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Landsacpe complexity & Soil Moisturevariation in south Georgia,USA,for remote sensinapplications Mario A. Girdalo , 2008 , Uni.GeorgiaUSA Present  by :  MARI ; FOROOTAN.
We adressed Temporal & spatial  Variation  Of SM In a heterogenous landscape
0-History !  1-OBJECTIVE &HYPOTHESIS 2-METHODOLOGY 3-RESULTS 4-CONCLUSION IN  THESE  PARTS
SM= soil moistue LRW=little river watershed=study area LULC=LandCover-LandUse ANOVA=analyze of variance LS=landscape H-P=hydra-probe Var. =variation P.C.C =pearson correlation coefficient Remember
Western  et al. ,1999 SM is not a random phen. Sp. Var. according to Size of Samp. Area & Env. Var. Anderson   et al. ,2003 Combination of Env. Factors (Soil.Veg.c,Topo,Climate) Create spatially distribution of SM Over dif.scales of space & time History
History  USDA-NASA 2003  (SMEX03) In situ devices  at LRW produce Relieble inf. Of SM Moran  ,2004 Cashion  ,2005 Under a complex LS. Remote sensors  with coarse spatial resolution  produce inaccurate estimates
Investigate  Spacial  var. In ground-based  SM data collection  From small plots (30*30) Similar to  pixel size of Small EFOV remote sensors TM , ETM+& ASTER &ALI In a heterogenous landscape  OBJECTIVE
We want toAssess Suitabolity of Using small plots For  field  validation  Of  Satellites remote sensing  Instruments With small EFOV( < 30m )
TM,ETM+ ASTER & ALI All are expected  To better capture  Local field conditions  Under landscape environmental  Complexity
Dispite Heterogeneity of study area It is possible to find  Temporally & Spatiolly Homogenous  SM behavior  Within small areas of  30*30. Our HYPOTHESIS
Study SM var. Within 5 dominate  LULC In  LRW Landscape. Another Objective
1- increase field knowledge of SM behavior in  Hetero.LS 2-lead to better interpretation of the  Satellite estimates Our Results Will
Methodology
-Study Area -Plot Data collection -Statistical Analysis
Study Area
*Relatively flat topography *Broad flood plains *Poorly defined stream  channels *gently sloping %1-%5 *sandyloam soil with sandy surface horizon  &heavier subsoil ,[object Object],& fast surface drainage *Annual av,RF=120 mm *unevently distribution  Short duration in Win. High density in Sum. Sum. are long &hot &humid Win. are short &mild Landscape composed of a diversity of LULC Forest , Cropland , Pasture, Residental area &  Wetlands Northen eastern  Portion of  The 334 km2 Little river watershed In South Atlantic coastal plain Of US Near  Tifton ,Georgia
An in situ Network 27 ground stations  As a source of ground-based  Point Data To 1- validate remote sensing analysis of SM and  Soil tempreture& Climate 2- long term Hydrological studies In South eastern of US 2002 - 2003
These 27 stations equipped with Steven-vitel  Hydra-Probe(steven water monitoring sys.)
H-P-s  Operated by USDA-ARS And record SM information &Ground tempreture At 3 depths 5 , 20 , 30 m Every 30 min Typ. Installed along Agriculture field boundaries, Fence rows & pasture areas & Typ. Surounded by Native grass veg.cover.
