Effects of Climate Change and Urbanization on Vegetation Phenology
in the Bucharest Metropolitan Area
DAN M. SAVASTRU, MARIA A. ZORAN*, ROXANA S. SAVASTRU,
MARINA N. TAUTAN, DANIEL V. TENCIU
National Institute of R&D for Optoelectronics,
Bucharest-Magurele,
ROMANIA
*Corresponding Author
Abstract: - Being an essential issue in global warming, the response of urban vegetation to climate change and
urbanization has become an increasing concern at both the local and global levels. This study aims to
investigate the effect of the urban environment on vegetation phenology for the Bucharest metropolitan area in
Romania and to identify the potential climate drivers that influence key phenology in the urban environment. In
this study, we comprehensively analyzed the response of urban vegetation phenology shifts due to climate
variability and urbanization in the Bucharest metropolitan area from a spatiotemporal perspective during the
2002- 2022 period. Through synergy use of time series of the main climate variables, Air temperature -AT, land
surface temperature (LST), and biophysical variables derived from MODIS Terra/Aqua satellite and in-situ
data, this study developed a complex statistical and spatial regression analysis. Green space was measured with
satellite-derived vegetation indicators Normalized Vegetation Index (NDVI), and Enhanced Vegetation Index
(EVI), Net Primary Production (NPP) data, which captures the combined availability of urban parks, street
trees, forest, and periurban agricultural areas. Leaf Area Index (LAI) and Photosynthetically active radiation
(FPAR) indicators have been used to characterize the effects of meteorological parameters and urbanization
impacts on vegetation phenology and their changes. The results show that the response of vegetation phenology
to urbanization level and climate parameters variability has a distinct spatiotemporal difference across the
urban/periurban gradient. The findings of this study show that the land surface temperature anomalies
associated with urbanization-induced climate warming, especially during strong summer heat waves and under
urban heat islands alter urban vegetation biophysical properties, directly impacting its phenology shifts. At the
metropolitan scale, the urban thermal environment directly impacts vegetation phenology patterns. The
quantitative findings of this study are of great importance for understanding the complex impacts of
urbanization and climate changes on vegetation phenology and for developing models to predict vegetation
phenological changes under future urbanization.
Key-Words: - climate changes, vegetation phenology, biophysical parameters, MODIS Terra/Aqua satellite
data, Bucharest, Romania.
Received: April 26, 2023. Revised: July 15, 2023. Accepted: September 10, 2023. Published: September 27, 2023.
1 Introduction
Is well known that urban vegetation absorbs carbon
dioxide - CO2 as organic compounds through the
mechanism of photosynthesis, regulating the global
carbon cycle and energy exchange, [1]. Vegetation
photosynthetic phenology is an ecologically
sensitive indicator of seasonal and interannual
changes in environmental conditions, related to the
rhythm variation of its photosynthetic activity, and
triggered by periodically changed environment, the
temporal shift of photosynthetic phenology being
responsible for the carbon balance of terrestrial
ecosystems changes, [2]. In the frame of global
warming and the increasing trends of extreme
climate events, urban vegetation is affected by the
increased levels of air temperature, atmospheric
carbon dioxide (CO2), and air pollutant
concentrations, [3], [4]. Vegetation phenology acts
as a control tool for urban cooling/warming effects
and provides helpful information for future urban
green space planning aimed at mitigating local
climate warming, [5]. Urban ecosystems have
remarkable human-induced characteristics, and
urbanization has altered the sensible and latent heat
fluxes over vegetation, causing apparent
phenological shifts. Due to the highest concentration
WSEAS TRANSACTIONS on ENVIRONMENT and DEVELOPMENT
DOI: 10.37394/232015.2023.19.90
Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
E-ISSN: 2224-3496
961
Volume 19, 2023
of human activity, causing the urban heat island
(UHI) effect, [6], [7], [8], [9], cities can be
considered ideal natural laboratories for predicting
the response of vegetation phenology to regional
and global warming. The response of vegetation
phenology to climate changes and urbanization
levels is an important issue of studies on complex
interactions between urbanization and vegetation.
