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How may climate change affect viticulture in Europe?

¿Cómo puede afectar el clima a la viticultura en Europa?
Hans R. Schultz
Institut für Weinbau und Rebenzüchtung
Fachgebiet Weinbau, Forschungsanstalt
Geisenheim, Germany
Global climate change has been a public discussion topic for several years. It is difficult to predict changes in climate and sea level due to the enhancement of the so-called greenhouse effect (including temperature rise, CO2 increase, and nitrogen deposition) but atmospheric CO2 concentration is measurably increasing and is expected to double current levels during the next century with marked effects on current agroclimatic conditions. Man has effectively accelerated global respiration about 10 million! times by the combustion of several billion years worth of accumulated photosynthate and other organic carbon in the course of a few hundred years. Aside global warming, shifts in rates and distribution of precipitation and increases in surface level ultraviolet (UV)-B radiation due to a depletion of the stratospheric ozone layer are among the likely alterations. Since actions and interactions of climatic factors and man-induced changes in for instance vegetation structure are very complex and oceans can act as large buffers on more radical short-term (years) changes, there is great uncertainty about what to expect over the next century. In contrast to research on natural terrestrial ecosystems and some agricultural crops, possible effects of a change in climate on grapevines have largely been ignored.

Possible consequences of increased temperature and altered precipitation patterns on Viticulture in Europe

Using several simulation models, it is generally agreed that global mean surface temperature could rise between 1–4,5 °C depending on the future development of industrial emissions with a best estimate of a near 1,8–2,5 °C warming by the middle of the next century (Carter et al., 1991, Intergovernmental panels on climate change (IPCC) 1992, 1994, 1998, 2001). An increase in temperature of this magnitude in Europe would have profound effects on Viticulture.

In fact current temperature development in the northern hemisphere clearly shows a gradual warming trend in all seasons (fig. 1), especially over the last twenty years (Jones et al., 2001). This warming has been less pronounced than that in the southern hemisphere over the same time period. However, global circulation models (GCM) currently predict a more rapid warming in the northern hemisphere over the next 50 years (Evans, 1996). This would considerably change the margins of suitability for grape growing shifting the northern boundary for Viticulture under this scenario on the order of 10–30 km per decade up to 2020 with a predicted doubling of this rate between 2020 and 2050 (Kenny and Harrison, 1993). This would also profoundly change the distribution of suitable varieties within Europe. Calculations using the Huglin climate index classification (Huglin, 1986) for varietal suitability in Geisenheim, Germany (50 ° latitude North) shows that Riesling, Pinot gris and Pinot noir are suitable cultivars for this location (fig. 2) based on the average climatic conditions over the past 30 years. If suitability would be based on the average temperature development over the next 50 years, cultivars such as Merlot or Cabernet franc become a possible choice (fig. 2). The warming trend can also be demonstrated through the large decrease in the frequency of autumn (October) frost events over the past 100 years (Hoppmann and Hüster, 1988). Indirect estimates of the growth of terrestrial vegetation by use of satellite data from measurements of the normalised difference vegetation index (NDVI) have recently confirmed that plant growth and growing season length is significantly increasing especially in the northern high latitudes (> 45 °N) (Myneni et al., 1997).

Concurrent to global warming are predictions on altered (annual, seasonal) precipitation patterns. For central Europe higher incidence of strong precipitation events in winter, higher frequency of extreme temperatures and less precipitation in summer are among the expected effects (Schönwiese and Rapp, 1997). Significant changes have already occurred over all continents and are predicted to continue based on GCMs for a doubling in CO2 concentration (Hulme et al., 1992). Even if actual precipitation rates and/or their distribution would be unaffected, water evaporation rates will increase due to higher surface temperatures of oceans and land masses. For land masses, changes in evaporation rates may reduce soil moisture on the long term. Some earlier predictions estimated 20-30% reduction in soil moisture in northern Europe, 30 to 50% in western Europe, 20 to 40% in central Europe, 20 to 30% for most of the Mediterranean region and even more for the Iberian peninsula (Stigliani and Salomons, 1992) but these estimates have been doubted recently based on past and current climatic trends (Schönwiese and Rapp, 1997). The impact on Viticulture and the socio-economic consequences would nevertheless be dramatic, especially in southern Europe where water is a scarce resource and irrigation is often not possible. Predictions based on past climatic trends between 1960 and 1990 (not models) show that coastal regions and western Europe in general will receive more precipitation in winter (fig. 3) but less in summer (fig. 4), but these scenarios are not uniform over Europe.

