Evidence exists of nighttime transpiration and its potential impact on plant/water relations for species in a diversity of ecosystems. However, relevant data related to typical desert riparian forest species remains l...Evidence exists of nighttime transpiration and its potential impact on plant/water relations for species in a diversity of ecosystems. However, relevant data related to typical desert riparian forest species remains limited Accordingly, we measured sap flow velocity of Populus euphratica using the heat ratio method between 2012 and2014. Nocturnal stem sap flow was separated into nighttime and stem refilling using the ‘‘forecasted refilling''method. Nighttime transpiration was observed for each phenophase. The highest value was during the full foliation period but lowest during leaf expansion and defoliation periods. The contribution of nighttime transpiration to daytime transpiration was an average of 15% but this was comparatively higher during the defoliation period. Relationships between nighttime transpiration, vapor pressure deficits, and air temperatures were more closely associated than with wind speed in all phenophases. Moreover, we found that nighttime transpiration linearly correlated to vapour pressure deficit during the first and the full foliation periods, but nighttime transpiration showed exponential correlations to air temperatures during the same phenophases. Additionally, environmental drivers of transpiration were significantly different between nighttime and daytime(P \ 0.05). Driving forces behind nighttime transpiration were characterized by many factors, and integrated impacts between these multiple environmental factors were complex. Future studies should focus on these integrated impacts on nighttime transpiration, and the physiological mechanisms of nighttime transpiration should be investigated, given that this could also influence its occurrence and magnitude during different phenophases.展开更多
Based on plant phenology data from 26 stations of the Chinese Phenology Observation Network of the Chinese Academy of Sciences and the climate data, the change of plant phenophase in spring and the impact of climate w...Based on plant phenology data from 26 stations of the Chinese Phenology Observation Network of the Chinese Academy of Sciences and the climate data, the change of plant phenophase in spring and the impact of climate warming on the plant phenophase in China for the last 40 years are analyzed. Furthermore, the geographical distribution models of phenophase in every decade are reconstructed, and the impact of climate warming on geographical distribution model of phenophase is studied as well. The results show that (i) the response of phenophase advance or delay to temperature change is nonlinear. Since the 1980s, at the same amplitude of temperature change, phenophase delay amplitude caused by temperature decrease is greater than phenophase advance amplitude caused by temperature increase; the rate of phenophase advance days decreases with temperature increase amplitude, and the rate of phenophase delay days increases with temperature decrease amplitude. (ii) The geographical distribution model between展开更多
Although important,phenological studies comparing congeneric species or the same species growing in different habitats are still scarce for the tropics.Herein,we integrate phylogeny,ecology and biometeorology to verif...Although important,phenological studies comparing congeneric species or the same species growing in different habitats are still scarce for the tropics.Herein,we integrate phylogeny,ecology and biometeorology to verify whether the phenophases of congeneric species Myrcia laruotteana and Myrcia amazonica or Clethra scabra differ when their populations inhabit wetland and drained habitats and to determine what abiotic factors affect the vegetative and reproductive phenophases of these species in distinct habitat patches.We collected data on phenological events of 80 trees for 1 year in Itacolomi State Park,Brazil,and related them to abiotic local factors.Contrary to our expectation,the phenophases of the congeneric species did not differ between habitats,but the reproductive phenophases of C.scabra did and was greater in drained soil.Phenophases of C.scabra were affected by the depth of the water table and maximum temperature in the wetland soil.Insolation,precipitation,maximum temperature and relative humidity influenced Myrcia and Clethra in the drained soil.The differences between C.scabra populations suggest that this species is phenotypically plastic and can present distinct phenophases depending on the habitat it inhabits.On the other hand,the congeneric Myrcia species may have similar phenophases in distinct habitats because of their shared similarities during their evolution.This study provides a better understanding of the ecology of these species and their adaptations to different abiotic conditions.Data of this nature are important in a changing world and can inform strategies for adaptive management.展开更多
Introduction:This paper describes the leafing,flowering and fruiting phenology of canopy trees in the dry deciduous forest of Bhadra wildlife sanctuary from June 2004 to May 2006.Method:All the woody canopy individual...Introduction:This paper describes the leafing,flowering and fruiting phenology of canopy trees in the dry deciduous forest of Bhadra wildlife sanctuary from June 2004 to May 2006.Method:All the woody canopy individuals(>20 cm girth at breast height)were identified and tagged with a unique number along a transect of approximately 2 Km comprising 157 individuals of 22 species.Observations were made at monthly intervals from June 2004 to May 2006 for leafing,flowering and fruiting phenophases.Result:Leaf fall starts in September,with a peak in December and January.Leaf initiation begins in February,with a peak in April before the monsoon.Leaf expansion starts in February from pre-monsoon with a peak in May and July during the monsoon.Leaf senescence begins in September to November and peaks in January to March.Flower bud initiates in January with a peak in April and May,and pollination begins in April with a peak in May and July before the monsoon to onset of monsoon.Fruit bud initiates in May with a peak in September and October.Unripened fruit was observed in May with a peak in September and November.Fruit fall begins in November with a peak in March.Conclusion:Our results show that leafing and flowering activities occur in the summer or pre-monsoon.Fruiting patterns occur during the monsoon to post-monsoon season.Seasonality among various phenophases indicates that leaf senescence flower initiation and fruit fall have strong seasonality.展开更多
