Article

Review of dew action effect on plants

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Abstract

Dew is one of the important water resources on the earth and is beneficial to the survival, growth and development of the plants based on the arid and semiarid environment. The disputed effects of dew on plants, beneficial and harmful, were reviewed in this study. The beneficial effects mainly consist of five aspects: (1) Supplying important water resource. In the arid and semiarid regions or in the dry season, dew is the main or the only water resource because of its higher frequency and sustaining time comparing with the precipitation, which keeps the organic synthesis and metabolism, accelerates the increase of biomass in plants. (2) Regulating inner water of plants. The function of dew on regulating inner water of plants includes the following several aspects based on related studies: helping plant to rapidly activate photosynthetic activity during desiccation and rehydration; supplying a moisture environment in repairing embryo DNA of seeds, maintaining seed viability under harsh desert conditions; regulating the transpiration pressure and helping the wilting plant arrive a higher steady restoration state; etc. (3) Improving water balance of soil. There is an indirect effect of dew on plant through improving water balance of soil. On one hand, dew forms on the soil surface or drops into the soil from the nearby plants, becoming an importing water resource. On the other hand, the soil evaporation decreases along with dew event appears, leading a mitigation of soil water tension to some extent. (4) Regulating growing environment of forest plants. The regulation effect appears on canopy firstly, and then into the forest. Dew deposition increases the water resource of forest, improves its water cycle. Along with the dew deposition and evaporation, the forest micro-climate changes, especially the wind speed, moisture and heat. Dew, as a medium, is concerned with the water-heat exchange process of the forest. (5) Dew was used widely in the performing process of foliage dressing, defoliant and pesticide for its characteristics including small dew amount, long time sustaining on objects, leading an accreting of long time, extending the time of sterilization. The harmful effects mainly consist of two aspects: (1) Inducing plant disease. The pathogen of fungus and bacteria releases spores and infects the host plant under a moisture condition, and induces plant disease easily, thus dew supplies opportunities for pathogen. The infection intensity differs from the differences of dew quantity and sustaining time. (2) Reducing output and quality of crops. The influence on the output and quality of crops is related to the quantity, sustaining time, acidification level of dew. The plant stomata movement was inhibited and the route of pollen diffusing was discouraged when the quantity and sustaining time of dew arrive at a higher level. Acid dew could lead to a degradation of vegetation for the decreasing of CO2 assimilation efficiency. Furthermore, the black spot disease of fruit could be induced by dew. The main problems in related researches were also pointed out in present paper. For example, the information of dew action effect on plants was absent; few documents referred to the changing environment, such as urban heat island and the polluted atmosphere etc; researches of dew on plant diversity and the use on biological control were lack. Future studies were recommended to (1) researches of the action effect and mechanisms of dew on plants; (2) researches on the interactions of dew and plants based on the interferential factors including acid dew and the urban heat island effect; (3) researches of the influence of dew on the plant diversity; (4) applied researches on controlling harmful plants using dew.

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Cations (pH, potassium, sodium, calcium, magnesium, and ammonium) and anions (sulfate, nitrate, nitrite, and chloride) concentrations were measured in Santiago city rain and dew waters collected during the 1995 to 1999. Concentrations measured in dews are considerably higher than those measured in rains. The high ionic concentration present in dew waters could contribute to their corrosion potential. Natural dust makes an important contribution to the ions present in dews, but the presence of rather high sulfate concentrations (up to 900 μeq/l) indicate a significant contribution of anthropogenic sources.A peculiar characteristic of dew waters is the relatively high nitrite concentrations (up to 180 μeq/l). This nitrite can be resuspended into the boundary layer after dew water evaporation, possibly due to the relatively high volatily of ammonium nitrite. This upward flux could constitute an important source of hydroxyl radicals in the early morning, contributing so to the initial steps of the observed photochemical smog.
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Dew is an important water source for desert organisms in semiarid and arid regions. Both field and laboratory experiments were conducted to investigate the possible roles of dew in growth of biomass and photosynthetic activity within cyanobacterial crust. The cyanobacteria, Microcoleus vaginatus Gom. and Scytonema javanicum (Kütz.) Born et Flah., were begun with stock cultures and sequential mass cultivations, and then the field experiment was performed by inoculating the inocula onto shifting sand for forming cyanobacterial crust during late summer and autumn of 2007 in Hopq Desert, northwest China. Measurements of dew amount and Chlorophyll a content were carried out in order to evaluate the changes in crust biomass following dew. Also, we determined the activity of photosystem II(PSII) within the crust in the laboratory by simulating the desiccation/rehydration process due to dew. Results showed that the average daily dew amount as measured by the cloth-plate method (CPM) was 0.154 mm during fifty-three days and that the crust biomass fluctuated from initial inoculation of 4.3 μg Chlorophyll a cm−2 sand to 5.8–7.3 μg Chlorophyll a cm−2 crust when dew acted as the sole water source, and reached a peak value of approximately 8.2 μg Chlorophyll a cm−2 crust owing to rainfalls. It indicated that there was a highly significant correlation between dew amounts and crust moistures (r = 0.897 or r = 0.882, all P < 0.0001), but not a significant correlation between dew and the biomass (r = 0.246 or r = 0.257, all P > 0.05), and thus concluded that dew might only play a relatively limited role in regulating the crust biomass. Correspondingly, we found that rains significantly facilitated biomass increase of the cyanobacterial crust. Results from the simulative experiment upon rehydration showed that approximately 80% of PSII activity could be achieved within about 50 min after rehydration in the dark and at 5 °C, and only about 20% of the activity was light-temperature dependent. This might mean that dew was crucial for cyanobacterial crust to rapidly activate photosynthetic activity during desiccation and rehydration despite low temperatures and weak light before dawn. It also showed in this study that the cyanobacterial crusts could receive and retain more dew than sand, which depended on microclimatic characteristics and soil properties of the crusts. It may be necessary for us to fully understanding the influence of dew on regulating the growth and activity of cyanobacterial crust, and to soundly evaluate the crust's potential application in fighting desertification because of the available water due to dew.
Article
Black Sigatoka is an important fungal disease of bananas and plantains. Dew duration on the upper leaves of these plants (Leaves 0 and 1) is an important factor in the development of the disease. A general dew estimation scheme, based on an energy budget approach, was adapted to the particular case of banana and plantain upper leaves in order to provide a tool for Black Sigatoka management. This scheme allows the estimation of dew duration from standard weather station measurements of air temperature and humidity, wind velocity, solar radiation and cloud cover. Values of dew duration estimated by this scheme were compared with observed values on plantain during 18 nights. On average, the differences between observed and estimated values were less than 1 h.