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Multi-Index Drought Assessment in Europe

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Any attempt for the application of integrated drought management, requires identifying and characterizing the event per se. The questions of scale, boundary, and of geographic areal extend are of central concern for any efforts of drought assessment, impacts identification, and thus of drought mitigation implementation mechanisms. The use of drought indices, such as Standardized Precipitation Index (SPI) and the Standardized Precipitation Evapotranspiration Index (SPEI), has often lead to pragmatic realization of drought duration, magnitude and spatial extend. The current effort presents the implementation of SPI and SPEI on a Pan-European scale and it is evaluated using existing precipitation and temperature data. The E-OBS gridded dataset for precipitation, minimum temperature, and maximum temperature used covered the period 1969 – 2018. The two indices estimated for time steps of 6, and 12 months. The results for the application period of recurrent droughts indicate the potential that both indices offer for an improvement on drought critical areas identification, threshold definitions and comparability, towards contingency planning leading to better mitigation efforts.
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Journal Name 2016, x, x; doi:10.3390/ www.mdpi.com/journal/xxxx
Proceedings paper
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Multi-Index Drought Assessment in Europe
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Panagiotis D. Oikonomou 1,*, Christos A. Karavitis 2, and Elpida Kolokytha 3
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Received: date; Accepted: date; Published: date
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Academic Editor: name
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1 Colorado Water Institute, Colorado State University, Campus Delivery 1033, Fort Collins, CO 80523-1033,
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USA; panagiotis.oikonomou@colostate.edu
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2 Water Resources Sector, Department of Natural Resources Development and Agricultural Engineering,
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Agricultural University of Athens, 75 Iera Odos, 11855, Athens, Greece; ckaravitis@aua.gr
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3 Division of Hydraulics and Environmental Engineering, Department of Civil Engineering, Aristotle
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University of Thessaloniki, University Campus, 54124 Thessaloniki, Greece; lpcol@civil.auth.gr
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* Correspondence: panagiotis.oikonomou@colostate.edu; Tel.: +1-970-491-6328
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Abstract: Any attempt for the application of integrated drought management, requires identifying
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and characterizing the event per se. The questions of scale, boundary, and of geographic areal
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extend are of central concern for any efforts of drought assessment, impacts identification, and thus
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of drought mitigation implementation mechanisms. The use of drought indices, such as
16
Standardized Precipitation Index (SPI) and the Standardized Precipitation Evapotranspiration
17
Index (SPEI), has often lead to pragmatic realization of drought duration, magnitude and spatial
18
extend. The current effort presents the implementation of SPI and SPEI on a Pan-European scale
19
and it is evaluated using existing precipitation and temperature data. The E-OBS gridded dataset
20
for precipitation, minimum temperature, and maximum temperature used covered the period 1969
21
2018. The two indices estimated for time steps of 6, and 12 months. The results for the application
22
period of recurrent droughts indicate the potential that both indices offer for an improvement on
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drought critical areas identification, threshold definitions and comparability, towards contingency
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planning leading to better mitigation efforts.
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Keywords: Drought; precipitation; SPI; SPEI; Europe
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1. Introduction
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Drought is a normal, periodic natural hazard, although often inaccurately pictured as an
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unexpected and exceptional phenomenon. It strikes practically all the planet, but its characteristics
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vary significantly from one region to another [1,2]. Drought is a temporary anomaly of the usual
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climatic events and it is considered a creepy slow evolving natural hazard, quite different from
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aridity, which is a long-term, permanent part of a climatic zone [39]. Droughts are generally caused
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by a combination of natural events that many times are boosted by anthropogenic pressures. The
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most common definition of drought is a rainfall deficiency, whose occurrence, distribution, and
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magnitude affect the existing water supply, demand, and consumption. Such deficiency may lead to
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in less than expected water quantities necessary for the natural and the societal systems.
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Droughts can befall anywhere in both high and low rainfall areas, in any locale and in any
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season. Drought impacts are exacerbated, when drought strikes a region with already limited water
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resources, and/or misuse and mismanagement of water and with discrepancies between water
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demand and water supply.