Plot Data collection
8 of 27 sites  Selected  Surounding H-P & Associated with the  In situ SM Monitoring station
30 * 03 m area Surrounded H.p And Subsequently sampled for SM SM was measured using Portable theta capacitance probe (measure dielectric conductivity similar to H.p)
To minimize Errors We use Same  equipment  &  Same  personnel
3 different Soil Dataduring 2005 - Jan2006
Data collected Randomly Within 8(30*30m) plots 1 8 16 26 32 40 50 63 66 For each plot 10-20 reading On  4 dif. Dates  March11  March28 April12 May24 2005
testing temporal stability of SM reading over a fairly short time period (here 48 h) On 2 consecutive days *Nov 30 & Dec 1 (2005) *Jan 13 & Jan 14 (2006) Systematic sampling 2
Each reading was taken in  3 intervals in  4 directions  From H.P station Total 20 sample per Plot
At some locations  Fewer than  4 directions  Were evaluated  Due to the presence of obstacles Such as Road  and Channels 4  perpendicular  direction Sampling  location Hdra-probe Station  30 M 30 M
collected from  5 field adjacent to plot areas Under the LULC; Grass ,Orchard,Bare land& Agriculture Cotton & Peanuts Associated with H.P sits: 50 , 32 , 66 & 40 3
Each LULC 8 – 10 SM readings At 3 intervals along a  25 – 30 m transect In 4 dif.times Nov – Dec 2005 & Jan 2006
Precipitation from each site  Raingages at H.P stations For 12-day period at intervals 5 min For each Sampling Dates
Statistical analysis
1- ANOVA 2-  time stability anaysis 3-  Tukey & tamhane hoc analysis 4-Pearson Correlation Coefficient  5-  t- test  (Were used to analyze Data)
Results
Results of precipitation analysis
No.  Of R.F For 12 day period previos to  Sampling date Ranged between 3  -  6
Max  average was  10 cm  In  28  March Min average was less than  2.2 In 24 May
March 11 March  28
April12 May  24
Nov & Dec January  2006
During R.F events  all sites received simultanous precipitation  with small var. among them. SO Water supply  was homogeneous  for all sites prior to Sample Date SO SM dif. Can be considered  As a result of  Intrinsic & mostly independet of water supply
When we compared it with precipitation record: 8  greatest cumulative prec. only for 3 Sam.Date. While  63 , 16 , 50  greatest prec. inputs for 5 other days Aand For lowest  40 , 32   Prec. Record shows they have above average These observations support  the Hypothesis: SM caused by intrinsic  Enviromental var. Beyond prec.acting At  the local scale Mean  volumetric  SM & infield Variation Recorded in  8 locations  Presented  8  highest valus of Vol.SM 40  lowest  valus of Vol.SM
ANOVA of SM
This analys use 2 sets of variation to perform  Composition between plots Variation   among  groups Variation   within  groups
It shows: ,[object Object]
Low SM var. within a given plot which suggest homogenous,[object Object]
A multiple comparesionamong the plots It one by one comparsionbetween sites
0  = means  weak relationship & More than 0 means have a relationship 1  ,  2  ,  3  ,… Bigger  score Stronger relationship
SO Weakest relationship  Were find between  8-26  /8-40  /8-66 / 40-50
SO Strongest  Relationship are  Between 26-32  /  32 – 66 / 50 -63
SO Site  8 Is most unique  SM Behaviuor Site  66 High level of  Similarity  With other sites
Similarity of 26  &  32  *Precipitation record: similar and  Less than 2.5 cm Dif.for all Samp.D. *Soil type: Both are belong to Tifton soil Series *Veg. cover: 32 short grass 26edge of agr.field in wich hay  is cut for cattle consumption
Similarity of 16  &  50  *Precipitation: Dif. Cumulative rain 10 & even 18 cm *Soil type: 16 Tifton series    50Sunsweet series *Veg. cover: Similar homogenous grass  &exposed to transit agri. Equipment Influenc soil physical characteristics
Most dissimilar sites were  8-26 / 8-40 /8-66 /40-50/50-32 Low assosiation was found between 16 &32 In total 6  Sam.D.
