection wavelength 350 nm; oven temperature, ambient; linear 172
gradient, 0 min 5% B, 5 min 15% B, 20 min 16% B, 35 min 18% B, 45 min 19% B, 55 min 173
27.5% B, 60 min 65% B, 65 min 98% B, 70 min stop; post time, 12 min. The amounts of 174
phenolics were estimated by comparing the peak areas obtained for the particular flavonoids 175
F1-F6 and caffeic acid derivatives P1-P9 with the peak area obtained for the internal standard 176
cynarin (CYN). 177
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178
Compound identification 179
Phenolics were grouped into flavonoids (F) and caffeic acid derivatives (phenolic acids, P) 180
based on their characteristic UV spectra (F: a broad maximum at 350 nm, P: a maximum at 181
330 nm with a shoulder at 295 nm). Peaks assignable to flavonoids (F1-F6) and phenolic 182
acids (P1-P9) were numbered consecutively with increasing HPLC retention times. Peak 183
characterization and compound identification was performed as previously described (Spitaler 184
et al. 2006). Peak identities are also revealed in Table 4. 185
186
Data analysis 187
Analyses of variance (ANOVAs) and Student-Newman-Keuls tests were calculated using 188
Stanton A. Glantz’ Biostatistics 4.04 (McGraw Hill, Columbus, OH, USA) software package. 189
190
Results 191
HPLC quantification of flowering head metabolites of Arnica montana cv. ARBO of a first 192
climate chamber trial focused on the effect of UV-B radiation. The control group was exposed 193
to ambient radiation intensities realistic for the Innsbruck area while the plants grown under 194
enhanced UV obtained a nearly threefold daily UV-B radiation dose. These differences in 195
growing conditions did not reveal any significant UV-B-dependent effect on secondary 196
metabolite profiles (data not shown) although the applied enhanced UV-BBE value exceeded 197
the radiation encountered at subnival altitudes in the Alps. 198
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A second climate chamber trial focused on effects of two different temperature regimes on 199
the phenolic pattern. The daily temperature regime in one chamber simulated field conditions 200
in July in the upper montane (approx. 1400 m a.s.l.) regions of the Tyrol area and in a second 201
chamber day and night temperatures simulated field conditions in lower montane regions. 202
Each climate chamber was sub-divided into two compartments, one excluding any 203
biologically effective UV-B radiation and another including UV-B radiation equaling 204
moderate ambient radiation conditions observed at montane altitudes. Table 4 displays 205
detailed results from this second trial. Moreover, Fig. 1 displays sample chromatograms from 206
a flowering head of each of the four experimental groups. 207
ANOVA (analysis of variance) from the data summarized in Table 4 for the total amounts 208
of flavonoids indicated no significant differences between any of the analyzed treatments 209
(ambient UV-B vs. no UV-B combined with lower vs. higher temperature). ANOVA in 210
combination with a consecutively performed Student-Newman-Keuls test of the results for the 211
total amounts of caffeic acid derivatives revealed significantly higher amount of caffeic acid 212
derivatives in the flowering heads of UV-B exclusion group of chamber 1 in comparison to all 213
other treatments. Most interestingly, ANOVA of data for the ratios of ortho-dihydroxy 214
flavonoids (Q) to other flavonoids (K) showed a highly significant inter-treatment variation (P 215
= 0.002). A consecutively performed Student-Newman-Keuls test revealed at P < 0.05 that 216
flowering heads from both groups (ambient UV-B and no UV-B) of chamber 1 (lower 217
temperatures) had a significantly higher Q/K ratio than flowering heads from both groups 218
cultivated at a temperature regime of only 5°C higher. Differences in the contribution of each 219
particular compound to the total of its compound class in percent are highlighted in Fig. 2. 220
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The following of the observed differences were statistically significant (ANOVA and 221
consecutive Student-Newman-Keuls test at P < 0.05 t): Both lower temperature groups 222
contained higher percentages of F1 and lower percentages of F5 and F6 than both higher 223