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Since there is no single definition of drought, its beginning and ending points are d ifficult to be
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accurately determined. Thus, it is difficult for decision makers and stakeholders to initiate measures
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to confront drought timely and accurately. In this quest, a drought indicator may be proved a
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valuable tool. Drought indicators are conveying objective information about a system’s status that
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may aid decision makers to identify the onset, magnitude and duration of a drought. Nevertheless,
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ECWS-3, 2018 2 of 7
the literature agrees that no single index alone can precisely describe the spatial extent, the duration
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and the magnitude of the phenomenon. Given such characteristics, appropriate and effective drought
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early-warning systems should be based on multiple indices and/or a synthesis of indicators to
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sufficiently demarcate the drought events [5,6,8,1016].
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Currently very few indicators may appropriately illuminate all the drought dimensions at a
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large scale. In addition, applying multiple and /or a combination of indicators provides crucial
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information to monitor and categorize droughts. There exists a plethora of climatic, water supply and
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demand indices to illustrate the drought dimensions and to portray them in a stochastic posture. Each
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index has strengths and weaknesses, with none being superior to the other in its specific application.
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In this regard, SPI and SPEI offer a very well tested and dependable combination of indicators, thus
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they were chosen for application to describe Drought conditions in Europe during the latest decades.
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Drought events have regularly occurred all over Europe and particularly in the last fifty years.
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The spatial extent, the magnitude, the duration of such drought events, as well as the diversified
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impacts inflicted on societies and the environment varied all over this period. Existing information
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in the pertinent literature categorizes the most harsh events that distressed more than (30%) of the
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EU territory as the ones in 1972-74, 1990-94, 2000, 2003, 2007 and 2011 with the most recent in 2018
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[4,1720].
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Drought information in the literature exposed that there are two distinct geographical regions
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in Europe reflecting mostly common meteorological, environmental and geomorphological
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conditions: the southern Mediterranean corridor from the Atlantic Ocean to Asia Minor including
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Portugal, Spain, southern France, Italy, Greece, and Cyprus); and the Northern one beyond the Alps
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mountain chain having Belgium, UK, Finland, Germany, Hungary, Lithuania, Netherlands, Norway,
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Slovakia [6,7,1721]. It is within these two regions that drought dimensions namely spatial extent,
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duration (temporal extent), and magnitude are markedly pronounced.
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Drought spatial extent is closely associated to a country’s given geographical locale and total
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area with the smaller countries to be usually devoured by the event per se (Cyprus, Greece, Italy,
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Malta, Spain, Portugal, France, Ireland, Great Britain, Denmark, Latvia, Estonia, etc.). Drought
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magnitude diversifies all over the continent with the most prominent the 1990-94, 2000 and 2007 ones
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in Spain Italy, Greece, France and Hungary [4,1719]. Drought duration is equally fluctuating from
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country to country. In the Mediterranean area Cyprus, Greece, Italy, Malta, Southern France, Portugal
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and Spain, are having an extended summer period annually with minimal rain. Thus, droughts may
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only manifest themselves during the rainy winter months. In other words, a drought may have a six-
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month duration which compounding to the arid summer period creates a full problematic year
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[4,6,7,22,23]. In the northern countries, droughts occur primarily during the rainy summer season
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having durations from one month (Germany, Hungary, and Lithuania) to two up to six months
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(Northern France, Austria, Belgium). It is noted that Finland was distressed by a nine-month drought
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from August 2002 to April 2003 [24,25]. The estimation of the foremost drought impacts usually
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involves economic costs resulting from the various droughts. Such estimations depict the overall
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economic impacts of droughts during the last fifty years to more than 100 billion € at EU level. They
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also present that the annual average impacts doubled from the 1976-1990 period to the 1991-2006 one.
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Overall, the impacts cost on the average 6.2 billion €/year up to 2003, with an escalation to 8.7 billion
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€ during the 2003 drought [24]. In the 2018 summer as shown in Figure 1, the majority of northern
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Europe is under a drought spell, including Ireland, Great Britain, Netherlands, Belgium, Northern
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France, Germany, Czech Republic, Denmark, Norway, Sweden, Estonia Latvia and Finland [20].
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In this regard, drought impacts are already influencing the agricultural production in the region.