8 – 26 / 8-40 / 8-66  Dif. Combination of Soil type SO Var. in water infiltration process SO Dif. SM content 40-50 / 50-32 Dif. Cumulative rainfall
Observation suggest that
In LRW LULC  Is a greater factor affecting  SM conditions Than  Cumulative Rainfall
Influnce of LULC In SM Indicated by our results in LRW. LS. That make: Dif. Evatranspiration & Soil water usage
Spatial resolution of R.sensing Sensors That are More appropriate to  Capture SM conditions under this LS. Will be defined by  *LS. Fragmentation *LULC composition *Sizes of LULC fragments
High levels of fragmetation at LRW With fragments of  Small size So Moderate to  Fine spatial resolutionsensors (~ 3 0  m) Are expected better suit the countinoussutdy Of SM in LRW
SM time suitability
Parasmetermean relative diffrence: 1-Measure how particular sample  compare with  Av. SM of plot 2-Indicator of  Infield  Variation of surface SM
26 has highest range on mean Dif. (36%-39%)
16 has Lowest Var. (-4%-+4%)
Highest Av. Of mean relative Dif. Was 2.6% in 66 Followed by  8 , (2.1%) 16 (1.2 %) 26 (1.0%) Otherwise mean relative Dif. Was  0.1 % below the plot Dif. Approach Zero High level of Homogeneity Within each  Sample plot
Results indicate Samp. Point within the plots are very close to each  Plot mean SO Can accurately  Estimate  Surface SM behavior Of  Entire 30*30 m  plot
Our results shows High level of in field  Homogeniety That’s in contrast with The results of similar research performed  In  large plots
in our research By selecting Small LS. fragments. The  in field heterogenitycasued by Topography Diffrence Was  Minimize
Stability in plots 40  &  50 Can be explained by their  Relatively Homogenous LC 50  part of a larger pasture and entire plot covered by same grass type 40  part of a mechanized AGR.Field & change  Veg-cover throughout growing season
So HemogeneityVeg.Cover & Homogenietyprecipitation,Slope,Soil physical characters  High stability of SM Recorded at these 2 sites
Pearson correlation coefficient
Was compare to evaluate if all  in field locations experience similar  SM VAR.s  within a  short period (one day in this case)
Correlations were significant in both sets But  Only for 26 , 32 , 63
P.C.C Is an indicator of  Spatial stability Of SM Point data
Low pcc with low significant level Process is unstable in space and for time  lag  In which Data collected
Two samples t-test
Computed to evaluate The Variation in Av.SM values  From one day to next
Results suggest that Surface SM Will notnecesserily Reflect profile conditions
SO Remote sensing retrieving algorithms Based only in direct or indirect Quantification of Surface conditions As Temp. , SM  May produce Errors When used in this LS.
These ERRORS Can be Minimized  by incorporatig in to Rem.Sen. Analysis data of Precipitation events prior to Samp.D & Infiltration analysis for soil type dominated of study area
Statistical analysis foragriculture LUtransects
Discriptive statistics for SM  On 4 dif. Date collection On 25-30 m long transects Related to Dif. LU Adajent to 5 plots
Results shows Orchard & grass Have the wettest conditions While Cotton& peanut fields Were the driest
Tilled AG.fiels lowest spatial variability with Av. Values around %1 Grass AG.field highest standard  deviation with values btween %1.8 - %2.6  Bare land  Intermediate behavior
SM Var. Between LU
ANOVA Between SM valuse for  five LULC  Showed  Significant statistical Dif.  For all 4 days
Variation between goups showed by Anova Peanut & Cotton   Most similar with No stat.Dif Among them  for any 4 days Greatest Dif. With orchard, grass & bareland Showing Stat.Dif on all Samp.Dates
Conclusion
AOVA high  Diffrences in SM among  the plots & high Hemogeneity within them Precipitation analysis similar rainfall conditions So SM.Var. explained by in situ local conditions
Temporal stability analysis SM has high stability within the small plots and single point can use to monitor SM Var. of all plot T-statistical analysisSMstatesin upper soil layer changes within 24H
And finally we found stat.Dif. In SM between Dif. LULC  as there adjacent plots
finally
The results confirm that
A remote sensing  approach that consider  Homogeneous LULC ,LS fragments  can be used to identify  LS units of similar SM behavior  under Heterogeneous landscapes
In addition The insitu USDA-ARS network  will serve better in remote sensing studies  in wich sensors  with fine spatial resolution  are evaluated
Thanx   4Your A 10tion Mari .forootan.1388

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Landsacpe Complexity & Soil Moisture Variation In South Copy

  • 1. Landsacpe complexity & Soil Moisturevariation in south Georgia,USA,for remote sensinapplications Mario A. Girdalo , 2008 , Uni.GeorgiaUSA Present by : MARI ; FOROOTAN.