Shifts in precipitation patterns may necessitate introduction of cover crops over winter in order to minimise soil erosion and to maximise water and nutrient storage. Favis-Mortlock (1994)  has shown that an increase in 8-15% rainfall in winter will increase erosion by 27 to 35%. On the other hand, higher frequency of extreme temperatures in summer will automatically lead to increased evapo-transpiration and, coupled with reduced precipitation in summer rainfall areas, may render full or partial use of cover crops impossible in countries such as Germany, Switzerland, or northern Italy where this is currently common practice. In recent years, off-flavour problems in white wine have been linked to competition problems for water and nitrogen between cover crop and grapevines in dry years (Rapp et al., 1993). However, soil erosion and nitrogen leaching coupled to reduced water quality for human consumption may preclude going back to clean cultivation. In other viticultural areas with no summer rain, like the ‘La Mancha’ area south of Madrid in Spain, soil tillage systems also may have to be changed completely. Common practice in these and other comparable regions in Europe is very frequent tillage to avoid capillary rise of water from deeper soil layers and subsequent unproductive evaporation, yet at low soil water content going to a no-tillage system may actually conserve more water.

Changes in soil water is not the only ‘soil’-parameter affected through changes in temperature and precipitation. Soil respiration is positively correlated with an increase in these variables and soil organic matter content will be altered in the long term and may require different ways of soil management practices. Higher winter temperatures coupled with higher relative precipitation in winter as compared to summer will cause large increases in organic matter decay rates. It must also be kept in mind, that concomitantly to the increase in ambient temperature and CO2, some sources predict a large additional deposition of nitrogen, particular in the northern hemisphere.

Influence of elevated carbon dioxide concentration

Although the CO2 concentration may have been close to 20 times the current level at certain times in earth’s history, it remained relatively stable at around 270 ppm over the last 5 centuries (Ehleringer and Cerling, 1995), beginning to rise only after the industrial revolution when human caused CO2 release became significant. The oldest continuous record of direct measurements of CO2 comes from the top of Mauna Loa, Hawaii, which started in 1957 (fig. 5A). The current level of near 370 ppm is more than 30% higher since the industrial revolution 200 years ago and nearly 20% higher since direct measurements began (fig. 5A). Fossil fuel consumption will further increase through the increase in world population, land use, and higher energy consumption per capita. Currently, a person in the United States of America, on average, uses 22 tons of carbon per year, whereas a person in India, for example, uses only 0.7 tons of carbon per year (Bazzaz, 1998), yet it is the developing nations who will contribute dramatically to future CO2 emissions through their development (for a complete list see internet data bank of Carbon Dioxide Information Analysis Centre at Oak Ridge National Laboratory, Tennessee, USA). The global increase in CO2 is thought to occur much faster than plants are capable of genetically adapting to the change and photosynthesis will inevitably be affected. Predictions of how much atmospheric CO2 concentration will rise during the next century differ between different model analyses but most agree on an approximate doubling by the end of this century (fig. 5B), with some scientists speculating that atmospheric CO2 concentration could actually exceed 1000 ppm (Bazzaz, 1998). The direct response of grapevines to a rise in CO2 concentration seems to be similar to the results obtained in most of the studies conducted on annual and perennial plants, where an increase in net photosynthesis, biomass, crop yield, light –nutrient– and water-use efficiency is found (Bindi et al., 1996a). In the short term, photosynthesis and water-use efficiency (ratio of photosynthesis to water consumption) is stimulated by increased CO2 (Schultz, 2000).Grapes grown in arid regions like Spain may therefore be expected to benefit from increased CO2 and may be able to at least partly overcome some of the adverse conditions created by increases in likelyhood and severity of drought events. But on the whole plant level, long term elevated CO2 exposure may have very different effects. The initial increase in photosynthesis may be partly or completely down-regulated if sinks for the manufactured photosynthate are not sufficient so that over a period of days, weeks or months of growth in elevated CO2, the acclimation response may be substantial enough that the photosynthetic rates of plants grown and measured in elevated CO2 may even become equal to those grown at current ambient concentrations (Bazzaz, 1998).