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According to EC (2018) the decrease in crop yields will exceed 50% in the majority of these countries,
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reaching up to 70% in Estonia. Hence, on August the 30th 2018, the European Commission offers
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advanced payments to distressed farmers to receive up to 70% of their direct payment and 85% of
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payments under rural development by mid-October 2018. It is pointed out that such compensations
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refer to economic costs and do not incorporate social and environmental costs as relevant data are
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not available. All in all, the improvement of the economic cost estimation has to comprise social and
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environmental impact assessments in an EC level approach.
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ECWS-3, 2018 3 of 7
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Figure 1. Weather Situation in EU Europe during July and August 2018 [26].
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2. Materials and Methods
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To produce SPI and SPEI, the ensemble version of the E-OBS dataset [27], which covers the area
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of 25N-71.5N x 25W-45E, in 0.25 degree regular latitude-longitude grid resolution, was used. The
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period on record of the E-OBS dataset starts on January 1950 and extends until September 2018. The
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information retrieved includes the following parameters: daily minimum temperature, daily
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maximum temperature, and daily precipitation sum. The data files are in NetCDF-4 format and their
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temporal resolution is daily following the regular calendar (including leap years). All data
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manipulation was performed in R [28] utilizing ncdf4 [29], raster [30], plyr [31], abind [32], and SPEI
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[33] R packages.
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For the computation of the 6-month and 12-month SPI, daily precipitation for the study period
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(Jan. 1969 - Sep. 2018) was converted to a monthly step. Missing value criteria for each one of the grid
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cells' (93,264 in total) daily time series were set for quality control purposes. Such criteria are that the
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missing daily values within a month should not exceed 35% or they should not exceed 30% if the
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missing data are continuous. The minimum (maximum) daily temperature data were transformed to
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monthly mean. Daily minimum (maximum) temperature also based on the aforementioned criteria.
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Monthly evapotranspiration was computed for each grid cell based on the 1985 Hargreaves method
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[34] in order to be used as input for the SPEI index calculation.
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3. Results and Discussion
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The resulting values were spatially visualized in a GIS environment. According to the
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classification presented in Figure 2. The 1990, 1993, 2003, 2007, 2015 and 2018, droughts were
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identified and spatially portrayed. From these droughts, the most intense drought periods were
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chosen to be included in the current effort namely the 1990, 2007 and 2018 ones. These events are
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presented in Figures 3, 4 and 5.
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Figure 2. SPI Classification scale.
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ECWS-3, 2018 4 of 7
(a)
(b)
Figure 3. SPI and SPEI for Europe on April and August 1990, a) 6-month step and b) 12-month step.
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From Figure 3, it may be deduced that the drought was spread out all over Europe. The distinct
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behaviour of southern Europe points out that drought is intensified at the end of the usually rainy
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winter season. Such an event was recorded in the pertinent literature [4,5,7,19,22]. Particularly in
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Greece precipitation was only 43% of the annual average [4], a fact also portrayed in Figure 3. On
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north-western Europe drought reaches its peak at the end of the summer period, when the usual
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rains are crucial also for agriculture. The pertinent literature reported that during 1989, the weather
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all over Europe was unusually dry. This particular trend has continued in 1990, and drought alert
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was issued in many European countries [5,35].
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(a)
(b)
Figure 4. SPI and SPEI for Europe on April and August 2007, a) 6-month step and b) 12-month step.
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From Figure 4 is more evident in North eastern Europe. Such an event was recorded by EEA [18]
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and Spinoni et al. [19]. Karavitis et al. [6] also report the manifestation of a rather minor drought in
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southern Europe.
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(a)
(b)
Figure 5. SPI and SPEI for Europe on April and August 2018, a) 6-month step and b) 12-month step.
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The 2018 drought clearly manifests its spell on the Northern part of Europe as portrayed in
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Figure 5. These facts are also shown in Figure 1, as well as in the pertinent literature [20,26,36]. By
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comparing the various drought incidents as portrayed by SPI and SPEI, it may be derived that the
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most intense drought was the greatest on record for the given time period.
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4. Conclusions
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Effective decision-making is paramount for improving the assessment and responses to drought.
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In order that such Decision Making to take place the aid of indicators to pinpoint, the dimension of
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drought phenomena is more than critical. The application of SPI and SPEI has led to clearly depict
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drought events all over Europe with two distinct zones, the Mediterranean and the Northern one
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beyond the Alps. It would seem that the 1990 drought was the greatest on record. Policy makers and
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others must understand that drought is a normal climatic phenomenon, and its recurrence is
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inevitable and the delineation of its dimension are fundamental for any drought contingency and
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impact mitigation efforts.