  • 2. We adressed Temporal & spatial Variation Of SM In a heterogenous landscape
  • 3. 0-History ! 1-OBJECTIVE &HYPOTHESIS 2-METHODOLOGY 3-RESULTS 4-CONCLUSION IN THESE PARTS
  • 4. SM= soil moistue LRW=little river watershed=study area LULC=LandCover-LandUse ANOVA=analyze of variance LS=landscape H-P=hydra-probe Var. =variation P.C.C =pearson correlation coefficient Remember
  • 5. Western et al. ,1999 SM is not a random phen. Sp. Var. according to Size of Samp. Area & Env. Var. Anderson et al. ,2003 Combination of Env. Factors (Soil.Veg.c,Topo,Climate) Create spatially distribution of SM Over dif.scales of space & time History
  • 6. History USDA-NASA 2003 (SMEX03) In situ devices at LRW produce Relieble inf. Of SM Moran ,2004 Cashion ,2005 Under a complex LS. Remote sensors with coarse spatial resolution produce inaccurate estimates
  • 7. Investigate Spacial var. In ground-based SM data collection From small plots (30*30) Similar to pixel size of Small EFOV remote sensors TM , ETM+& ASTER &ALI In a heterogenous landscape OBJECTIVE
  • 8. We want toAssess Suitabolity of Using small plots For field validation Of Satellites remote sensing Instruments With small EFOV( < 30m )
  • 9. TM,ETM+ ASTER & ALI All are expected To better capture Local field conditions Under landscape environmental Complexity
  • 10. Dispite Heterogeneity of study area It is possible to find Temporally & Spatiolly Homogenous SM behavior Within small areas of 30*30. Our HYPOTHESIS
  • 11. Study SM var. Within 5 dominate LULC In LRW Landscape. Another Objective
  • 12. 1- increase field knowledge of SM behavior in Hetero.LS 2-lead to better interpretation of the Satellite estimates Our Results Will
  • 14. -Study Area -Plot Data collection -Statistical Analysis
  • 16.
  • 17.
  • 18. An in situ Network 27 ground stations As a source of ground-based Point Data To 1- validate remote sensing analysis of SM and Soil tempreture& Climate 2- long term Hydrological studies In South eastern of US 2002 - 2003
  • 19. These 27 stations equipped with Steven-vitel Hydra-Probe(steven water monitoring sys.)
  • 20.
  • 21.
  • 22.
  • 23. H-P-s Operated by USDA-ARS And record SM information &Ground tempreture At 3 depths 5 , 20 , 30 m Every 30 min Typ. Installed along Agriculture field boundaries, Fence rows & pasture areas & Typ. Surounded by Native grass veg.cover.
  • 25. 8 of 27 sites Selected Surounding H-P & Associated with the In situ SM Monitoring station
  • 26.