基金financially supported by the Key Research Program of Frontier Sciences CAS(QYZDJ-SSWDQC031)Key Project of the Chinese Academy of Sciences(KZZDEW-04-05)+1 种基金the National Natural Science Foundation of China(91025024)the ‘‘Western Light’’ project of the Chinese Academy of Science
文摘Evidence exists of nighttime transpiration and its potential impact on plant/water relations for species in a diversity of ecosystems. However, relevant data related to typical desert riparian forest species remains limited Accordingly, we measured sap flow velocity of Populus euphratica using the heat ratio method between 2012 and2014. Nocturnal stem sap flow was separated into nighttime and stem refilling using the ‘‘forecasted refilling''method. Nighttime transpiration was observed for each phenophase. The highest value was during the full foliation period but lowest during leaf expansion and defoliation periods. The contribution of nighttime transpiration to daytime transpiration was an average of 15% but this was comparatively higher during the defoliation period. Relationships between nighttime transpiration, vapor pressure deficits, and air temperatures were more closely associated than with wind speed in all phenophases. Moreover, we found that nighttime transpiration linearly correlated to vapour pressure deficit during the first and the full foliation periods, but nighttime transpiration showed exponential correlations to air temperatures during the same phenophases. Additionally, environmental drivers of transpiration were significantly different between nighttime and daytime(P \ 0.05). Driving forces behind nighttime transpiration were characterized by many factors, and integrated impacts between these multiple environmental factors were complex. Future studies should focus on these integrated impacts on nighttime transpiration, and the physiological mechanisms of nighttime transpiration should be investigated, given that this could also influence its occurrence and magnitude during different phenophases.
基金This work was supported by the Chinese Academy of Sciences (Grant No. KZCX2-314), the National Natural Science Foundation of China (Grant No. 49901001), and Institute of Geographic Sciences and Natural Resources Research, the Chinese Academy of Sciences
文摘Based on plant phenology data from 26 stations of the Chinese Phenology Observation Network of the Chinese Academy of Sciences and the climate data, the change of plant phenophase in spring and the impact of climate warming on the plant phenophase in China for the last 40 years are analyzed. Furthermore, the geographical distribution models of phenophase in every decade are reconstructed, and the impact of climate warming on geographical distribution model of phenophase is studied as well. The results show that (i) the response of phenophase advance or delay to temperature change is nonlinear. Since the 1980s, at the same amplitude of temperature change, phenophase delay amplitude caused by temperature decrease is greater than phenophase advance amplitude caused by temperature increase; the rate of phenophase advance days decreases with temperature increase amplitude, and the rate of phenophase delay days increases with temperature decrease amplitude. (ii) The geographical distribution model between
基金supported by the Research,Graduate and Innovation Department (PROPP) of the Federal University of Ouro Preto (UFOP)。
文摘Although important,phenological studies comparing congeneric species or the same species growing in different habitats are still scarce for the tropics.Herein,we integrate phylogeny,ecology and biometeorology to verify whether the phenophases of congeneric species Myrcia laruotteana and Myrcia amazonica or Clethra scabra differ when their populations inhabit wetland and drained habitats and to determine what abiotic factors affect the vegetative and reproductive phenophases of these species in distinct habitat patches.We collected data on phenological events of 80 trees for 1 year in Itacolomi State Park,Brazil,and related them to abiotic local factors.Contrary to our expectation,the phenophases of the congeneric species did not differ between habitats,but the reproductive phenophases of C.scabra did and was greater in drained soil.Phenophases of C.scabra were affected by the depth of the water table and maximum temperature in the wetland soil.Insolation,precipitation,maximum temperature and relative humidity influenced Myrcia and Clethra in the drained soil.The differences between C.scabra populations suggest that this species is phenotypically plastic and can present distinct phenophases depending on the habitat it inhabits.On the other hand,the congeneric Myrcia species may have similar phenophases in distinct habitats because of their shared similarities during their evolution.This study provides a better understanding of the ecology of these species and their adaptations to different abiotic conditions.Data of this nature are important in a changing world and can inform strategies for adaptive management.
文摘Introduction:This paper describes the leafing,flowering and fruiting phenology of canopy trees in the dry deciduous forest of Bhadra wildlife sanctuary from June 2004 to May 2006.Method:All the woody canopy individuals(>20 cm girth at breast height)were identified and tagged with a unique number along a transect of approximately 2 Km comprising 157 individuals of 22 species.Observations were made at monthly intervals from June 2004 to May 2006 for leafing,flowering and fruiting phenophases.Result:Leaf fall starts in September,with a peak in December and January.Leaf initiation begins in February,with a peak in April before the monsoon.Leaf expansion starts in February from pre-monsoon with a peak in May and July during the monsoon.Leaf senescence begins in September to November and peaks in January to March.Flower bud initiates in January with a peak in April and May,and pollination begins in April with a peak in May and July before the monsoon to onset of monsoon.Fruit bud initiates in May with a peak in September and October.Unripened fruit was observed in May with a peak in September and November.Fruit fall begins in November with a peak in March.Conclusion:Our results show that leafing and flowering activities occur in the summer or pre-monsoon.Fruiting patterns occur during the monsoon to post-monsoon season.Seasonality among various phenophases indicates that leaf senescence flower initiation and fruit fall have strong seasonality.