temperature groups. Both UV-B exclusion groups contained higher percentages of P4 than 224
both groups treated with ambient UV-B. Moreover, both groups treated with ambient UV-B 225
contained higher percentages of P9 than the higher temperature group grown without any 226
UV-B. 227
Conclusively, I) total flavonoid amounts did not show any significant differences between 228
treatments. II) The ratio of B-ring mono- to ortho-diphenolic flavonol derivatives 229
significantly differed between plants grown under the two temperature regimes, while the 230
different UV-B regimes applied at a specific temperature did not affect this parameter. III) A 231
significant increase of caffeic acid derivatives grown under reduced temperatures was only 232
observed for plants grown in the absence of UV-B radiation. 233
234
Discussion 235
Earlier investigations on native (Zidorn and Stuppner 2001; Zidorn et al. 2005; Alonso-236
Amelot et al., 2007) as well as cultivated plants (Spitaler et al. 2006, 2008; Ganzera et al. 237
2008) revealed significant positive correlations with the sea level of the growing site as well 238
as with the amounts of certain phenolic antioxidants. In the light of prevailing theories these 239
altitudinal variations were interpreted as adaptive responses to the elevated level of harmful 240
UV-B radiation present at higher altitudes (Blumthaler et al. 1997). 241
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Our first climate chamber trial with A. montana gave clear evidence that enhanced UV-B 242
radiation did not account for the altitude-dependent differences in secondary metabolite 243
profiles observed in the natural environment. In contrast, when different temperatures were 244
applied under otherwise identical environmental conditions in the second trial, comparable 245
shifts in secondary metabolite profiles were observed as in plants grown in different altitudes 246
in nature. Obviously decreasing mean temperatures observed with increasing altitudes have to 247
be regarded as the key factor for altitudinal changes in secondary metabolite profiles. It is 248
remarkable that only 5°C reduction in the temperature profile applied to experimental plants 249
in our controlled chamber trial had a pronounced and significant effect on their metabolic 250
profile. In view of this observation, interpretations of many earlier experiments either 251
performed in climate chambers under controlled conditions or in natural environments should 252
be carefully re-evaluated taking this new aspect into account. 253
Detailed comparisons of the magnitudes of the observed changes in the climate chamber 254
experiments described here as compared to changes observed in previous field trials (Spitaler 255
et al. 2008) are given in Tables 1-3. The changes observed for the total amounts of caffeic 256
acid derivatives (if any) are the same as observed in field experiments (Spitaler et al. 2008, 257
Table 3). In contrast, the changes in the ratio of ortho-dihydroxy to other flavonoids (Q/K 258
ratio) found in the climate chamber experiments are about two times as high as observed in 259
field experiments for plants collected in the altitudes simulated here (Spitaler et al. 2008, 260
Table 2). However, this fact might be explained by the phenology of A. montana under field 261
conditions. In the field trials flowering heads from A. montana cv. ARBO were harvested at 262
the lowest altitude (590 m a.m.s.l.) at the end of May or in early June, whereas flowering 263
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13
heads from the site closest in altitude to the climate simulated here as high montane (site 5, 264
1430 a.m.s.l.) were on average collected four weeks later. Thus, differences in day and night 265
temperatures during the peak of flowering (and the harvest of flowering heads) were less 266
pronounced than the temperature differences at the different altitudes would imply. Average 267
mean temperatures in Innsbruck for May, June and July are 13.7°C, 16.3°C and 18.3°C, 268
respectively. This increase of 2.0° to 2.6°C per month is about half the expected decrease 269
between altitudes of 600 and 1400 m in the Innsbruck area, which is in the order of 4.8° to 270