Also, land surface vegetation and its spatiotemporal
changes determine the radiation balance of the
surface and affect the surface temperature and
boundary-layer structure of the atmosphere. Due to
anthropogenic and natural factors, urban vegetation
land cover changes result in the land surface albedo
changes. Recent studies highlighted that
urbanization has both direct impacts on vegetation
due to changes associated with the replacement of
vegetated areas with build-up surfaces, and indirect
impacts on vegetation related to the shifts of
vegetation characteristics resulting from changes in
climatic and environmental factors, [10]. The
increase in urban impervious land cover surfaces
can be used as a proxy for urbanization rate and
assessment of its impacts on vegetation phenology
as well as on induced impacts on long-term surface
urban heat island intensity, [11]. On the other side,
urbanization affects different climatic, especially the
urban thermal environment, [12] and environmental
factors that impact vegetation functions, [13]. The
impact of air pollutants on urban vegetation has
several aspects: with the increasing anthropogenic
CO2 emissions, the near-surface CO2 concentrations
in urban areas are enhanced, which may increase the
vegetation productivity and growth through the
stimulation of photosynthetic rates, while high
concentrations of particulate matter -PM deposition
on vegetation may have adverse effects on
photosynthesis, [14]. Synergy's use of time series-
derived satellite biophysical parameters and in-situ
monitoring data can provide helpful information for
urban vegetation phenology spatiotemporal
dynamics. The rapid advance of satellite-to-earth
observation technology provides a fast, systematic,
cost-effective, and excellent configuration for
processing large and complex spatial data. Remotely
sensed phenological observations have become
important for revealing the response and feedback
of vegetation dynamics to global climate change,
[15], [16], [17], [18], [19].
2 Materials and Methods
2.1 Study Site
The urban metropolitan region of Bucharest (Figure
1) capital of Romania is located in the South
Eastern part of the country, and South-Eastern part
of Europe, being bounded by latitudes 44.33 ON and
44.66 ON and 25.90 OE and 26.20 OE longitudes. Its
center is situated at 44.4355381 oN Latitude and
26.100049 oE Longitude. It has about 1.8 million
inhabitants. According to the European
Commission urban vegetation land cover represents
5.6% of the total territory of the urban core, [20]. In
Bucharest, the green space is very low as compared
with other European metropolises like Paris,
London, and Brussels, where urban/periurban
vegetation land cover is placed in the range (7.37 -
20.84) m2/capita. From 1993 year till 2020 the
metropolitan vegetation land cover in Bucharest has
decreased, from 4839 ha in 1993 to 4506 ha, [21].
This large area covers multiple urban-to-rural
transition areas and consists of different vegetation
types (shrubs, grass, forest, crops, etc.).
Additionally, the metropolitan area has a diverse
landscape pattern in terms of the spatial distribution
of various land cover types, with flat plain areas.
Satellite remote sensing time series data can be used
to gather data on the urban vegetation density, the
size of the land area, and field conditions.
Fig. 1: Bucharest test site, capital of Romania
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DOI: 10.37394/232015.2023.19.90
Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
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The study test area includes Bucharest city and
the surrounding periurban areas with very complex
environments (built, green, and blue structures),
under a rapid urbanization process, and one of the
most air-polluted cities in Europe. Its climate is
temperate continental, with Western European
Climate influences, Mediterranean Cyclones, and
the East-European Anticyclone.
2.2 Data Sets
Daily time series of average daily meteorological
data, including air temperature at 2m height (T), air
relative humidity (RH), air pressure (p), wind speed
intensity (w), and direction, for the Bucharest
metropolitan region were collected from the
Modern-Era retrospective analysis for Research and
Applications, Version 2 (MERRA-2) at, [22], and,
Climate Change Service of Copernicus (C3S) data,
[23]. This study focused on estimating Bucharest
metropolis vegetation land cover phenology
dynamics using time series MODIS Terra data for
the 2002-2022 period. The analyzed period has
registered several heat wave periods, of which the
summers of 2003, 2007, 2010, 2012, 2017, and
2022 have been the highest. We used time series
MODIS Terra products: 8-Day L3 Global 1km SIN
Grid land surface temperature (LST)/emissivity
MOD11A2/LST_Day_1km, 16-day MODIS
13Q1/250m_16_days_NDVI/EVI composites with a
250 m spatial resolution, and MODIS Tera Leaf
Area Index (LAI) MOD15A2H MODIS/Terra Leaf
Area Index/FPAR 8-Day with 500m spatial
resolution, mainly for their capacity to detect
anthropogenic and climate impacts on urban
vegetation land cover changes. Also, we used
MODIS Terra/Aqua phenology data for both cycles
1 and 2 data. Missing values were replaced by linear
interpolation considering neighboring values within
the LST, NDVI/EVI, LAI, and FPAR time series.
