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1.    Possible saturated  area    Example of a digital hemispherical photograph  Saturation    should only be found near the zenith  far from the foliage        Alternative exposure settings  exposure setting based on the sky reference is not possible   If you have  time at hand and want to be as accurate as possible and can read out data on a large memory capacity  laptop every other evening  Take 2 4 photos per sampling point and evaluate visually right in the field  and at night of each field work  The photographs with the highest foliage to sky contrast are the best   thus you may want to delete all others keeping only one photograph per sampling point  Unless you  want to evaluate the uncertainty in LAI estimation per sampling point accounting for exposure errors   Fix the F stop to constant  best at 5 3   Then take picture at  1   2   3 and  2 exposure relative to the  automatic  For example if the automatic exposure is 1 125  then the four exposures would respectably    be 1 250   1   1 500  1 1000 and 1 30   2     Set up used for Canon EOS 5D Mark II wit Sigma 6mm f 3 5 EX DG Circular Fisheye at SAFE  Experimental Forest Site  Sabah  Malaysia  http   www safeproject net    At each sampling point   three images have been taken in auto bracketing mode  the camera automatically takes all  three at each go  set via the camera menu  The aperture has been set to F   9  which can be  adjusted if needed  The three images are from left  0 standard exposure   1 underexposure   1  
2.    that    Leave sample and plot names unchanged  When finished go back to Settings and   highlight Constants  set Absorption to 0 85  EAADP  Ellipsoidal leaf Angle Distribution   Parameter    1   Done only once for specific fieldwork person  Menu  use the arrow tab to the right to change   in Menu with arrow tab to File   Data Storage   Enter     Your name  e g  Samuel      Disk  internal  no memory cards inserted  thus no A B C existing in this Psion     Type  comma separated   In Menu     File  you can save your configuration    Menu  use the arrow tab to the right to change to Settings  Highlight Site and press enter     Enter new name and with arrows pointing downwards enter new geographic coordinates   Then at plot go to site far from forest edge or big opening in canopy or hold Sunscan probe   levelled above the canopy  e g  low vegetation such as short grass      there should be no   shadow of vegetation on Sunscan   Ideally  there is no direct sunlight or interspaced white   clouds but slightly overcast sky conditions      Measure beam fraction  Highlight BFrac on screen of Psion  Hold a white sheet of paper  up so that ca  1 3 or the 1m long probe is covered by its shade and then Press the button    on the Sunscan   Don t hold the shade too close to the probe   otherwise it will cut out some of the diffuse light    as well  SunData looks at the readings from the photodiodes and uses the lowest value to    calculate the Diffuse component of the incident light  It use
3.   A   Disney  M   Pellikka  P   Marchant  R  2012  Leaf area index for biomes of the    Eastern Arc Mountains  Landsat and SPOTobservations along precipitation and altitude gradients  Remote  Sensing of Environment  118  103 115     Ridler  W    amp  Calvard  S   1978   Picture thresholding using an iterative selection method   EEE Transactions  on Systems  Man  and Cybernetics  6  260 263     Weiss  M    amp  Baret  F   2010   CAN EYE V6 1 User Manual  EMMAH laboratory  Mediterranean environment  and agro hydro system modelisation   French National Institute of Agricultural Research  INRA      Weiss  M   Baret  F   Myneni  R  B   Pragn  re  A    amp  Knyazikhin  Y   2000   Investigation of a model inversion    technique to estimate canopy biophysical variables from spectral and directional reflectance data   Agronomie  20  3 22     Zhang  Y   Chen  J M    amp  Miller  J R   2005   Determining digital hemispherical photograph exposure for leaf  area index estimation  Agricultural and Forest Meteorology  133  166 181     12    
