Journal articles: 'Ecophysiology'

1

Lüttge, Ulrich, and Fabio R. Scarano. "Ecophysiology." Revista Brasileira de Botânica 27, no. 1 (March 2004): 1–10. http://dx.doi.org/10.1590/s0100-84042004000100001.

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2

Jones, Hamlyn G. "Ecophysiology." Trends in Plant Science 1, no. 4 (April 1996): 129–30. http://dx.doi.org/10.1016/s1360-1385(96)90009-6.

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3

Collins, Chris. "Plant ecophysiology." Crop Protection 17, no. 2 (March 1998): 185. http://dx.doi.org/10.1016/s0261-2194(97)00106-3.

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4

Robinson, David. "Comparative ecophysiology?" New Phytologist 146, no. 3 (June 2000): 389–90. http://dx.doi.org/10.1046/j.1469-8137.2000.00655.x.

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5

Humphreys, Mike W. "Plant ecophysiology." New Phytologist 155, no. 2 (August 2002): 202–3. http://dx.doi.org/10.1046/j.1469-8137.2002.00461_4.x.

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6

Boyd, C. E. "Fish ecophysiology." Aquaculture 114, no. 3-4 (August 1993): 361–62. http://dx.doi.org/10.1016/0044-8486(93)90312-m.

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7

Berlinsky, David. "Fish ecophysiology." Aquatic Toxicology 30, no. 4 (December 1994): 381–82. http://dx.doi.org/10.1016/0166-445x(94)00055-7.

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8

Merrett, P. "Ecophysiology of Spiders." Journal of Arid Environments 13, no. 1 (July 1987): 91a—92. http://dx.doi.org/10.1016/s0140-1963(18)31157-1.

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9

De Costa, W. A. Janendra M., A. Janaki Mohotti, and Madawala A. Wijeratne. "Ecophysiology of tea." Brazilian Journal of Plant Physiology 19, no. 4 (December 2007): 299–332. http://dx.doi.org/10.1590/s1677-04202007000400005.

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Tea [Camellia sinensis (L.) O. Kuntze] is one of the most important beverage crops in the world. The major tea-growing regions of the world are South-East Asia and Eastern Africa where it is grown across a wide range of altitudes up to 2200 m a.s.l.. This paper reviews the key physiological processes responsible for yield determination of tea and discusses how these processes are influenced by genotypic and environmental factors. Yield formation of tea is discussed in terms of assimilate supply through photosynthesis and formation of harvestable sinks (i.e. shoots). The photosynthetic apparatus and partial processes (i.e. light capture, electron transport and carboxylation) of tea show specific adaptations to shade. Consequently, maximum light-saturated photosynthetic rates of tea are below the average for C3 plants and photoinhibition occurs at high light intensities. These processes restrict the source capacity of tea. Tea yields are sink-limited as well because shoots are harvested before their maximum biomass is reached in order to maintain quality characters of made tea. In the absence of water deficits, rates of shoot initiation and extension are determined by air temperature and saturation vapour pressure deficit, with the former having positive and the latter having negative relationships with the above rates. During dry periods, when the soil water deficit exceeds a genotypically- and environmentally-determined threshold, rates of shoot initiation and extension are reduced with decreasing shoot water potential. Tea yields respond significantly to irrigation, a promising option to increase productivity during dry periods, which are experienced in many tea-growing regions.

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Duffey, Eric. "Ecophysiology of spiders." Biological Conservation 43, no. 3 (1988): 242–43. http://dx.doi.org/10.1016/0006-3207(88)90117-6.

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11

Bartak, M., V. Dvorak, J. Kalina, J. A. Bourret, L. Burketova, M. Cervena, F. Fric, et al. "Section 1 - Ecophysiology." Biologia plantarum 34, Suppl.1 (January 1, 1992): 489–95. http://dx.doi.org/10.1007/bf02930802.

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12

Aktan, N., N. Palavan-Unsal, A. V. Andonov, K. M. Georgieva, I. T. Yordanov, L. Atanasiu, E. Petcu, et al. "Session 17 Ecophysiology." Biologia plantarum 36, Suppl.1 (January 1, 1994): S257—S307. http://dx.doi.org/10.1007/bf02931129.

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13

Tomasi, Thomas E., Briana N. Anderson, and Theodore Garland. "Ecophysiology of mammals." Journal of Mammalogy 100, no. 3 (May 23, 2019): 894–909. http://dx.doi.org/10.1093/jmammal/gyz026.

