a love story about forest drought detection: the ...modis data used4,5: mod09ga-daily surface...

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A love story about forest drought detection: the relationship between MODIS data and Climate time series. C. Domingo (1), M. Ninyerola (1), X. Pons (1) and J. Cristóbal (2). (1) Grumets Research Group. Universitat Autònoma de Barcelona. Spain. ([email protected]) (2) Geophysical Institute. University of Alaska Fairbanks (USA). Research on drought affection is essential, not only for agriculture ecosystems, which are the most studied because are the first economic sector to be affected, but also for forest ecosystems 1 providing invaluable services to society. However, these two ecosystems present different drought characteristics in terms of duration, due to different life cycle length, in terms of intensity, given the difference between the water reservoir capacity, and in terms of the topography of the area affected. Introduction & aims 1 Therefore a different perspective analysis should be used to study forest drought affection. This work integrates the climatic anomalies, traditionally used in an agricultural drought framework through the SPEI index (Standardized Precipitation Evapotranspiration Index) 2 with information related to the real physiological state of the vegetation through vegetation indices (VI) derived from remote sensing data. The aim of this research is to show the necessity to understand biological spatio-temporal drought patterns for drought monitoring by integrating both climate and remote-sensing data. This is accom- plished by: Investigating drought patterns derived from a continuous spatio-temporal climate data Ascertaining the potential of RS data to determine drought events on forest areas DROUGHT AGRICULTURE & GRASSLAND ENVIRONMENT FORESTS & NATURAL ECOSYSTEMS SPEI VI + Meteorological data from 7180 stations distributed along conterminous Spain (1950 to 2012) was assembled. Monthly mean temperature and monthly total precipitation were interpolated, considering the appropriate geographical factors 3 , obtaining 100 m resolution grids for the whole Spain. An SPEI tool, developed in the MiraMon software framework, was used to compute a spatially continuous SPEI useful to identify climate drought anomalies. SPEI was calculated at different time-scales: 3, 6, 9, 12, 18, 24, 36 and 48 months. The more negative the index value, the higher the intensity of drought. Altogether configured a SPEI Big DataBase of about 6000 grids (rasters) corresponding to one grid per month per time-scale for 61 years. SPEI-Climate Anomalies Data Set 2 P (mm) 380 0 T (ºC) 23.4 -1.5 03 06 09 12 18 24 36 48 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec SPEI 3 -3 2008_05 Drought spatio-temporal moving wave 2008_08_05 Vegetation Indices (VI) Estimation 3 MODIS data used 4,5 : MOD09GA-Daily Surface Reflectance-500 m MOD11A1-Daily Land Surface Temperature (LST)-1 km From 2001 to 2012 (validation period) Improved Quality Assurance Data Set masks due to their regular quality Validation area AUTOMATIC ALGORITHM SELECTION 6,7 5 MONTHLY VI COMPOSITES 4331 scenes downloaded 1204 scenes selected Greenness Temperature NDVI VCI NDWI LST The monthly VI composites are related to three vegetation characteristics: water content, greeness and evapotranspiration (ET) VCI: Vegetation Condition Index 8 NDVI: Normalized Difference Vegetation Index 9 NDDI: Normalized Difference Drought Index 10 NDWI: Normalized Difference Water Index 11 TVDI: Temperature Vegetation Dryness Index 12 LST: Land Surface Temperature Study points with different level of affection Forest area NDVI 1 0 NDWI 1 -1 2008_05 2008_05 The higher the NDVI/VCI and NDWI, the greener and wetter, respectively. The lower the NDDI and TVDI, the less the drought and the less the ET, respectively. Results for the study case & conclusions 4 The analysis of SPEI temporal characteristics for the study case show different interpretations according to different time-scales. Short time-scales (3, 6 or 9 months) are characterized by an intense above zero and below zero patterns. Negative peaks denote short-term drought relative to Mediterranean summer or winter precipitation shortages, such as summer 2003 and 2005, and winter 2007–spring 2008. Positive peaks denote the rainiest periods, for instance, 2004 and from 2008 to 2010. Long time-scales are characterized by their significant and persistent negative values episodes, crucial to identify hidden dry periods that, combined with any short-term drought, might develop into a fatal event for forests, such as wildfires. −2 −1 0 1 2 −2 −1 0 1 2 −2 −1 0 1 2 −2 −1 0 1 2 SPEI_03 SPEI_06 SPEI_09 SPEI_12 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 Years SPEI Values Sample Point −2 −1 0 1 2 −2 −1 0 1 2 −2 −1 0 1 2 −2 −1 0 1 2 SPEI_18 SPEI_24 SPEI_36 SPEI_48 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 Years SPEI Values Sample Point Rainy spells Dry spells MODIS signal is sensitive to vegetation responses to drought and concurs with SPEI pattern. Summer 2005 was dry according to SPEI and NDVI-NDWI show a sustained decrease indicating changes in greenness and water content, respectively. Winter 2008 drought event also affected forest activity, given the decrease in the NDVI and NDWI indices. On the contrary, summer 2003 drought does not appear causing strong impact on forests according to VI, thus remote sensing data is essential to understand the real physiologic state of the vegetation. Regression analyses between SPEI and VI: a positive correlation between SPEI and NDVI, NDWI, VCI and a negative correlation between SPEI and NDDI, TVDI, LST, are found. A lag period between the SPEI and the vegetation response is observed. Conclusions 13,14 SPEI grids are appropriate to monitor drought distribution patterns. Shorter time scales monitor almost real time drought events while longer time-scales identify long-term precipitation deficits. MODIS filtering data is essential and VI are good representatives of drought affection on forest areas. This multi-source methodology is specially indicated to monitor large regions or areas with difficult acces suitable, to drought vulnerability. 2003 2005 2006 2008 2010 NDDI TDVI 0.30 0.40 0.50 0.60 0.70 0.10 0.30 0.50 0.70 0.90 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec NDVI NDWI 0.55 0.65 0.75 0.85 0.10 0.20 0.30 0.40 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec -3 -2 -1 0 1 2 3 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 0.4 0.6 0.8 TVDI SPEI_06 -3 -2 -1 0 1 2 3 0 25 50 75 100 VCI SPEI_03 Lag 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 Regression analyses according to time-scales present an inverse behavior between SPEI and VI. The shorter the time-scale, the better the temperature indices correlate (R 2 ≈0.56). VI related to greenness or water content gains importance as the time-scale increases ( R 2 ≈0.38). Scales longer than 24 months have weaker relationship. Indeed, the longer the time-scale, the lower the correlation. Regression analyses according to years indicate that SPEI and VI are not correlated for normal to rainy years, while SPEI explains up to 60% of the VI variability for dry years. This study was supported by the Spanish Ministry of Science and Innovation by an FPU scholarship (2010-2014), the Ministry of Economy and Competitiveness through the research project “DinaCliVe” (CGL2012-33927) and the Catalan Government funds (SGR2014-1491). Xavier Pons is recipient of an ICREA Acadèmia Excellence in Research grant (2011-2015)