4.  and elevation  in WGS 1984 or UTM  of large field markers  like road    crossing  tall single trees  tall buildings  to provide data for satellite image ortho rectification     Measurement checklist     e Plot picture showing biome in its beauty   e GPS of plot corners and in the case of transect of sampling points   e 3 hemispherical images  upward facing  per sampling point    gt  12 per subplot following    Zhang  method       e Optional  hemispherical images that are facing downward   e 3 Sunscan readings per sampling point  36 readings per subplot   e Slope  Elevation of plot   e Estimated size of forest patch  distance to road    e Notes on soil  undergrowth cover  density  height   and leaf cover on ground    3 Hemispherical Images     camera  settings    3 1 Camera and lens    Different camera systems can be used  but each camera needs to be calibrated to define optical centre  and projection function  Calibration may be done following steps outlined in the CANEYE image  analysis software  Weiss  amp  Baret  2010  download software and manuals from    https   www4 paca inra fr can eye       Suggestions for camera systems     e 8 mega pixels Nikon Coolpix 8800 VR digital camera equipped with a fish eye Nikon FC E9  lens adapter  full frame sensor   e 12 3 megapixels Nikon D5000 SLR digital camera equipped with a Sigma 4 5mm F2 8 fisheye  lens adapter  full frame sensor   e 12 2 megapixels Canon EOS 450D equipped with a Sigma 4 5mm F2 8 fisheye lens adapter  not  a ful
5.  dissertation  Publicationes Instituti Geographici Universitatis  Helsingiensis p  A147     Gonsamo  A    amp  Pellikka  P   2008   Methodology comparison for slope correction in canopy leaf area index    estimation using hemispherical photography  Forest Ecology and Management  256  749 759     Gonsamo  A    amp  Pellikka  P   2009   The computation of foliage clumping index using hemispherical  photography  Agricultural and Forest Meteorology  149  1781 1787     Jacquemoud  S    amp  Baret  F   1990   Prospect   A model of leaf optical properties spectra  Remote Sensing of  Environment  34  75 91     Jonckheere  B   Muys  B    amp  Coppin  P   2005 a   Allometry and optical in situ LAI determination  A case study  in Belgium  Tree Physiology  25  723 732     Jonckheere  I  G  C   Muys  B    amp  Coppin  P  R   2005 b   Derivative Analysis for In Situ High Dynamic Range    Hemispherical Photography and Its Application in Forest Stands  IEEE Geoscience and Remote Sensing  Letters  2  296 300     Jonckheere  I  G  C   Fleck  S   Nackaerts  K   Muys  B   Coppin  P   Weiss  M    amp  Baret  F   2004   Review of    methods for in situ leaf area index determination     part I  Theories  sensors and hemispherical photography   Agricultural and Forest Meteorology  121  19 35     Lang  A  R  G    amp  Yueqin  X   1986   Estimation of leaf area index from transmission of direct sunlight in  discontinuous canopies  Agricultural and Forest Meteorology  37  229 243   Pfeifer  M   Gonsamo
6. Manual to measure and model leaf area index  and its spatial variability on local and landscape scale    Dr Marion Pfeifer   amp  Dr Alemu Gonsamo       February 7   2014      Ecology and Evolution  Faculty of Natural Sciences  Imperial College of Science  Technology and    Medicine  UK  marion pfeifer   gmail com      Geography Department  University of Toronto  100 St  George Street  Toronto  M5S 3G3     Canada  gonsamoaQ geog utoronto ca    To be used as guide in the projects ICIPE CHIESA        Climate Change Impacts on Ecosystem    Services and Food Security in Eastern Africa     http   chiesa icipe org   funded by Ministry for Foreign  Affairs of Finland  and TZ REDD in Tanzania  funded by the Ministry of Foreign Affairs  Norway         Key points    Landscape scale  Stratified random sampling design to capture heterogeneity within  biomesFriday  07 February 2014Friday  07 February 2014   Equipment  hemispherical camera  tripod  compass  camera  lens  lens adapter  if needed   and  Sunscan instrument  batteries for Psion handheld  incl  backup battery   markers  level  GPS   more batteries           Measure GPS of land markers  points observable from space such as trees  big houses    Measure GPS of plots and biome types   Take GPS of plot corners  V ALERI plots  and sampling points  Transects    Hemispherical  measure sky exposure   decrease shutter speed by two stops or employ auto   bracketing    Sunscan  3 SunScan readings per sampling point taken from different ang