Landsat ETM+ 17/07/2022 image was used for
validation and training. Have been selected 6
periurban and 6 urban test areas corresponding to
the six sectors of Bucharest city, a central Bucharest
test area, and the entire metropolis test area. In situ-
monitoring data with GER-260 spectroradiometer
additional data, as well as meteorological
observational data have been used. Statistical
analysis through Spearman rank correlation
coefficients was used. ENVI 5.7, e-cognition, and
ORIGIN 11 software have been used.
2.3 Statistical Analysis
For similarity between two-time series data of the
averaged daily air pollutants, climate observables
(air temperature and relative humidity, wind speed,
surface solar irradiance Planetary Boundary Layer
heights), in Bucharest, this study used Spearman
cross-correlation analysis and non-parametric test
coefficients as well as linear regression analysis. For
assessment of the normality of the averaged daily
time-series data sets, Kolmogorov-Smirnov Tests of
Normality were used. Because the daily climate
variables have a non-normal distribution, Spearman
rank correlation was selected to identify the linear
correlation between the important variables: (1) air
pollutants PM2.5, PM10 concentrations, climate
variables, and ORIGIN 11.0 software version 2023
for Microsoft Windows was used for data
processing.
3 Results and Discussion
Bucharest city, the capital of Romania had an
intense and rapid periurban development after 1990,
and the boundaries of the functional urban region
have shifted outwards from the urban core. The
rapid urbanization of the Bucharest metropolitan
area may be responsible for the recorded higher air
and land surface temperatures associated with UHIs
and HWS during summer periods due to vegetation
land cover reduction and increase of impervious
surfaces. According to Copernicus Urban Atlas land
use land cover (LULC) in 2018 distribution (km2)
for Bucharest metropolitan region shows: artificial
area was 33.6%, agricultural area 53%, natural areas
10.7%, wetland 0.2%, and water 2.4%. This study
used spatiotemporal analysis of time series MODIS
Terra/Aqua NDVI, EVI, LAI, FPAR, LST, NPP,
and vegetation phenology indicators for analysis of
urban vegetation phenology in the Bucharest
metropolitan area during 2002-2022 years. The
main objective of this study was to establish
whether a significant correlation exists between
these indices and other factors. The synergy of Heat
Waves and Urban Heat Islands (UHI) effects
increases the air and land surface temperature in
densely populated metropolitan areas, making urban
areas more predisposed to heat stress compared with
rural areas.
3.1 Impact of Air Temperature and Land
Surface Temperature on Urban Vegetation
During the summer season (June-August), the rank
correlation analyses at the metropolitan pixel scale
(40.5km x 40.5 km) revealed that TA and LST
present a strong positive correlation (r= 0.86%,
p<0.01). Land Surface Temperature (LST) is a
significant radiative skin parameter of the ground,
that provides essential information on surface-
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Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
E-ISSN: 2224-3496
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atmosphere interactions and energy fluxes between
the atmosphere and the ground in the
urban/periurban areas. Gross Primary Production
(GPP) and Net Primary Production (NPP) represent
vegetation productivity. Figure 2 shows the annual
rates of Net Primary Production at 500m spatial
resolution from MODIS Terra data for the 2002-
2022 period and evidences the clear decreasing
trends of urban vegetation phenology during
recorded summer HWs of years 2000, 2003, 2007,
2012, 2016 and 2022. During the recorded summer
heat wave events in Bucharest metropolitan region,
the average extracted net radiation was in the range
of 896- 999 Wm-2. At the microscale, surface albedo
and temperature should have a large variety in the
selected six urban sectors because of the large
material and structural versatilities. The storage heat
flux exceeds the sensible heat flux in urban areas,
whereas the sensible heat flux is higher than the
storage heat flux in industrial areas. In particular,
negative storage heat flux appears at a number of
industrial points, [24]. This tendency shows that
high surface temperature in the periurban industrial
areas of Bucharest is induced by mass energy
consumption because most of the anthropogenic
heat discharge is transferred to the atmosphere as
sensible heat. Figure 3 presents the temporal
distribution of NDVI and LST over the Bucharest
metropolitan area during the 2002-2022 period.