5.6°C (8 * 0.6° to 0.7°C per 100 m of altitude) (Ganzera et al. 2008). In conclusion plants 271
growing at the higher altitude sites live in a colder environment than plants in the valley 272
during the peaks of their respective flowering periods but these differences are considerably 273
diminished by the delayed flowering period and in turn the 5°C difference applied in our 274
climate chamber experiment equals more than just a 800 m difference in the altitude of the 275
growing site. 276
Ortho-dihydroxy flavonoids are three- to four-fold better radical scavengers than 277
flavonoids lacking this feature (Rice-Evans et al. 1996) and plants rich in these compounds 278
are therefore better protected against damage by free radicals than plants containing lower 279
amounts of these compounds. The need for the plants in higher altitudes to have additional 280
damage protection against free radicals is not, as assumed previously, mainly driven by the 281
necessity for an improved UV-B protection at higher altitudes (Blumthaler et al. 1997) but 282
stems from the fact that radical scavenging activity of plant phenolics is less effective in low 283
temperature environments than in moderate temperature environments (Bilger et al. 2007). 284
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Practical implications from the data presented here include a) scientific support for and 285
explanation of the old, and mostly passed on by word-of-mouth, alpine myth that plants 286
collected in higher altitudes have a higher "healing potential" (due to the higher amount of 287
bioactive phenolics) than plants collected in low altitudes and b) hints for the systematic 288
cultivation of medicinal plants and vegetables rich in desirable antioxidative constituents (the 289
higher the altitude and/or the cooler the climate the higher the expected yield of antioxidants). 290
Though some key factors on climatic impact on variation in secondary metabolite profiles 291
are becoming clearer with the presented data and with data from recent studies, many 292
interesting questions remain unsolved, for example: Is there a cumulative climatic effect over 293
time? How long have differing temperature regimes to be maintained before changes in 294
secondary metabolite patterns become detectable? After which period of time do differences 295
in secondary metabolite profiles disappear after identical climatic conditions are restored? 296
297
Acknowledgements 298
CZ thanks the Swarovski foundation for financial support. The authors thank Verena 299
Schneeberger (Innsbruck) for technical assistance. 300
301
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condensed tannins of high altitude Pteridium arachnoideum in relation to sunlight 304
exposure, elevation, and rain regime. Biochem Syst Ecol 35:1-10 305
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temperature in the absence of UV-B radiation. Photochem Photobiol Sci 6:190-195 307
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Caldwell MM, Bornman JF, Ballaré CL, Flint SD, Kulandaivelu G (2007) Terrestrial 316
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effects of flower maturity and simulated mechanical harvesting on quality and yield. 323
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Page 18
Table 1 Regression equations for the total amounts of flavonoids in field experiments for the growing seasons 2003 to 2005
and predicted differences between high montane (1400 m) and low montane (600 m) in comparison to simulated high and low
montane climate regimes
Year/Treatment Para-
meter
a b P predicted value
for 600 m site
predicted value
for 1400 m site
percent change
between 1400
and 600 m
2003 nat. soil F 21.2 - 0.00035 0.743 21.0 20.7 - 1.33 %
2004 nat. soil F 18.3 - 0.00116 0.469 17.6 16.7 - 5.27 %
2005 nat. soil F 16.7 0.00161 0.257 17.7 19.0 + 7.29 %
2005 potted F 18.5 0.00024 0.859 18.6 18.9 + 1.03 %
Average F 18.7
( 1.9)
0.000085
( 0.00117)
0.582
( 0.271)
18.7
( 1.6)
18.8
( 1.6)
+ 0.43 %
( 5.26 %)
2007 phytotron
no UV
F - - - 21.1
( 3.8)
20.1
( 4.7)
- 4.74 %
2007 phytotron
ambient UV
F - - - 21.9
( 4.8)
17.9
( 3.7)
- 18.3 %
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19