There is regulation at the biochemical, physiological and the molecular level of photosynthesis, and judging from the large differences in vegetative and reproductive development between grape cultivars (Champagnol, 1984), it is likely that sink size and activity will largely affect the responses of different varieties to elevated CO2. Bindi et al. (1996a) in a study using a FACE-system (free air carbon dioxide enrichment in the field) with the variety Sangiovese over several months, found a stronger increase in leaf area (+ 35%) and vegetative dry weight (+ 49%), than in reproductive dry weight (+21%) when CO2 concentration was increased to 700 ppm. The increase in vegetative dry matter was confirmed when simultaneous changes in temperature and solar radiation were additionally considered in running several climate change scenarios and GCMs, but yield response was negative in most cases and more so for Cabernet Sauvignon than for Sangiovese (Bindi et al., 1996b). Faster development of larger leaf areas may in turn have important consequences for water consumption and canopy management, which just points to the difficulty in predicting the combined action of several changing environmental factors.

Can increasing Ultraviolet radiation levels affect grapevine physiology and grape composition?

Increasing UV-B radiation can be damaging for terrestrial organisms. The UV-B wavelength band ranges from 280 nm to 320 nm, though only wavelengths greater than 290 nm can reach the Earth’s surface. In sunlight, the ratio of UV-B to photosynthetically active radiation (PAR; 400-700 nm) fluctuates, primarily caused by changes in solar angle and thickness of the ozone layer. Depletion of the ozone layer results from emissions of halogenated chemicals, such as chlorofluorocarbons (also called halocarbons) and decreases the effectiveness for UV-B screening (Tevini, 1996). Stratospheric ozone levels are near their lowest point since measurements began. Changes over the past decades are difficult to quantify because of lack of suitable historical data. Estimates range from an average increase of about 8% per decade (Blumthaler and Ambach, 1990) at high altitudes to 4-7% since 1970 for the Northern Hemisphere and 130% for the Antarctica in spring (Madronich et al., 1998). However, the temporal and spatial variation due to cloud cover, atmospheric pollutants and surface albedo is very large. Based on satellite observations monthly deviations from these mean values can reach up to near +40% under clear sky conditions for latitudes between the 30th and 50th degree North (McPeters et al., 1996), where almost all grapes are grown in Europe. Additionally, seasonal fluctuations may largely exceed the average increase in UV-radiation and are likely to cause significant biological damage.

Increased UV-B can be damaging to terrestrial organisms including plants and microbes, but these organisms also have protective and repair mechanisms. The impact of UV-B on the morphological, physiological and biochemical features of higher plants has been extensively studied and foremost decreases of leaf expansion (Tevini and Teramura, 1989), fresh and dry weight, total biomass and photosynthetic capacity have been noted (Krupa and Jäger, 1996). UV-B responses may not remain instantaneous and effects could accumulate from year to year in long-lived perennial plants such as trees (Madronich et al., 1998) and thus there is a chance that this may also occur in grapevines.

Increases in UV-absorbing compounds seem to be a general reaction to increased UV-B radiation (Tevini, 1996; Jansen et al., 1998). The stimulation of these compounds is primarily intended to reduce UV-radiation penetration into plants and other organisms. For instance the formation of yellow and red pigments has been shown to significantly reduce the penetration of UV-light into nectarine fruit (Blanke, 1996). Some key-enzymes involved in flavonoid biosynthesis (chalcone synthase) and the phenyl-propanoid pathway (phenylalanine ammonium-lyase) have been shown to be upregulated by UV-radiation, as are levels of key antioxidants glutathione and ascorbate (Jansen et al., 1998), whereas carotenoid pigment formation and the incorporation of nitrogen into amino acids (AA) can be inhibited (Döhler et al., 1995; Jansen et al., 1998). Since components such as flavonoids, amino acids and carotenoids are important constituents of grapes with a marked effect on flavour development, some influence of UV-B radiation on grape composition can be expected (Schultz et al., 1998) (table 1).

Table 1 Some known effects of UV-B radiation and their possible relevance for grape production

UV-B effects

Possible relevance for grape production

• activation of genes of the phytopropanoid pathway

accumulation of flavonoids and anthocyanins (colour formation, wine composition)

• inactivation (damage) of photosystem II and of photosynthetic enzymes

decreased photosynthesis

• reduced chlorophyll and carotenoid concentrations

decreased photosynthesis,

altered aroma compounds?