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14

Senger, Horst. "Ecophysiology of photosynthesis." Journal of Photochemistry and Photobiology B: Biology 28, no. 2 (May 1995): 175. http://dx.doi.org/10.1016/1011-1344(95)90135-3.

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15

Lombard, Fabien, Florent Renaud, Christopher Sainsbury, Antoine Sciandra, and Gabriel Gorsky. "Appendicularian ecophysiology I." Journal of Marine Systems 78, no. 4 (November 2009): 606–16. http://dx.doi.org/10.1016/j.jmarsys.2009.01.004.

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16

Kapos, Valerie, S. S. Mulkey, R. L. Chazdon, and A. P. Smith. "Tropical Forest Plant Ecophysiology." Journal of Applied Ecology 34, no. 3 (June 1997): 831. http://dx.doi.org/10.2307/2404930.

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17

Hawthorne, William D., S. S. Mulkey, R. L. Chazdon, and A. P. Smith. "Tropical Forest Plant Ecophysiology." Journal of Ecology 85, no. 1 (February 1997): 105. http://dx.doi.org/10.2307/2960636.

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18

Skillman, John, Stephen S. Mulkey, Robin L. Chazdon, and Alan P. Smith. "Tropical Forest Plant Ecophysiology." Ecology 78, no. 3 (April 1997): 965. http://dx.doi.org/10.2307/2266080.

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19

Santos Matos, Fábio. "Ecophysiology Of Leaf Senescence." Agronomy & Agricultural Science 3, no. 1 (March 13, 2020): 1–6. http://dx.doi.org/10.24966/aas-8292/100020.

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20

Baird, Donald J., T. Braunbeck, W. Hanke, and H. Segner. "Fish Ecotoxicology and Ecophysiology." Journal of Animal Ecology 63, no. 4 (October 1994): 1007. http://dx.doi.org/10.2307/5279.

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21

Morison, J. I. L. "P3 General Plant Ecophysiology." Journal of Experimental Botany 47, supp1 (May 1, 1996): 37–48. http://dx.doi.org/10.1093/oxfordjournals.jxb.a022914.

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22

Kolb, Thomas E. "ecophysiology of coniferous forests." Forest Ecology and Management 82, no. 1-3 (April 1996): 254. http://dx.doi.org/10.1016/s0378-1127(96)90010-9.

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23

Spellerberg, Ian F. "Ecophysiology of Desert Vertebrates." Journal of Arid Environments 17, no. 3 (November 1989): 357–58. http://dx.doi.org/10.1016/s0140-1963(18)30892-9.

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24

Cloudsley-Thompson, J. L. "Ecophysiology of Desert Reptiles." Journal of Arid Environments 15, no. 2 (November 1988): 215. http://dx.doi.org/10.1016/s0140-1963(18)30995-9.

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25

Turner, Ian M. "Tropical forest plant ecophysiology." Trends in Ecology & Evolution 11, no. 12 (December 1996): 518–19. http://dx.doi.org/10.1016/0169-5347(96)88904-x.

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26

Bickford, Christopher P. "Ecophysiology of leaf trichomes." Functional Plant Biology 43, no. 9 (2016): 807. http://dx.doi.org/10.1071/fp16095.

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This review examines how leaf trichomes influence leaf physiological responses to abiotic environmental drivers. Leaf trichomes are known to modulate leaf traits, particularly radiation absorptance, but studies in recent decades have demonstrated that trichomes have a more expansive role in the plant–environment interaction. Although best known as light reflectors, dense trichome canopies modulate leaf heat balance and photon interception, and consequently affect gas exchange traits. Analysis of published studies shows that dense pubescence generally increases reflectance of visible light and near-infrared and infrared radiation. Reflective trichomes are also protective, reducing photoinhibition and UV-B related damage to leaf photochemistry. Little support exists for a strong trichome effect on leaf boundary layer resistance and transpiration, but recent studies indicate they may play a substantive role in leaf water relations affecting leaf wettability, droplet retention and leaf water uptake. Different lines of evidence indicate that adaxial and abaxial trichomes may function quite differently, even within the same leaf. Overall, this review synthesises and re-examines the diverse array of relevant studies from the past 40 years, illustrating our current understanding of how trichomes influence the energy, carbon and water balance of plants, and highlighting promising areas for future research.

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27

Gloser, J. "Ecophysiology of Tropical Intercropping." Biologia plantarum 38, no. 4 (December 1, 1996): 562. http://dx.doi.org/10.1007/bf02890607.

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28

Kirst, Gunter O., and Christian Wiencke. "ECOPHYSIOLOGY OF POLAR ALGAE." Journal of Phycology 31, no. 2 (April 1995): 181–99. http://dx.doi.org/10.1111/j.0022-3646.1995.00181.x.