  • 27. 30 * 03 m area Surrounded H.p And Subsequently sampled for SM SM was measured using Portable theta capacitance probe (measure dielectric conductivity similar to H.p)
  • 28. To minimize Errors We use Same equipment & Same personnel
  • 29. 3 different Soil Dataduring 2005 - Jan2006
  • 30. Data collected Randomly Within 8(30*30m) plots 1 8 16 26 32 40 50 63 66 For each plot 10-20 reading On 4 dif. Dates March11 March28 April12 May24 2005
  • 31. testing temporal stability of SM reading over a fairly short time period (here 48 h) On 2 consecutive days *Nov 30 & Dec 1 (2005) *Jan 13 & Jan 14 (2006) Systematic sampling 2
  • 32. Each reading was taken in 3 intervals in 4 directions From H.P station Total 20 sample per Plot
  • 33. At some locations Fewer than 4 directions Were evaluated Due to the presence of obstacles Such as Road and Channels 4 perpendicular direction Sampling location Hdra-probe Station 30 M 30 M
  • 34. collected from 5 field adjacent to plot areas Under the LULC; Grass ,Orchard,Bare land& Agriculture Cotton & Peanuts Associated with H.P sits: 50 , 32 , 66 & 40 3
  • 35. Each LULC 8 – 10 SM readings At 3 intervals along a 25 – 30 m transect In 4 dif.times Nov – Dec 2005 & Jan 2006
  • 36. Precipitation from each site  Raingages at H.P stations For 12-day period at intervals 5 min For each Sampling Dates
  • 38. 1- ANOVA 2- time stability anaysis 3- Tukey & tamhane hoc analysis 4-Pearson Correlation Coefficient 5- t- test (Were used to analyze Data)
  • 41. No. Of R.F For 12 day period previos to Sampling date Ranged between 3 - 6
  • 42. Max average was 10 cm In 28 March Min average was less than 2.2 In 24 May
  • 45. Nov & Dec January 2006
  • 46. During R.F events all sites received simultanous precipitation with small var. among them. SO Water supply was homogeneous for all sites prior to Sample Date SO SM dif. Can be considered As a result of Intrinsic & mostly independet of water supply
  • 47. When we compared it with precipitation record: 8  greatest cumulative prec. only for 3 Sam.Date. While 63 , 16 , 50  greatest prec. inputs for 5 other days Aand For lowest 40 , 32  Prec. Record shows they have above average These observations support the Hypothesis: SM caused by intrinsic Enviromental var. Beyond prec.acting At the local scale Mean volumetric SM & infield Variation Recorded in 8 locations Presented  8  highest valus of Vol.SM 40  lowest valus of Vol.SM
  • 49. This analys use 2 sets of variation to perform Composition between plots Variation among groups Variation within groups
  • 50.
  • 51.
  • 52. A multiple comparesionamong the plots It one by one comparsionbetween sites
  • 53. 0 = means weak relationship & More than 0 means have a relationship 1 , 2 , 3 ,… Bigger score Stronger relationship
  • 54. SO Weakest relationship Were find between 8-26 /8-40 /8-66 / 40-50
  • 55. SO Strongest Relationship are Between 26-32 / 32 – 66 / 50 -63
  • 56.
  • 57. SO Site 8 Is most unique SM Behaviuor Site 66 High level of Similarity With other sites
  • 58. Similarity of 26 & 32 *Precipitation record: similar and Less than 2.5 cm Dif.for all Samp.D. *Soil type: Both are belong to Tifton soil Series *Veg. cover: 32 short grass 26edge of agr.field in wich hay is cut for cattle consumption
  • 59. Similarity of 16 & 50 *Precipitation: Dif. Cumulative rain 10 & even 18 cm *Soil type: 16 Tifton series 50Sunsweet series *Veg. cover: Similar homogenous grass &exposed to transit agri. Equipment Influenc soil physical characteristics
  • 60. Most dissimilar sites were 8-26 / 8-40 /8-66 /40-50/50-32 Low assosiation was found between 16 &32 In total 6 Sam.D.
  • 61. 8 – 26 / 8-40 / 8-66 Dif. Combination of Soil type SO Var. in water infiltration process SO Dif. SM content 40-50 / 50-32 Dif. Cumulative rainfall
  • 63. In LRW LULC Is a greater factor affecting SM conditions Than Cumulative Rainfall
  • 64. Influnce of LULC In SM Indicated by our results in LRW. LS. That make: Dif. Evatranspiration & Soil water usage
  • 65. Spatial resolution of R.sensing Sensors That are More appropriate to Capture SM conditions under this LS. Will be defined by *LS. Fragmentation *LULC composition *Sizes of LULC fragments
  • 66. High levels of fragmetation at LRW With fragments of Small size So Moderate to Fine spatial resolutionsensors (~ 3 0 m) Are expected better suit the countinoussutdy Of SM in LRW
  • 68. Parasmetermean relative diffrence: 1-Measure how particular sample compare with Av. SM of plot 2-Indicator of Infield Variation of surface SM
  • 69.