(vitispirane, 1,1,6-trimethyl-1,2-dihydronaphtalene, TDN, ß-damascenone)?

xanthophylls, leaf and berry energy balance?

• effects on nitrogen metabolism (via carbon supply or direct effects on key enzymes)

decreased amino acid concentration (yeast metabolism, fermentation kinetics, higher alcohol formation, secondary aromatic compounds)

• thicker leaves, wax composition

more disease resistance

• photo-oxidation of indole acetic acid (IAA, auxin),  UV-B absorption by tryptophan

possible formation of o-aminoacetophenone (off-flavour in white wines)

• increase in ascorbic acid and glutathione content through the formation of free radicals

photoprotection, sulfur metabolism, induction of enzyme activities (important for yeast metabolism)?

• flowering and phenology

may be affected in some varieties

• alterations in soil microflora and fauna

nutrient availability

Additionally, on the molecular level, UV-B can destruct peptides and lipids and can photo-degrade the plant hormone auxin which absorbs in the UV-B range and may play a significant role in the formation of an off-flavour in white wines increasingly found over the last decade in Central Europe (Geßner et al., 1999) (table 1).

In a field trial with different levels of UV-radiation we found both amino acid (AA) and carotenoid concentration at harvest to be substantially reduced under current level ambient UV-B radiation in berry skins of the cultivar White Riesling (Schultz et al., 1998). Additionally, AA composition was altered under UV-B radiation, exhibiting lower levels of arginine and glutamine, the main sources of AA for yeast metabolism. Several authors suggested that the difference between the carotenoid level at the onset of ripening and that at harvest indicates the formation of norisoprenoids (Razungles et al., 1993; Bureau et al., 1998). These compounds have been linked to the ageing flavour of wines (vitispirane, 1,1,6-trimethyl-1,2-dihydronaphtalene, TDN) and the fruity character of must and wine (damascenone). Thus the response to UV-light may not be exclusively negative, but our current knowledge on this subject is still very limited. The great challenge in the future will be to predict the responses of grapevines to simultaneously changing climatic components and to develop adequate strategies to overcome potential problems.


Bazzaz F.A.: «Elevated CO2 and Plant Productivity in the 21st Century: Can we feed billions and preserve biological diversity?», In: Photosynthesis: Mechanisms and Effects, Vol. V, Ed G. Garab Kluwer Academic Publishers, 1998: 3923-3940.

Bindi M., Fibbi L., Gozzini B., Orlandini S., Seghi L.: «The effect of elevated CO2 concentration on grapevine growth under field conditions», Acta Horticulturae 1996a; 427: 325-330.

Bindi M., Fibbi L., Gozzini B., Orlandini S., Miglietta F.: «Modelling the impact of future climate scenarios on yield and yield variability of grapevine», Climate Research 1996b; 7: 213-224.

Blanke M.M.: «Transmission of UV-Irradiance into Nectarine Fruit», Angew Bot 1996; 70: 76-77.

Blumenthaler M., Ambach W.: «Indications of increasing solar ultraviolet-B radiation flux in alpine regions», Science 1990; 248: 206-208.

Bureau S.M., Razungles A.J., Baumes R.L., Bayonove C.L.: «Effect of vine or bunch shading on the carotenoid composition in Vitis vinifera L. berries. I. Syrah grapes», Vit Enol Sci 1998; 53: 64-71.

Carter T.R., Parry M.L., Porter J.H.: «Climatic change and future agroclimatic potential in Europe», Journal of Climatology 1991; 11: 251-269.

Champagnol F.: Eléments de physiologie de la vigne et de viticulture générale, Imprimerie DEHAN, Montpellier, 1984.

Döhler G., Hagmeier E., David C.: «Effects of solar and artificial UV irradiation on pigments and assimilation of 15N ammonium and 15N nitrate by macroalgae», Journal of Photochemistry and Photobiology B: Biology 1995; 30: 179-187.

Evans T.E.: «The Effects of Changes in the World Hydrological Cycle on the Availability of Water Resources», In: Global Climate Change and Agricultural Production, Eds. F. Bazzaz and W. Sombroek, John Wiley and Sons, Chichester, 1996: 15-48.

Ehleringer J.R., Cerling T.E.: «Atmospheric CO2 and the ratio of intercellular to ambient CO2 concentrations in plants», Tree Physiol 1995; 15: 105-111.