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  • A love story about forest drought detection: the relationship between MODIS data and Climate time series.C. Domingo (1), M. Ninyerola (1), X. Pons (1) and J. Cristóbal (2). (1) Grumets Research Group. Universitat Autònoma de Barcelona. Spain. ([email protected]) (2) Geophysical Institute. University of Alaska Fairbanks (USA).

    Research on drought affection is essential, not only for agriculture ecosystems, which are the most studied because are the first economic sector to be affected, but also for forest ecosystems1 providing invaluable services to society. However, these two ecosystems present different drought characteristics in terms of duration, due to different life cycle length, in terms of intensity, given the difference between the water reservoir capacity, and in terms of the topography of the area affected.

    Introduction & aims 1

    Therefore a different perspective analysis should be used to study forest drought affection.

    This work integrates the climatic anomalies, traditionally used in an agricultural drought framework through the SPEI index (Standardized Precipitation Evapotranspiration Index)2 with information related to the real physiological state of the vegetation through vegetation indices (VI) derived from remote sensing data.

    The aim of this research is to show the necessity to understand biological spatio-temporal drought patterns for drought monitoring by integrating both climate and remote-sensing data. This is accom-plished by: Investigating drought patterns derived from a continuous spatio-temporal climate data Ascertaining the potential of RS data to determine drought events on forest areas

    DROUGHTAGRICULTURE & GRASSLAND ENVIRONMENT

    FORESTS & NATURAL

    ECOSYSTEMS

    SPEI VI

    +Meteorological data from 7180 stations distributed along conterminous Spain (1950 to 2012) was assembled. Monthly mean temperature and monthly total precipitation were interpolated, considering the appropriate geographical factors3, obtaining 100 m resolution grids for the whole Spain. An SPEI tool, developed in the MiraMon software framework, was used to compute a spatially continuous SPEI useful to identify climate drought anomalies. SPEI was calculated at different time-scales: 3, 6, 9, 12, 18, 24, 36 and 48 months. The more negative the index value, the higher the intensity of drought. Altogether configured a SPEI Big DataBase of about 6000 grids (rasters) corresponding to one grid per month per time-scale for 61 years.