Fig. 2: Temporal pattern of Net Primary Production
of Bucharest vegetation during the 2002-2022
period
Based on the spatial and seasonal (spring and
summer) distributions of LSTNDVI relations over
Bucharest metropolitan area (40.5km x 40.5 km),
using long-term (20022022) MODIS Terra images,
this study found that relations between LST and
NDVI/EVI were highly diverse among the various
urban/periurban biomes and seasons throughout the
entire study period. So, during the spring season
MarchMay), LST-NDVI presents the dominance of
significant positive correlation (Spearman rank
correlation coefficient r=0.71; p<0.01 for metropolis
area), while during the summer season (June
August), most of the vegetation test areas turned to
negative correlation (for metropolis areal r= -0.68,
p<0.01). For the autumn and winter seasons, LST
shows positive correlations with NDVI/EVI (r= 0.62
and p<0.01 for the metropolis area). This study
demonstrates that the drought/vegetation/stress
spectral indices, based on the prevalent hypothesis
of an inverse summer LSTNDVI correlation are
spatially and temporally dependent.
4/7/2002 4/7/2006 4/7/2010 4/7/2014 4/7/2018 4/7/2022
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
NDVI
LST_Day
Day
NDVI
BUCHAREST
250
260
270
280
290
300
310
320
LST_Day (oK)
Fig. 3: Temporal patterns of daily average MODIS
LST (oK) and NDVI during 2002-2022 for the
Bucharest metropolitan area.
Figure 4 presents the temporal distribution of
FPAR and LAI over the Bucharest metropolitan
area during the 2002-2022 period. Statistical
analysis shows positive significant correlations
between land surface temperature both day and
night with FPAR (Spearman rank correlation
BUCHAREST
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Dan M. Savastru, Maria A. Zoran,
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coefficient LSTDay-FPAR r=0.87; p<0.01, and
LSTNight-FPAR r=0.85; p<0.01, for metropolis
areal). Also, LST exhibits lower positive
correlations with LAI for both day and night
monitoring data (Spearman rank correlation
coefficient LSTDay-LAI r=0.20; p<0.01, and
LSTNight-LAI r=0.25; p<0.01, for metropolis areal).
Spearman rank correlation coefficients between
LST and evapotranspiration- ET present moderate
positive values (LSTDay-ET r=0.32; p<0.01, and
LSTNight-ET r=0.39; p<0.01, for metropolis areal).
7/4/2002 7/4/2006 7/4/2010 7/4/2014 7/4/2018 7/4/2022
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6 LAI 40.5x40.5 km
FPAR 40.5x40.5 km
Data
LAI_500m (MOD15A2H)
BUCHAREST
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
FPAR_500m (MOD15A2H)
Fig. 4: Temporal patterns of daily average MODIS
LAI and FPAR during 2002-2022 for the Bucharest
metropolitan area.
3.2 Urban Vegetation Phenology Evolution
Time series satellite remote sensing data provide a
useful tool for spatiotemporal observations of the
land surface, making it essential for urban
vegetation phenology study across large geographic
areas. From MODIS Terra available
MOD17A3HGF products, during analyzed 2002-
2022 period urban vegetation phenology showed
different temporal patterns per cycles 1 (spring) and
2 (autumn), the changes been triggered by climate
changes being influenced by alterations in
meteorological conditions at micro- and mesoscale
as a result of urbanization and the intensification of
anthropogenic activities in Bucharest metropolitan
region (as can be seen in Figure 5 and Figure 6).
Like other studies, [25], [26], [27], the figures in
this article found different yearly changes (advanced
or delayed) in the average start of the vegetation in
spring and autumn seasons date of selected years
during the period 2002-2022. Although differences
were also observed for the end and length of the
growing season, these patterns showed great
interannual variability of urban vegetation
phenology corresponding to different stages
(Greenup, Maturity, MidGreendown, MidGreenup,
and Peak). The analysis of more specific vegetation
classes enables a better understanding of the
phenological response of vegetation to urbanization
intensity. Also, the sensitivity of vegetation
productivity to air temperature, precipitation rate,
soil moisture, and solar surface irradiance are the
key metrics for understanding the variations in
vegetation productivity under changing climate and
predicting future changes in ecosystem functions,
[28], [29].