Favis-Mortlock D.: «Modelling soil erosion on UK agricultural land under a changed climate», In: Soil Responses to Climate Change, NATO ASI Series. Vol. 23. Eds. M.D.A Rounsevell and P.J. Loveland, Springer Verlag, Berlin, 1994: 211-216.

Geßner M., Köhler H.J., Christoph N.: «Die “untypische Alterungsnote” im Wein VIII», Rebe und Wein 1999; 8: 264-267.

Hoppmann D., Hüster H.: (1988) «100 Jahre Klimabeobachtungen im Rheingau», Wein-Wissenschaft 1988 ; 43 : 147-160.

Huglin P.: Biologie et écologie de la vigne, Payot, Lausanne, Switzerland, 1986.

Hulme M., Marsh R., Jones P.P.: «Global changes in a humidity index between 1931-1960 and 1961-1990», Climate Research 1992; 2: 1-22.

Jansen M.A.K., Gaba V., Greenberg B.: «Higher plants and UV-B radiation: Balancing damage, repair and acclimation», Trends in Plant Science 1998; 4: 131-135.

Jones P.D., Parker D.E., Osborn T.J., Briffa K.R.: «Global and hemispheric temperature anomalies-land and marine instrumental records», In: Trends: A Compendium of Data on Global Change. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, U.S Department of Energy ´, Oak Ridge, Tenn., USA.

Kenny G.H., Harrison P.A.: «The effects of climatic variability and change on grape suitability in Europe», Journal of Wine Research 1993; 4: 163-183.

Krupa S.V., Jäger H.J.: «Adverse effects of elevated levels of ultraviolet (UV)-B radiation and ozone (O3) on crop growth and productivity», In: Global Climate Change and Agricultural Production, Eds. F. Bazzaz and W. Sombroek, John Wiley and Sons, Chichester, 1996: 141-169.

Madronich S., McKenzie R.L., Björn L.O., Caldwell M.M.: «Changes in biologically active ultraviolet radiation reaching the Earth`s surface», In: Environmental effects of ozone depletion: 1998 Assessment, United Nations Environmental Programme. Eds. J.C. van der Leun, X. Tang and M. Tevini, UNEP, Nairobi, Kenya, 1998.

McPeters R.D., Hollandsworth S.M., Flynn L.E., Herman J.R., Seftor C.J.: «Long-term ozone trends derived from the 16-year combined Nimbus7/Meteor 3 TOMS Version record», Geophysical Research Letters 1996; 23: 3699-3702.

Myneni R.B., Keeling, C.D., Tucker, C.J., Asrar, G., Nemani, R.R. (1997) Increased plant growth in the northern high latitudes from 1981 to 1991. Nature, 386, 698-702.

Rapp, A., Versini, G. and Ullemeyer, H. (1993) 2-Aminoacetophenon: Verursachende Komponente der “Untypischen Alterungsnote” (Naphtalinton, Hybridton) bei Wein. Vitis 32, 61-62.

Razungles A., Gunata Z., Pinatel S., Baumes R., Bayonove C.: «Étude quantitative de composés terpénique, norisoprénoïdes et leurs précurseurs dans diverses variétés de raisins», Sciences des Aliments 1993 ; 13 : 59-72.

Schönwiese C.D., Rapp J.: Climate Trend Atlas of Europe – Based on Observations 1891-1990, Kluwer, Dordrecht, 1997.

Schultz H.R., Löhnertz O., Bettner W., Bálo B., Linsenmeier A., Jähnisch A., Müller M., Gaubatz B., Váradi G.: «Is grape composition affected by current levels of UV-B radiation?», Vitis 1998; 37: 191-192.

Schultz H.R.: «Climate Change and viticulture: A European perspective on climatology, carbon dioxide and UV-B effects», Australian Journal of Grape and Wine Research 2000; 6: 2-12.

Stigliani B., Salomons W.: Pollutants and some not impossible environmental problems caused by climate change, IIASA, Laxenburg, Austria, 1992: 1-15.

Tevini M.: «Erhöhte UV-B Strahlung: Ein Risiko für Nutzpflanzen?», Biologie unserer Zeit 1996; 26: 245-254.

Várallyay G.: «Climate change, soil salinity and alkalinity», In: Soil Responses to Climate Change. NATO ASI Series. Vol. 23. Eds M.D.A Rounsevell and P.J.Loveland, Springer Verlag, Berlin, 1994: 39-54.

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