    SPEI-Climate Anomalies Data Set 2

    P (m

    m) 380

    0

    T (º

    C)

    23.4

    -1.5

    03 06 09 12 18 24 36 48 Jan

    Feb

    Mar

    Apr

    May

    Jun

    Jul

    Aug

    Sep

    Oct

    Nov

    Dec

    SPEI

    3

    -3

    2008

    _05

    Drou

    ght s

    patio

    -tem

    pora

    l mov

    ing

    wav

    e

    2008

    _08_

    05

    Vegetation Indices (VI) Estimation3MODIS data used4,5: MOD09GA-Daily Surface Reflectance-500 m MOD11A1-Daily Land Surface Temperature (LST)-1 km From 2001 to 2012 (validation period) Improved Quality Assurance Data Set masks due to their regular qualityValidation

    area

    AUTOMATIC ALGORITHM SELECTION6,7

    5 MONTHLY VI COMPOSITES

    4331 scenes downloaded

    1204 scenes selected

    Gre

    enne

    ss

    Temperature

    NDVIVCI

    NDWI

    LST

    The monthly VI composites are related to three vegetation characteristics: water content, greeness and evapotranspiration (ET)

    VCI: Vegetation Condition Index8 NDVI: Normalized Difference Vegetation Index9

    NDDI: Normalized Difference Drought Index10 NDWI: Normalized Difference Water Index11

    TVDI: Temperature Vegetation Dryness Index12

    LST: Land Surface Temperature

    Study points with different level of affection

    Forest area

    ND

    VI

    1

    0

    ND

    WI

    1

    -12008_05 2008_05

    The higher the NDVI/VCI and NDWI, the greener and wetter, respectively. The lower the NDDI and TVDI, the less the drought and the less the ET, respectively.

    Results for the study case & conclusions 4The analysis of SPEI temporal characteristics for the study case show different interpretations according to different time-scales.

    Short time-scales (3, 6 or 9 months) are characterized by an intense above zero and below zero patterns. Negative peaks denote short-term drought relative to Mediterranean summer or winter precipitation shortages, such as summer 2003 and 2005, and winter 2007–spring 2008. Positive peaks denote the rainiest periods, for instance, 2004 and from 2008 to 2010.

    Long time-scales are characterized by their significant and persistent negative values episodes, crucial to identify hidden dry periods that, combined with any short-term drought, might develop into a fatal event for forests, such as wildfires.

    −2−1

    012

    −2−1

    012

    −2−1

    012

    −2−1

    012

    SP

    EI_03

    SP

    EI_06

    SP

    EI_09

    SPEI_12

    2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013Years

    SPEI

    Val

    ues

    Sam

    ple

    Poin

    t

    −2−1

    012

    −2−1

    012

    −2−1

    012

    −2−1

    012

    SPEI_18

    SPEI_24

    SP

    EI_36

    SPEI_48

    2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013Years

    SPEI

    Val

    ues

    Sam

    ple

    Poin

    t

    Rainy spells Dry spells

    MODIS signal is sensitive to vegetation responses to drought and concurs with SPEI pattern. Summer 2005 was dry according to SPEI and NDVI-NDWI show a sustained decrease indicating changes in greenness and water content, respectively. Winter 2008 drought event also affected forest activity, given the decrease in the NDVI and NDWI indices. On the contrary, summer 2003 drought does not appear causing strong impact on forests according to VI, thus remote sensing data is essential to understand the real physiologic state of the vegetation.

    Regression analyses between SPEI and VI: a positive correlation between SPEI and NDVI, NDWI, VCI and a negative correlation between SPEI and NDDI, TVDI, LST, are found. A lag period between the SPEI and the vegetation response is observed.

    Conclusions13,14 SPEI grids are appropriate to monitor drought distribution patterns. Shorter time scales monitor almost real time drought events while longer time-scales identify long-term precipitation deficits. MODIS filtering data is essential and VI are good representatives of drought affection on forest areas. This multi-source methodology is specially indicated to monitor large regions or areas with difficult acces suitable, to drought vulnerability.