Fig. 5:Temporal pattern of the vegetation phenology
during cycle 1 in Bucharest metropolitan region.
Is considered that solar-induced chlorophyll
fluorescence is a great proxy for vegetation
productivity in urban and all terrestrial ecosystems.
Among several factors that directly and indirectly
affect vegetation productivity the most important
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Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
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are: meteorological and hydrological conditions;
increasing carbon dioxide (CO2) concentrations
drive enhanced vegetation productivity) and also
lead to rising temperatures; soil nutrient availability
determines potential vegetation productivity, [30],
[31], [32].
Fig. 6: Temporal pattern of the vegetation
phenology during cycle 2 in Bucharest metropolitan
region.
4 Conclusion
Climate warming, air pollution, and heatwaves
(HWs)-related drought events could become a major
driver of large-scale urban vegetation dieback. The
main contributions of this study consist in: (1) the
investigation of the effect of the urban environment
on vegetation phenology for the Bucharest
metropolitan region in Romania, and (2) identifying
the main potential drivers that influence key
phenology in the urban environment. Also, urban
temperate deciduous and broadleaf forests placed in
Baneasa, Cernica-Branesti, and Snagov areas have
been affected by the rise of summer HWs
temperatures through significant disturbances. In the
next decades is expected as climate change to
trigger significant changes in urban vegetation
phenology, air and land surface temperature, and
soil moisture, altering the urban ecosystems. The
novelty of this research was the use of the time
series MODIS Terra/Aqua remotely sensed
observations to assess the importance of phenology
and environmental factors on vegetation
productivity indicating that phenology was the
dominant driver during the investigated period,
despite the differences in the importance of land
surface temperature. The results of this study
support the hypothesis that urbanization produces
significant differences in plant phenology in
Bucharest metropolis, and points to contrasting
responses by different functional vegetation types.
Although differences were also observed for both
the end date and length of the growing season
between vegetation types, these patterns showed
great inter-annual variability. The analysis of
different time series remotely sensed data and
meteorological/hydrological data provide the trends
of spatial patterns of increased land surface
temperature-LST, decreased soil moisture, and
lengthened phenology.
Acknowledgments:
This work was supported by the Romanian Ministry
of Research, Innovation and Digitalization: through
Program 1- Contract no. 18PFE/30.12.2021;
National Research Development and Innovation
Plan 2022-2027, project no. PN 23 05; Grant
CNCS-UEFISCDI, project number PN-III-P4-PCE-
2021-0585; Romanian Ministry of European
Investment and Projects & Romanian Ministry of
Research, Innovation and Digitalization, Contract
no.8/1.2.1 PTI ap.2/17.02.2023
References:
[1] Chen S., Huang Y., Gao S., Wang G., Impact
of physiological and phenological change on
carbon uptake on the Tibetan Plateau revealed
through GPP estimation based on spaceborne
solar-induced fluorescence, Sci. Total
Environ. 663, 2019, pp.45-59.
[2] Liu Z., Zhou Y., Feng Z., Response of
vegetation phenology to urbanization in urban
agglomeration areas: A dynamic urbanrural
gradient perspective, Science of The Total
Environment 864, 2023, 161109.
[3] Li W., Chen R., Ma D., Wang C., Yang Y.,
Wang C., Chen H., Yin G., Tracking autumn
photosynthetic phenology on Tibetan plateau
grassland with the greenred vegetation index.
Agricultural and Forest Meteorology 339,
2023, 109573,
WSEAS TRANSACTIONS on ENVIRONMENT and DEVELOPMENT
DOI: 10.37394/232015.2023.19.90
Dan M. Savastru, Maria A. Zoran,
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Daniel V. Tenciu
E-ISSN: 2224-3496
966
Volume 19, 2023
https://doi.org/10.1016/j.agrformet.
2023.109573.
[4] Dow C., Kim A., D’Orangeville L., et al.,
Warm springs alter timing but not total
growth of temperate deciduous trees,
Nature 608 (7923), 2022, pp.552-557.