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Author Contributions: P.O. and C.K. conceived, designed and performed the experiments; P.O., C.K. and E.K.
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analyzed the data; P.O., C.K. and E.K. wrote the paper.
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Conflicts of Interest: “The authors declare no conflict of interest."
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Abbreviations
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The following abbreviations are used in this manuscript:
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SPI: Standardised Precipitation Index
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SPEI: Standardised Precipitation Evapotranspiration Index
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... The context of continental or global drought assessment utilizing SPI and/or SPEI is becoming more and more frequent in the literature (Lloyd-Hughes and Saunders 2002;Spinoni et al. 2014;Spinoni et al. 2015;Zarch et al. 2015;Spinoni et al. 2017;Stagge et al. 2017;Oikonomou et al. 2018). Spinoni et al. (2017) reported past drought trends all over Europe on both annual basis (from 1950 to 2012) and seasonal basis (from 1950 to 2015). ...
... Then as portrayed and analyzed in Figs. 2, 3 and 4 (maps 17-28), from 1989 up to 2003, southern Europe is experiencing many severe droughts with fewer incidents in the Central and Northern Europe, as it is also described in the literature (Golubev and Dronin 2004;Vidal et al. 2010;Karavitis et al. 2012;Samaniego et al. 2013;Karavitis et al. 2014;World Bank 2018) Overall, from the presented analyses the 1990-2005 period inflicted the most severe droughts for all Europe. Then, from 2004 up to 2018, central and northern Europe become the drought hot spots, with far fewer incidents in the southern part mainly located in the Iberian Peninsula (Figs. 2, 3 and 4 maps 29-40), as also recorded (Marsh et al. 2007;Bissolli et al. 2012;Samaniego et al. 2013;Maia et al. 2015;Noone et al. 2017;Oikonomou et al. 2018;González-Hidalgo et al. 2018). By examining all the quinquennia, the overall frequency analyses, no apparent tendency towards progressively more drought incidents may be reported for the last fifty years, as also independent research indicated (Bissolli et al. 2012;Martins et al. 2012;Sheffield et al. 2012;Hanel et al. 2018). ...
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Indices are used for representing complex phenomena; however, concerns usually arise regarding their objectivity and reliability, particularly dealing with their uncertainties during the development process. The current overarching objective is to reveal the significance of employing different weighting techniques in the application of the Standardized Drought Vulnerability Index (SDVI) and demarcate any pertinent implications that may emerge in drought decision making. Greece, as it is very often facing the catastrophic effects of droughts, presents an almost ideal case for the SDVI testing. SDVI outcomes were tested utilizing five weighting techniques deriving from four weighting methods. The analyses indicated that the use of complex weighting models may not be necessary in all cases and that the simple equal weighting method seems more effective to estimate drought vulnerability. It also seems more important to address the search for valid, reliable and relevant individual indicators forming the complex index as well as appropriate index development processes that would measure performance of water bodies, systems and schemes, monitor the process of equitable sharing, and provide mechanisms for monitoring the state and changes in interdependent water systems.
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Drought is a complex natural hazard with its adverse multifaceted impacts cascading in every physical and human system. The vulnerability magnitude of various areas to drought mostly depends on their exposure to water deficiency, the existing water management policy framework and its implementation. The Standardized Drought Vulnerability Index (SDVI) is an integrated attempt towards characterizing drought vulnerability based on a comparative classification system, incorporating precipitation patterns, the supply and demand trends, and the socioeconomic background as the most crucial contributors to drought vulnerability. This work attempts to evolve the SDVI by presenting a more rigorous method of index parameters estimation and argues that the combination of in-situ and satellite data improve the index results in an effort to further minimize the paucity of drought related information. At the same time, it helps to surpass previous limitations in temporal and spatial propagation of the vulnerability concept. The new framework is applied in the South Platte Basin, within Colorado, on the 2012 summer drought (July-September). The proposed index modification may convey drought information in a more holistic manner to decision makers. SDVI could aid in advancing the understanding of each component contribution through in situ and remote sensing data integration and in avoiding existing practices of broken linkages and fragmentation of the reported impacts. Thus, it is believed that the SDVI could serve as an additional tool to guide decisions and target mitigation and adaptation actions, allowing for a more integrated management approach.
