This study is a contribution to understanding the ways and mechanisms with which tree-stands interact with the environment, forming the micrometeorological regime of the soil-plant-atmosphere system, along with expanding knowledge on the mass and energy exchanges between vegetation and the atmosphere, under the Mediterranean climate conditions. The thesis is focused on the investigation of the micrometeorology of a natural deciduous ecosystem, compared to the weather conditions above, the specification of the interactions between the micrometeorological parameters on a diurnal, seasonal and annual basis (combined with the phenological phases of the vegetation), the differentiation of the micrometeorological regime following a forest fire or logging, the study of the weather effects on the vegetation water requirements and the relationship between water consumption and production, the evaluation of defense and adaptation mechanisms of Mediterranean ecosystems against extreme weather and climate conditions, the evaluation of the forest contribution on CO2 absorption, the study of radiation quantity, quality and distribution in and use by the canopy and finally the study of the ecosystem-environment energy exchanges.
Research was accomplished in a selected natural deciduous oak forest within the region of Corinth, S. Greece, where a well equipped micrometeorological station was placed. The data covers the period 1999-2006 with some missing gaps.
The results of the study show that the main portion of the global solar radiation, Rs and specifically the photosynthetically active radiation, PAR, is captured by the tree-tissues even when there is no foliage. Due to selective absorption of PAR, the light that finally reaches the forest floor is extremely reduced. Logging increases the radiation transmission and reduces reflection and absorption by the canopy, although radiation distributes more uniformly in the foliage. Crawling-fire effect on the optical properties of the ecosystem is rather periodic, because of changes in the properties of the ground only. The seasonal optical properties variation can be used for the accurate identification of the phenological stages of the trees. The exponential radiation model for the radiant energy distribution in the canopy gives satisfactory results, although the deciduous canopy architecture is non uniform.
The temperature and relative humidity profiles inside and over the canopy show an almost mirror effect to each other. During the day, maximum temperature and minimum relative humidity are observed at the top of the forest. Vapor pressure deficit profile is almost identical to that of temperature and vapor pressure, being maximum at the canopy top, reduces with height especially in summer. At night, the temperature and vapor pressure deficit profiles are positive, whereas those of relative humidity and vapor pressure are negative (in all seasons except in winter). Vapor pressure values increase with height in the forest and stabilize above canopy top. The daily temperature range over the ecosystem is relatively small, becoming maximum near the ground, especially at full foliage. The layer of dead leaves covering the forest floor protects roots from frost damage in winter and high temperature and evaporation loss in summer. The period favoring vegetation growth is quite long, but a significant part of it, is characterized by thermal stress.
Logging reduces drought conditions in foliage - by allowing better air mixture - and daily relative humidity range. In extremely low soil moisture conditions (mainly in August) oak trees inhibit their growth. Trees have been adapted to reduced water availability during summer, by developing an extended root system, which allows the exploitation of water in deeper layers. Development over a clay soil layer and formation of a relatively small leaf area increase their ability to survive under the intensive drought Mediterranean conditions. The soil-covering quite thick layer of slowly decomposing dead leaves reduces water losses through evaporation and strengthens vegetation to cope with dry periods.
The wind velocity profile over the canopy follows the typical logarithmic form, day and night. The wind speed values inside the forest (at and below the top) are very small. The canopy roughness parameters, d and zo, take the values 9.6±1.3 m and 1.2±0.9 m, respectively, at full leaf development and 11.2 m and 1.2 m at senescence. Forest surface seems to be very rough, absorbing momentum effectively. Limited tree logging has a negligible effect on wind profile, as vegetation gaps created seem to encourage vertical rather than horizontal air flow.
Net radiation fluxes, Rn, are almost 75% of Rs. Solar radiation is used more effectively during summer than in winter and at midday than at noon or morning. The thermal stress reduces the effective use of radiation but logging seems to increase effectiveness. On a 24 h basis, during the fully leafed period, Rn is composed by 53-56% latent heat, LE, and by 27-30% sensible heat, H. In August, the percentages become 16% and 31%, respectively, under rather extreme dry atmospheric conditions and reduced soil water availability.
The energy absorbed by the canopy (Rn-G) is “consumed” by 81% for H and LE (in June and July), whereas the rest is stored in plant tissues as heat, ΔΗ. ΔH becomes even greater in August, due to water shortage not allowing the productive use of the absorbed solar radiation.
Windspeeds greater than 0.6 m/s favor faster air mixing, reducing LE and H fluxes. However, a speed increase up to 0.6 m/s linearly increases heat fluxes. When trees are fully leafed and during daytime, the Bowen ratio, b, takes values between 0.70-1.67 and most of the time is greater than unit (with smaller values at midday). About 37-67% of the sum (LE+H) is devoted to LE (with lower percentages at midday). Soil heat flux, G, is quite small and gets positive values only a few hours during midday. The evapotranspiration efficiency of PAR absorbed by the ecosystem (ε=LE/PARabs) during the fully leafed period is about 0.69, a relatively small value (compared to similar ecosystems in northern Europe), due to reduced water availability in summer.
The annual water requirements of the ecosystem are about 440 mm, when the annual precipitation in the region is much greater. However, because of its imbalanced time distribution, the trees face water stress in summer, which becomes more intensive in August. The daily mean evapotranspiration rate is maximum in June and July (3.5 mm d-1), with an even greater value at midday (0.43 mm h-1). Under reduced soil water availability (as in August), stomatal resistance increases and water loss reduces rapidly. Stomatal closure is, thus, a defense mechanism that the vegetation calls up under strong drying atmospheric forces. Then, even at midday, the mean evapotranspiration rate is smaller than 0.16 mm h-1.
CO2 absorbance is maximum when the canopy has leaves. In other seasons, the ecosystem is functioning as a source rather than as a sink of carbon. The rates of CO2 absorption are increasing with absorbed radiation fluxes, becoming almost zero when PARabs is lower than 220 W m-2. The annual net carbon uptake by the ecosystem is 6.37 t C ha-1 y-1, when the greater monthly CO2 absorbance is achieved during June and July (mean value 752 g CO2 m-2 month-1) and especially at midday (0.82 g C m-2 h-1). On an annual basis, about 13,500 t CO2 are absorbed by the whole ecosystem (580 ha). Every tree absorbs about 7.3 kg CO2 per year. In August, CO2 absorbance reduces rapidly because of low photosynthetic rates and becomes about half of the maximum (July) values. Water use efficiency (WUE) is about 0.20 mmol H2O/μmol CO2 (water loss of 1 kg produces 3.3 g C). Maximum productive rates are achieved when soil moisture is about 0.35. At lower values CO2 and H2O fluxes reduce almost linearly. Mean daily values of VPD greater than 2 kPa lead to about 50% reduction in productivity.
Although the deciduous ecosystem develops under rather adverse (xerothermic) climatic conditions seems to be quite productive. It has relatively short water needs and developed adaptation (survival) mechanisms, such as the use of morning dew as an additional water source in summer, the root system development for deeper soil water use, the biomass development over a water holding clay soil layer, the evaptoranspiration and photosynthesis reduction under extremely dry conditions via stomatal closure, the development of a relatively small leaf area, the relatively inefficient use of the absorbed by leaves radiation and finally the existence of a thick layer of dead leaves covering the forest floor and protecting the root system against thermal and water stresses.