[5] Keenan T., Gray J., Friedl M. et al., Net
carbon uptake has increased through
warming-induced changes in temperate forest
phenology, Nature Clim Change 4, 2014,
pp.598604.
https://doi.org/10.1038/nclimate2253
[6] Ding C., Meng Y., Huang W., Xie Q.,
Varying effects of tree cover on relationships
between satellite-observed vegetation greenup
date and spring temperature across Eurasian
boreal forests, Science of The Total
Environment 899, 2023, 165650.
[7] Naserikia M., Hart M.A., Nazarian N.,
Bechtel B, Background climate modulates the
impact of land cover on urban surface
temperature, Scientific Reports 12, 2022,
15433. | https://doi.org/10.1038/s41598-022-
19431-x.
[8] Li L., Zhan W., Hu L. et al., Divergent
urbanization-induced impacts on global
surface urban heat island trends since 1980s,
Remote Sensing of Environment 295, 2023,
113650,
https://doi.org/10.1016/j.rse.2023.113650.
[9] Deng X., Gao F., Liao S., Liu Y., Chen W.,
Spatiotemporal evolution patterns of urban
heat island and its relationship with
urbanization in Guangdong-Hong Kong-
Macao greater bay area of China from 2000 to
2020, Ecological Indicators 146, 2023,
109817,
https://doi.org/10.1016/j.ecolind.2022.109817.
[10] Wu H., Han L., Li T., Summertime climatic
effects of urbanization and their impacts on
human thermal comfort in Xiangjiang
watershed, South-Central China, Urban
Climate 50, 2023, 101582,
https://doi.org/10.1016/j.uclim.2023.101582.
[11] Huang K., et al., Persistent increases in
nighttime heat stress from urban expansion
despite heat island mitigation, J. Geophys.
Res.-Atmos., 126, 2021, e2020JD033831.
[12] Huang X., Song J., Wang C., Chui T.F.M. ,
Chan P.W., The synergistic effect of urban
heat and moisture islands in a compact high-
rise city, Build. Environ., 205, 2021.
[13] Yao R., Hu Y., Sun P., Bian Y., Liu R., Zhang
S., Effects of urbanization on heat waves
based on the wet-bulb temperature in the
Yangtze River Delta urban agglomeration,
China, Urban Climate 41, 2022, 101067,
https://doi.org/10.1016/j.uclim.2021.101067.
[14] Aleš U., Jan K., Eva P., Hana H., Petr S.,
Temporal changes in years of life lost
associated with heat waves in the Czech
Republic, Sci. Total Environ., 716, 2020,
137093, 10.1016/j.scitotenv.2020.137093.
[15] Du H., Wang M., Liu Y., Guo M., Peng C., Li
P., Responses of autumn vegetation
phenology to climate change and urbanization
at northern middle and high latitudes,
International Journal of Applied Earth
Observation and Geoinformation 115, 2022,
103086.
[16] Wang S., Cescatti A., Zhang Y., Zhou Y.,
Song L., Li, Global enhanced vegetation
photosynthesis in urban environment and its
drivers revealed by satellite solar-induced
chlorophyll fluorescence data, Agricultural
and Forest Meteorology 340, 2023, 109622.
[17] Hongchao J., Guang Y., Xiaomin L., Bingrui
J., Zhenzhu X, Yuhui W., Climate extremes
drive the phenology of a dominant species in
meadow steppe under gradual warming,
Science of The Total Environment 869, 2023,
161687.
[18] Ye Y., Zhang X., Shen Y., Wang J., Crimmins
T., Scheifinger H., An optimal method for
validating satellite-derived land surface
phenology using in-situ observations from
national phenology networks, ISPRS Journal
of Photogrammetry and Remote Sensing 194,
2022, pp.74-90.
[19] Díaz J.G., Montserrat Gutiérrez-Bustillo A.,
Rojo J., Influence of urbanisation on the
phenology of evergreen coniferous and
deciduous broadleaf trees in Madrid (Spain),
Landscape and Urban Planning 235, 2023,
104760.
[20] European Commission, Environment - cities
and greater cities, EUROSTAT (Ed.),
URB_CENV. EUROSTAT, ec.europa.eu,
2022.
[21] National Institute of Statistics, Green space
surface per counties and localities
(municipalities and towns), In: Statistics,
N.I.o. (Ed.), GOS103A, 2022.