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29

Shu, Fukai. "Ecophysiology of tropical intercropping." Field Crops Research 47, no. 1 (July 1996): 78–79. http://dx.doi.org/10.1016/0378-4290(96)81478-x.

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30

Sayer, M. D. J. "Fish: Ecotoxicology and ecophysiology." Journal of Experimental Marine Biology and Ecology 173, no. 2 (November 1993): 294–95. http://dx.doi.org/10.1016/0022-0981(93)90061-r.

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31

Przybyłowicz, W. J., J. Mesjasz-Przybyłowicz, P. Migula, M. Nakonieczny, M. Augustyniak, M. Tarnawska, K. Turnau, et al. "Micro-PIXE in ecophysiology." X-Ray Spectrometry 34, no. 4 (2005): 285–89. http://dx.doi.org/10.1002/xrs.826.

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32

Duan, Chensong, Zhifeng Wu, Hu Liao, and Yin Ren. "Interaction Processes of Environment and Plant Ecophysiology with BVOC Emissions from Dominant Greening Trees." Forests 14, no. 3 (March 7, 2023): 523. http://dx.doi.org/10.3390/f14030523.

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In global greening, biogenic volatile organic compound (BVOC) emissions and their influencing factors have been considered due to their significant roles in the biosphere and atmosphere. Many studies have reported relationships of BVOC emissions with environmental factors and plant ecophysiology. However, the direct and indirect effects of environmental factors on BVOC emissions remain unclear, and the causal relationships between plant ecophysiology and BVOC emissions are ambiguous. We measured the isoprene and monoterpene emissions from dominant greening plants using a dynamic enclosure system and quantified the interactions of environment–-plant and ecophysiology–BVOC emissions using a path analysis model. We found that isoprene emission was directly affected by photosynthetic rate, and indirectly affected by photosynthetically active radiation and air temperature (Tair). Monoterpene emissions were directly affected by atmospheric pressure, relative air humidity and specific leaf weight, and indirectly affected by Tair.

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33

Miller-Goodman, Mary S. "Grassland Ecophysiology and Grazing Ecology." Crop Science 42, no. 3 (2002): 981. http://dx.doi.org/10.2135/cropsci2002.0981.

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34

Crafts‐Brandner, Steven J. "Handbook of Plant Ecophysiology Techniques." Crop Science 42, no. 4 (July 2002): 1387–88. http://dx.doi.org/10.2135/cropsci2002.1387a.

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35

Miller‐Goodman, Mary S. "Grassland Ecophysiology and Grazing Ecology." Crop Science 42, no. 3 (May 2002): 981–82. http://dx.doi.org/10.2135/cropsci2002.9810.

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36

Close, Dugald C., and Christopher L. Beadle. "The Ecophysiology of Foliar Anthocyanin." Botanical Review 69, no. 2 (April 2003): 149–61. http://dx.doi.org/10.1663/0006-8101(2003)069[0149:teofa]2.0.co;2.

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37

Campostrini, Eliemar, and David M. Glenn. "Ecophysiology of papaya: a review." Brazilian Journal of Plant Physiology 19, no. 4 (December 2007): 413–24. http://dx.doi.org/10.1590/s1677-04202007000400010.

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Papaya (Carica papaya L.) is a principal horticultural crop of tropical and subtropical regions. Knowledge of how papaya responds to environmental factors provides a scientific basis for the development of management strategies to optimize fruit yield and quality. A better understanding of genotypic responses to specific environmental factors will contribute to efficient agricultural zoning and papaya breeding programs. The objective of this review is to present current research knowledge related to the effect of environmental factors and their interaction with the photosynthetic process and whole-plant physiology. This review demonstrates that environmental factors such as light, wind, soil chemical and physical characteristics, temperature, soil water, relative humidity, and biotic factors such as mycorrhizal fungi and genotype profoundly affect the productivity and physiology of papaya. An understanding of the environmental factors and their interaction with physiological processes is extremely important for economically sustainable production in the nursery or in the field. With improved, science-based management, growers will optimize photosynthetic carbon assimilation and increase papaya fruit productivity and quality.

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38

Almeida, Alex-Alan F. de, and Raúl R. Valle. "Ecophysiology of the cacao tree." Brazilian Journal of Plant Physiology 19, no. 4 (December 2007): 425–48. http://dx.doi.org/10.1590/s1677-04202007000400011.