  • 70. 26 has highest range on mean Dif. (36%-39%)
  • 71. 16 has Lowest Var. (-4%-+4%)
  • 72. Highest Av. Of mean relative Dif. Was 2.6% in 66 Followed by 8 , (2.1%) 16 (1.2 %) 26 (1.0%) Otherwise mean relative Dif. Was 0.1 % below the plot Dif. Approach Zero High level of Homogeneity Within each Sample plot
  • 73. Results indicate Samp. Point within the plots are very close to each Plot mean SO Can accurately Estimate Surface SM behavior Of Entire 30*30 m plot
  • 74. Our results shows High level of in field Homogeniety That’s in contrast with The results of similar research performed In large plots
  • 75. in our research By selecting Small LS. fragments. The in field heterogenitycasued by Topography Diffrence Was Minimize
  • 76. Stability in plots 40 & 50 Can be explained by their Relatively Homogenous LC 50  part of a larger pasture and entire plot covered by same grass type 40  part of a mechanized AGR.Field & change Veg-cover throughout growing season
  • 77. So HemogeneityVeg.Cover & Homogenietyprecipitation,Slope,Soil physical characters  High stability of SM Recorded at these 2 sites
  • 79. Was compare to evaluate if all in field locations experience similar SM VAR.s within a short period (one day in this case)
  • 80. Correlations were significant in both sets But Only for 26 , 32 , 63
  • 81. P.C.C Is an indicator of Spatial stability Of SM Point data
  • 82. Low pcc with low significant level Process is unstable in space and for time lag In which Data collected
  • 84. Computed to evaluate The Variation in Av.SM values From one day to next
  • 85.
  • 86. Results suggest that Surface SM Will notnecesserily Reflect profile conditions
  • 87. SO Remote sensing retrieving algorithms Based only in direct or indirect Quantification of Surface conditions As Temp. , SM May produce Errors When used in this LS.
  • 88. These ERRORS Can be Minimized by incorporatig in to Rem.Sen. Analysis data of Precipitation events prior to Samp.D & Infiltration analysis for soil type dominated of study area
  • 90. Discriptive statistics for SM On 4 dif. Date collection On 25-30 m long transects Related to Dif. LU Adajent to 5 plots
  • 91.
  • 92. Results shows Orchard & grass Have the wettest conditions While Cotton& peanut fields Were the driest
  • 93. Tilled AG.fiels lowest spatial variability with Av. Values around %1 Grass AG.field highest standard deviation with values btween %1.8 - %2.6 Bare land  Intermediate behavior
  • 95. ANOVA Between SM valuse for five LULC Showed Significant statistical Dif. For all 4 days
  • 96. Variation between goups showed by Anova Peanut & Cotton  Most similar with No stat.Dif Among them for any 4 days Greatest Dif. With orchard, grass & bareland Showing Stat.Dif on all Samp.Dates
  • 98. AOVA high Diffrences in SM among the plots & high Hemogeneity within them Precipitation analysis similar rainfall conditions So SM.Var. explained by in situ local conditions
  • 99. Temporal stability analysis SM has high stability within the small plots and single point can use to monitor SM Var. of all plot T-statistical analysisSMstatesin upper soil layer changes within 24H
  • 100. And finally we found stat.Dif. In SM between Dif. LULC as there adjacent plots
  • 103. A remote sensing approach that consider Homogeneous LULC ,LS fragments can be used to identify LS units of similar SM behavior under Heterogeneous landscapes
  • 104. In addition The insitu USDA-ARS network will serve better in remote sensing studies in wich sensors with fine spatial resolution are evaluated
  • 105. Thanx 4Your A 10tion Mari .forootan.1388