[22] Solar Radiation Data. https://www.soda-
pro.com/meteo-data (Accessed date: 1 June
2023).
[23] Copernicus Climate Change Service.
https://www.copernicus.eu/climate (Accessed
date: 1 June 2023).
WSEAS TRANSACTIONS on ENVIRONMENT and DEVELOPMENT
DOI: 10.37394/232015.2023.19.90
Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
E-ISSN: 2224-3496
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Volume 19, 2023
[24] Sun X.,Yuan L., Liu M.,Liang S., Li D., Liu
L., Quantitative estimation for the impact of
mining activities on vegetation phenology and
identifying its controlling factors from
Sentinel-2 time series, International Journal
of Applied Earth Observation and
Geoinformation 111, 2022, 102814.
[25] Donnelly A., Yu R., Liu. L., Comparing in
situ spring phenology and satellite-derived
start of season at rural and urban sites in
Ireland, International Journal of Remote
Sensing 42(20), 2021, pp.7821-7841.
[26] Dronova I., Taddeo S., Remote sensing of
phenology: Towards the comprehensive
indicators of plant community dynamics from
species to regional scales, Journal of Ecology
110(7), 2022, pp.1460-1484.
[27] Jia W., Zhao S., Zhang X., Liu S., Henebry G.
M., Liu, L., Urbanization imprint on land
surface phenology: The urbanrural gradient
analysis for Chinese cities, Global Change
Biology 27(12), 2021, 28952904.
[28] Dang C., Shao Z., Huang X., Zhuang Q.,
Cheng G., Qian, J., Climate warming-induced
phenology changes dominate vegetation
productivity in Northern Hemisphere
ecosystems, Ecological Indicators 151, 2023,
110326,
https://doi.org/10.1016/j.ecolind.2023.110326.
[29] Dang C., Shao Z., Huang X., Zhuang Q.,
Cheng G., Qian J., Vegetation greenness and
photosynthetic phenology in response to
climatic determinants, Front. For. Glob.
Change 6, 2023, 75.
[30] Guo L., Gao J., Ma S., Chang Q., Zhang L.,
Wang S., Zou Y., Wu S., Xiao X., Impact of
spring phenology variation on GPP and its lag
feedback for winter wheat over the North
China Plain, Sci. Total Environ., 2020,
138342.
[31] Kӧrner C., Basler D., Phenology under global
warming, Science 327 (5972), 2010, pp.1461
1462.
[32] Zeng X., Hu Z., Chen A., Yuan W., et al.,
The global decline in the sensitivity of
vegetation productivity to precipitation from
2001 to 2018, Global Change Biology 28
(22), 2022, pp.6823-6833.
Contribution of Individual Authors to the
Creation of a Scientific Article (Ghostwriting
Policy)
- Maria Zoran: Conceptualization; Methodology,
Supervision, Writing - review & editing.
- Roxana Savastru: Methodology, Validation,
Review.
- Dan Savastru: Methodology, Validation, Review.
Marina Tautan: Methodology, Validation.
- Daniel Tenciu: Software.
Sources of Funding for Research Presented in a
Scientific Article or Scientific Article Itself
This work was supported by the Romanian Ministry
of Research, Innovation and Digitalization: through
Program 1- Contract no. 18PFE/30.12.2021;
National Research Development and Innovation
Plan 2022-2027, project no. PN 23 05; Grant
CNCS-UEFISCDI, project number PN-III-P4-PCE-
2021-0585; Romanian Ministry of European
Investment and Projects & Romanian Ministry of
Research, Innovation and Digitalization, Contract
no.8/1.2.1 PTI ap.2/17.02.2023
Conflict of Interest
The authors have no conflict of interest to declare.
Creative Commons Attribution License 4.0
(Attribution 4.0 International , CC BY 4.0)
This article is published under the terms of the
Creative Commons Attribution License 4.0
https://creativecommons.org/licenses/by/4.0/deed.en
_US
WSEAS TRANSACTIONS on ENVIRONMENT and DEVELOPMENT
DOI: 10.37394/232015.2023.19.90
Dan M. Savastru, Maria A. Zoran,
Roxana S. Savastru, Marina N. Tautan,
Daniel V. Tenciu
E-ISSN: 2224-3496
968
Volume 19, 2023