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Cacao, one of the world's most important perennial crops, is almost exclusively explored for chocolate manufacturing. Most cacao varieties belong to three groups: Criollo, Forastero and Trinitario that vary according to morphology, genetic and geographical origins. It is cropped under the shade of forest trees or as a monocrop without shade. Seedlings initially show an orthotropic growth with leaf emission relatively independent of climate. The maturity phase begins with the emission of plagiotropic branches that form the tree crown. At this stage environmental factors exert a large influence on plant development. Growth and development of cacao are highly dependent on temperature, which mainly affects vegetative growth, flowering and fruit development. Soil flooding decreases leaf area, stomatal conductance and photosynthetic rates in addition to inducing formation of lenticels and adventitious roots. For most genotypes drought resistance is associated with osmotic adjustment. Cacao produces caulescent flowers, which begin dehiscing in late afternoon and are completely open at the beginning of the following morning releasing pollen to a receptive stigma. Non pollinated flowers abscise 24-36 h after anthesis. The percentage of flowers setting pods is in the range 0.5 - 5%. The most important parameters determinants of yield are related to: (i) light interception, photosynthesis and capacity of photoassimilate distribution, (ii) maintenance respiration and (iii) pod morphology and seed fermentation, events that can be modified by abiotic factors. Cacao is a shade tolerant species, in which appropriate shading leads to relatively high photosynthetic rates, growth and seed yield. However, heavy shade reduces seed yield and increases incidence of diseases; in fact, cacao yields and light interception are tightly related when nutrient availability is not limiting. High production of non-shaded cacao requires high inputs in protection and nutrition of the crop. Annual radiation and rainfall during the dry season explains 70% of the variations in annual seed yields.

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39

Wilkins, R. J. "Grassland Ecophysiology and Grazing Ecology." Grass and Forage Science 56, no. 2 (June 29, 2001): 201–2. http://dx.doi.org/10.1046/j.1365-2494.2001.00256.x.

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40

Jones, H. G., N. Archer, E. Rotenberg, and R. Casa. "Radiation measurement for plant ecophysiology." Journal of Experimental Botany 54, no. 384 (March 1, 2003): 879–89. http://dx.doi.org/10.1093/jxb/erg116.

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41

Buskirk, Ruth E. "Ecophysiology of Spiders. Wolfgang Nentwig." Quarterly Review of Biology 62, no. 4 (December 1987): 452. http://dx.doi.org/10.1086/415670.

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42

Südekum, Karl-Heinz. "Grassland Ecophysiology and Grazing Ecology." Animal Feed Science and Technology 94, no. 3-4 (December 2001): 208–9. http://dx.doi.org/10.1016/s0377-8401(01)00291-7.

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43

FEILD, TAYLOR S., and NAN CRYSTAL ARENS. "The ecophysiology of early angiosperms." Plant, Cell & Environment 30, no. 3 (January 11, 2007): 291–309. http://dx.doi.org/10.1111/j.1365-3040.2006.01625.x.

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44

Lamont, Byron B., Roy Wittkuhn, and Dylan Korczynskyj. "Ecology and ecophysiology of grasstrees." Australian Journal of Botany 52, no. 5 (2004): 561. http://dx.doi.org/10.1071/bt03127.