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The current work presents the application of the seasonal Auto Regressive Integrated Moving Average Model (ARIMA) using the Standard Precipitation Index (SPI) as a drought indicator and then depicting the spatial distribution through geo-statistical methods. Greece is very often facing the hazardous impacts of droughts, hence presenting an almost ideal case for such an application. The applied methodology used precipitation data from 55 meteorological stations in two sets distributed throughout the country. To assess the drought, SPI was calculated for a variety of temporal steps. The statistical analyses of the examined temporal step parameters were performed and the Seasonal ARIMA model was employed. Then based on such link, forecasting attempts were derived and presented. The effort may lead to a further understanding of drought duration, magnitude and spatial extend in semi-arid areas. It is believed that such a methodology may provide some useful anticipatory information on the area’s vulnerability to drought and thus portraying the system’s susceptibility to change, damages and losses. In this context, drought contingency planning may be included in the decision making arsenal in order to also widen existing perceptions of the area’s inherent weaknesses and limited resilience to both anthropogenic and natural hazards, serving at the same time as an early warning mechanism.
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This study evaluates the efficacy of Palmer drought indices to monitor hydrological droughts in river discharges and soil moisture in selected watersheds with varying geomorphologic characteristics in region of Thessaly, Greece. The Palmer four indices (PDSI, Weighted PDSI, PHDI and the moisture anomaly Z-index) were used as indicators of meteorological drought severity. The hydrological drought severity was evaluated from the outputs of the monthly UTHBAL conceptual water balance model. The UTHBAL model was calibrated with the available observed runoff data to extend, reconstruct and produce runoff and soil moisture timeseries for the hydrologic period 1960–2002 at the study catchments. The produced hydrologic variables were normalized through Box-Cox transformation and standardized to normal distribution. The standardized hydrologic variables were used as an indicator of hydrological drought severity and were compared with the Palmer drought indices timeseries estimated by basin-wide meteorological data. The results showed that, in general, the Weighted PDSI and the moisture anomaly Z-index were found to better represent river discharges and soil moisture, respectively, for all study watersheds irrespectively to their area, geophysical, and hydroclimatic characteristics. However, the results were quite variable in the identification of specific historical drought periods. Although, the Palmer indices were successful in the identification of drought severity of historical events, they failed to identify the drought duration.
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Future climate warming is expected to enhance plant growth in temperate ecosystems and to increase carbon sequestration. But although severe regional heatwaves may become more frequent in a changing climate, their impact on terrestrial carbon cycling is unclear. Here we report measurements of ecosystem carbon dioxide fluxes, remotely sensed radiation absorbed by plants, and country-level crop yields taken during the European heatwave in 2003. We use a terrestrial biosphere simulation model to assess continental-scale changes in primary productivity during 2003, and their consequences for the net carbon balance. We estimate a 30 per cent reduction in gross primary productivity over Europe, which resulted in a strong anomalous net source of carbon dioxide (0.5 Pg C yr(-1)) to the atmosphere and reversed the effect of four years of net ecosystem carbon sequestration. Our results suggest that productivity reduction in eastern and western Europe can be explained by rainfall deficit and extreme summer heat, respectively. We also find that ecosystem respiration decreased together with gross primary productivity, rather than accelerating with the temperature rise. Model results, corroborated by historical records of crop yields, suggest that such a reduction in Europe's primary productivity is unprecedented during the last century. An increase in future drought events could turn temperate ecosystems into carbon sources, contributing to positive carbon-climate feedbacks already anticipated in the tropics and at high latitudes.
European Environment Agency Trends and projections in Europe 2015: Tracking progress towards Europe's 195 climate and energy targets
  • A Loukas
  • L Vasiliades
  • J Tzabiras
Loukas, A.; Vasiliades, L.; Tzabiras, J. Evaluation of climate change on drought impulses in Thessaly, 14. European Environment Agency Digest of EEA indicators 2014; Technical report No 8/2014; Publications 15. European Environment Agency Trends and projections in Europe 2015: Tracking progress towards Europe's 195 climate and energy targets; Technical report No 4/2015; Publications Office of the European Union: 196 Luxemburg, 2015;