Table 2 Regression equations for the ration of ortho-dihydroxy (Q) to other flavonoids (K) in field experiments for the growing
seasons 2003 to 2005 and predicted differences between high montane (1400 m) and low montane (600 m) in comparison to
simulated high and low montane climate regimes
Year/Treatment Para-
meter
a b P predicted value
for 600 m site
predicted value
for 1400 m site
percent change
between 1400
and 600 m
2003 nat. soil Q/K 1.03 0.000290 0.001 1.20 1.43 + 19.3 %
2004 nat. soil Q/K 0.721 0.000326 0.000 0.92 1.18 + 28.5 %
2005 nat. soil Q/K 1.05 0.000418 0.000 1.30 1.64 + 25.7 %
2005 potted Q/K 1.21 0.000306 0.016 1.39 1.64 + 17.6 %
Average Q/K 1.00
( 0.20)
0.000335
( 0.000057)
0.004
( 0.008)
1.20
( 0.20)
1.47
( 0.22)
+ 22.8 %
( 5.2 %)
2007 phytotron
no UV
Q/K - - - 1.37
( 0.16)
2.27
( 0.62)
+ 65.7 %
2007 phytotron
ambient UV
Q/K - - - 1.47
( 0.44)
2.13
( 0.36)
+ 44.9 %
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20
Table 3 Regression equations for the total amounts of caffeic acid derivatives in field experiments for the growing seasons
2003 to 2005 and predicted differences between high montane (1400 m) and low montane (600 m) in comparison to simulated
high and low montane climate regimes
Year/Treatment Para-
meter
a b P predicted value
for 600 m site
predicted value
for 1400 m site
percent change
between 1400
and 600 m
2003 nat. soil P 28.2 0.00342 0.032 30.3 33.0 + 9.04 %
2004 nat. soil P 24.4 0.00379 0.108 26.7 29.7 + 11.4 %
2005 nat. soil P 21.7 0.00643 0.001 25.6 30.7 + 20.1 %
2005 potted P 16.5 0.0109 0.000 23.0 31.8 + 37.8 %
Average P 22.7
( 4.9)
0.00614
( 0.00345)
0.035
( 0.051)
26.4
( 3.0)
31.3
( 1.4)
+ 19.6 %
( 13.0 %)
2007 phytotron
no UV
P - - - 38.6
( 8.9)
49.0
( 7.8)
+ 26.9 %
2007 phytotron
ambient UV
P - - - 39.5
( 9.1)
35.4
( 5.2)
- 10.4 %
Page 21
Table 4 Average quantification results for plants grown in climate chambers varying in UV-B
radiation and temperature regimea
Compound common name temp.: high-
montane, no UV-B
temp.: high-
montane, ambient
UV-B
temp.: sub- montane, no UV-B
temp.: sub- montane, ambient
UV-B
x sx x sx x sx x sx
quercetin 3-O--D-glucoside F1 11.71 2.15 10.37 2.90 9.69 1.92 10.52 2.89
patuletin 3-O--D-glucoside F2 1.77 0.30 1.76 0.32 2.48 0.73 2.02 0.21
kaempferol 3-O--D-glucoside F3 2.81 1.22 2.24 0.44 3.35 0.80 3.77 1.93
kaempferol 3-O--D-glucuronide F4 1.95 0.75 1.41 0.42 1.72 0.38 2.15 0.75
6-methoxykaempferol 3-O--D-glucoside
F5
0.72 0.55 0.79 0.36 1.68 0.48 1.41 0.86 hispidulin F6 1.14 0.19 1.36 0.44 2.21 0.30 2.03 0.40 sum of flavonoids F1-F6 ΣF1-F6 20.10 4.67 17.93 3.74 21.13 3.76 21.89 4.76 quotient Q/K =
(F1+F2)/(F3+F4+F5+F6) Q/K 2.27 0.62 2.13 0.36 1.37 0.16 1.47 0.44
chlorogenic acid P1 6.69 1.68 4.38 0.80 4.74 0.76 5.42 1.97 unknown hydroxycinnamate
ester P2
0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 unknown hydroxycinnamate
ester P3
6.38 1.46 5.23 0.84 4.85 1.12 5.83 2.09 3,5-dicaffeoylquinic acid P4 20.24 6.69 10.73 3.07 15.11 2.41 12.71 2.64 1-methoxyoxaloyl-3,5-di-
caffeoylquinic acid P5
8.50 2.39 8.64 1.26 8.22 3.87 8.27 3.35 4,5-dicaffeoylquinic acid P6 2.47 1.07 1.44 0.26 1.85 0.51 1.70 0.60 unknown hydroxycinnamate
ester P7
1.81 0.52 1.83 0.17 1.96 0.59 1.86 0.45 unknown hydroxycinnamate
ester P8
0.79 0.21 0.76 0.37 0.56 0.29 0.67 0.33 unknown hydroxycinnamate
ester P9
2.14 0.69 2.36 0.61 1.29 0.96 3.09 1.45
sum of caffeic acid derivatives P1-P9
ΣP1-P9 49.02 7.84 35.37 5.20 38.58 8.90 39.54 9.20
a Arithmetic means are derived from six samples, which were analyzed three time each.
Page 22
22
Fig. 1 Sample chromatograms from flowering heads of each of the four treatment groups
investigated in the 2007 phytotron experiment: a) high montane, no UV-B (sample AA1); b)
high-montane, ambient UV-B (sample AB7); c) sub-montane, no UV-B (sample AC4), and d)
sub-montane, ambient UV-B (sample AD2).
Fig. 2 Bars represent the contributions of each compound to the total of its compound class
(flavonoid and caffeoyl derivatives, respectively) in percent. Compound abbreviations are
explained in Table 4. Each diagram represents means and standard deviations of the means of
one of the four treatments in the 2007 phytotron experiment: a) high montane, no UV-B; b)
high-montane, ambient UV-B; c) sub-montane, no UV-B, and d) sub-montane, ambient UV-
B.