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‘Xanthorrhoea…is in habit one of the most remarkable genera of Terra Australis, and gives a peculiar character to the vegetation of that part of the country where it abounds’ Robert Brown (1814). Grasstrees (arborescent Xanthorrhoea, Dasypogon, Kingia), with their crown of long narrow leaves and blackened leafbase-covered trunk (caudex), are a characteristic growth form in the Australian flora. Xanthorrhoea is the most widespread genus, with 28 species that are prominent from heathlands to sclerophyll forests. While leaf production for X. preissii reaches a peak in spring–summer, growth never stops even in the cool winter or dry autumn seasons. Summer rain, accompanied by a rapid rise in leaf water potential, may be sufficient to stimulate leaf production, whereas root growth is confined to the usual wet season. Grasstrees are highly flammable yet rarely succumb to fire: while retained dead leaves may reach >1000°C during fire, the temperature 100 mm above the stem apex remains <60°C and the roots are insulated completely. Immediately following fire, leaf production from the intact apical meristem is up to six times greater than that at unburnt sites. For X. preissii, pre-fire biomass is restored within 40 weeks; the mass of live leaves remains uniform from thereon, whereas the mass of dead leaves increases steadily. Leaves usually survive for >2 years. In X. preissii, the post-fire growth flush corresponds to a reduction in starch storage by desmium in the caudex. Minerals, especially P, are remobilised from the caudex to the crown following a spring fire, but accumulate there following an autumn fire. At least 80% of P is withdrawn from senescing leaves, while >95% K and Na are leached from dead leaves. Most stored N and S are volatilised by fire, with 1–85% of all minerals returned as ash. Despite monthly clipping for 16 months, X. preissii plants recover, although starch reserves are depleted by 90%, indicating considerable resilience to herbivory. Analysis of colour band patterns in the leafbases of X. preissii shows that elongation of the caudex may vary more than 5–50 mm per annum, with 10–20 mm being typical. Exceptionally tall plants (>3 m) may reach an age of 250 years, with a record at 450 years (6 m). Fires, recorded as black bands on the leafbases, in south-western Australia have been decreasing in frequency but increasing in variability since 1750–1850. Some grasstrees have survived a mean fire interval of 3–4 years over the last two centuries. In more recent times, some grasstrees have not been burnt for >50 years. The band-analysis technique has been used to show a downward trend in plant δ13C of 2–5.5‰ from 1935 to the present. Grasstrees are most likely to flower in the first spring after fire. A single inflorescence is initiated from the apical meristem, elongating at up to 100 mm day–1 and reaching a length up to 3 m, with one recorded at 5.5 m. This rapid rate of elongation is achieved through leaf (and inflorescence) photosynthesis and desmium starch mobilisation. The developing spike and seeds are vulnerable to a moth larva. Leaf production recommences from axillary buds and the trade-off with reproduction is equivalent to 240 leaves in X. preissii. Flowering and seed production are affected by time of fire. Grasstrees are mainly insect-pollinated. Up to 8000 seeds per spike are produced, although pre-dispersal granivory is common. Seeds are released in autumn and persist in the soil for <2 years. Most fresh seeds germinate in the laboratory but germination is inhibited by light. At any time, seedlings and juveniles may account for most plants in the population, although there may be up to an 80% reduction within 1 year of seedling emergence, often due to kangaroo herbivory. In the absence of fire, mortality of adults may be 4% per annum. Although few grasstree species are considered rare or threatened, their conservation requirements, especially in regard to a suitable fire regime, remain unknown. Grasstrees are particularly susceptible to the exotic root pathogen, Phytophthora cinnamomi, although recruitment among some species has been observed 20–30 years after pathogen invasion. Much remains to be known about the biology of this icon of the Australian bush.

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45

Manczinger, L., Zs Antal, and L. Kredics. "Ecophysiology and breeding of mycoparasiticTrichodermastrains." Acta Microbiologica et Immunologica Hungarica 49, no. 1 (March 2002): 1–14. http://dx.doi.org/10.1556/amicr.49.2002.1.1.

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46

Alberdi, Miren, León A. Bravo, Ana Gutiérrez, Manuel Gidekel, and Luis J. Corcuera. "Ecophysiology of Antarctic vascular plants." Physiologia Plantarum 115, no. 4 (July 11, 2002): 479–86. http://dx.doi.org/10.1034/j.1399-3054.2002.1150401.x.

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47

Raven, John A., and Catriona L. Hurd. "Ecophysiology of photosynthesis in macroalgae." Photosynthesis Research 113, no. 1-3 (July 28, 2012): 105–25. http://dx.doi.org/10.1007/s11120-012-9768-z.

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48

DaMatta, Fábio M. "Ecophysiology of tropical tree crops: an introduction." Brazilian Journal of Plant Physiology 19, no. 4 (December 2007): 239–44. http://dx.doi.org/10.1590/s1677-04202007000400001.

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In this special issue, ecophysiology of major tropical tree crops, considered here on a broader sense and including species such as banana, cashew, cassava, citrus, cocoa, coconut, coffee, mango, papaya, rubber, and tea, are examined. For most of these crops, photosynthesis is treated as a central process affecting growth and crop performance. The crop physiological responses to environmental factors such as water availability and temperature are highlighted. Several gaps in our database concerning ecophysiology of tropical tree crops are indicated, major advances are examined, and needs of further researches are delineated.

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49

Tognetti, Roberto, and John D. Marshall. "Relationship between Forest Ecophysiology and Environment." Forests 12, no. 1 (January 9, 2021): 68. http://dx.doi.org/10.3390/f12010068.

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Although aspects of forest ecophysiology and forest environments have received considerable attention from research scientists in the last three decades, assessment of implications for meeting the climate targets and international agreements is still a matter of debate [...]

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50

Mann, Kenneth H. "Seaweeds: Their environment, biogeography, and ecophysiology." Limnology and Oceanography 36, no. 5 (July 1991): 1066. http://dx.doi.org/10.4319/lo.1991.36.5.1066.

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Journal articles on the topic 'Ecophysiology'

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