    2003 2005 2006 2008 2010

    ND

    DI

    TDVI

    0.30

    0.40

    0.50

    0.60

    0.70

    0.10

    0.30

    0.50

    0.70

    0.90

    Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

    Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

    ND

    VIN

    DW

    I

    0.55

    0.65

    0.75

    0.85

    0.10

    0.20

    0.30

    0.40

    Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

    Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

    −3−2

    −1

    0

    1

    23

    2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013

    0.4

    0.6

    0.8TVDISPEI_06

    −3−2

    −1

    0

    1

    23

    0

    25

    50

    75

    100VCISPEI_03 Lag

    2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013

    Regression analyses according to time-scales present an inverse behavior between SPEI and VI. The shorter the time-scale, the better the temperature indices correlate (R2≈0.56). VI related to greenness or water content gains importance as the time-scale increases (R2≈0.38). Scales longer than 24 months have weaker relationship. Indeed, the longer the time-scale, the lower the correlation. Regression analyses according to years indicate that SPEI and VI are not correlated for normal to rainy years, while SPEI explains up to 60% of the VI variability for dry years.

    This study was supported by the Spanish Ministry of Science and Innovation by an FPU scholarship (2010-2014), the Ministry of Economy and Competitiveness through the research project “DinaCliVe” (CGL2012-33927) and the Catalan Government funds (SGR2014-1491). Xavier Pons is recipient of an ICREA Acadèmia Excellence in Research grant (2011-2015)

  • BIBLIOGRAPHY:

    1. Jacob, A.L., Wilson, S.J. & Lewis, S.L. 2014. Ecosystem services: Forests are more than sticks of carbon. Nature, 507(7492).

    2. Vicente-Serrano, S.M., Beguería, S. & López-Moreno, J.I., 2010. A Multiscalar Drought Index Sensitive to Global Warming: The Standardized Precipitation Evapotranspiration Index. Journal of Climate, 23(7): pp. 1696–1718.

    3. Ninyerola, M., Pons, X. & Roure, J.M. 2007. Monthly precipitation mapping of the Iberian Peninsula using spatial interpolation

    tools implemented in a Geographic Information System. Theoretical and Applied Climatology, 89(3–4): pp. 195–209.

    4. Vermote, E.F., Kotchenova,S.Y. & Ray, J.P. 2011. MOD09 (Surface Reflectance) User’s Guide, Version 1.3. MODIS Land Surface Reflectance Science Computing Facilit.

    5. Guindin-Garcia, N. et al. 2012. An evaluation of MODIS 8- and 16-day composite products for monitoring maize green leaf area

    index. Agricultural and Forest Meteorology, 161: pp. 15–25.

    6. Pesquer, L., Domingo, C. & Pons, X. 2013. A Geostatistical Approach for Selecting the Highest QualityMODIS Daily Images. In J.M. Sanches, L. Micó, & J.S. Cardoso, eds. Pattern Recognition and ImageAnalysis. Lecture Notes in Computer Science. Springer Berlin Heidelberg. pp. 608–615.

    7. Pons, X. et al. 2014. Automatic and improved radiometric correction of Landsat imagery using reference values from MODIS

    surface reflectance images. International Journal of Applied Earth Observation and Geoinformation, 33: pp. 243–254.

    8. Kogan, F. & Sullivan, J., 1993. Development of global drought-watch system using NOAA/AVHRR data. Advances in Space Research, 13(5), pp. 219–222.

    9. Holben, B.N., 1986. Characteristics of maximum-value composite images from temporal AVHRR-data. International Journal of

    Remote Sensing, 7(11), p.1417.

    10. Gu, Y. et al., 2007. A five-year analysis of MODIS NDVI and NDWI for grassland drought assessment over the central Great Plains of the United States. Geophysical Research Letters, 34(6).

    11. Gao, B., 1996. NDWI--A normalized difference water index for remote sensing of vegetation liquid water from space. Remote

    Sensing of Environment, 58(3), pp. 257–266. GEOSS, 2014. http://www.earthobservations.org/geoss.php.

    12. Sandholt, I., Rasmussen, K. & Andersen, J., 2002. A simple interpretation of the surface temperature/ vegetation index space for assessment of surface moisture status. Remote Sensing of Environment, 79(2–3), pp. 213–224.

    13. Deshayes, M. et al. 2006. The contribution of remote sensing to the assessment of drought effects in forest ecosystems. Annals

    of Forest Science, 63(6): pp. 579–595.

    14. Domingo, C. et al. 2015. Integration of climate time series and MODIS data as an analysis tool for forest drought detection. In: Drought: Research and Science-Policy Interfacing. Edited by Joaquin Andreu Alvarez, Abel Solera, Javier Paredes-Arquiola, David Haro-Monteagudo, and Henny van Lanen. CRC Press 2015 Ch.13. pp. 97–104. ISBN: 978-1-138-02779-4