7. TATION   If there is slope  then upscaling using high resolution satellite to    coarse resolution may not work     To fasten the 1mage processing step  the user should always keep the same position when acquiring  the image  This will allow the operator to apply the same mask to all the images at once  However   this should only become relevant when taking downward looking pictures  In the upward looking    images  best use remote control to set off camera or use automatic countdown function     Shadows in the image will make the class allocation more difficult  A fish eye field of view is large     Therefore  make sure that there is no one or anything else  bag  instrument  etc   present on the image     3 5 Image extraction  processing and analysis    After downloading from the camera system  each image has to be pre processed  The pixel  brightness values for the blue band are extracted from each RGB image to achieve maximum  contrast between leaf and sky  because absorption of leafy materials is maximal and sky  scattering tends to be highest in that band  Jacquemoud  amp  Baret  1990  Jonckheere et al    2005 b      Marker  amp  GPS Image processing  Ria       Image download    i  Extraction of blue band K     l    Thresholding         CAN EYE v6           e Vegetation versus non vegetation     LAI based on gap fraction       i ca South      Marker  amp  GPS e Plotestimates   gt  8 images    Thresholding procedures have been developed in order to avoid subjective decisi
8. ands in  Tanzania are more heterogeneous  Otherwise it would be very good to have as many plots randomly  distributed in forest stratified patches so that one may be able to use them to validate global LAI or    other biophysical products        The more variable the biome  the more sampling plots or the larger the plot size     2 Sampling Design on local scale    To capture heterogeneity of vegetation canopy structure and biomass within a stratum  e g  Vegetation  plot as specified for RAINFOR carbon measurement protocols   five subplots  SP  should be sampled   The subplots are distributed randomly within the plot  e g  red  SP1 to SP5 or grey  SP1 to SP5    Subplot size may vary with plant functional type sampled  but ideally is 20 m x 20 m unless sampling  follows a linear transect  Mark plot corners with red yellow tape and record the coordinates of the plot    comers     Transect plots are very good to save time on field data collection  For example you can run four  transects for 1 km   To avoid sampling bias  chose a starting point and then follow the linear transect  running through the stratum along the south     north line with measurements every 10 m to 20 m   Ideally  there 1s a land marker at the or close to the starting point  which is obvious to detect from    space for locating the transect on the satellite image  Take a GPS reading at each measurement point     Marker  amp  GPS  M2 North       Marker  amp  GPS  MI    It is essential to record GPS coordinates
9. egetation  Compute difference between LAI 80cm per    plot and LAI ground level to get LAI of low vegetation     5 References    Baret  Morissette  T  J   Fernandes  R  A   Champeaus  J  L   Myneni  R  B   Chen  J   Plummer  S   et al   2006   Evaluation of the representativeness of network of sites for the global validation and intercomparison of land  biophysical products  Proposition of the CEOS BELMANIP  IEEE Transactions on Geoscience and Remote  Sensing  44  1794 1803    Breda  N  J   J   2003   Ground based measurements of leaf area index  a review of methods  instruments and  current controversies  Journal of Experimental Botany  54  2403 2417    Garrigues  S   Allard  D   Weiss  M    amp  Baret  F   2002   Comparing VALERI sampling schemes to better  represent high spatial resolution satellite pixel from ground measurements  How to characterize an ESU   Available for download at http   w3 avignon inra fr valeri methodology  samplingschemes pdf  accessed    17 08 2011      11    Garrigues  S   Lacaze  R   Baret  F   Morisette  J  T   Weiss  M   Nickeson  J  E   Fernandes  R   Plummer  S    Shabanov  N  V   Myneni  R  B   Knyazikhin  Y    amp  Yang  W   2008   Validation and intercomparison of  global Leaf Area Index products derived from remote sensing data  Journal of Geophysical Research  113   doi  10 1029 2007JG000635     Gonsamo  A   2009   Remote sensing of leaf area index  enhanced retrieval from close range and remotely    sensed optical observations  Academic
10. l frame sensor resulting in images being cropped at the top and at the bottom   e Personal favourite  21 1 megapixels Canon EOS 5D Mark II Digital SLR camera body equipped  with SIGMA 8mm f 3 5 EX DG Circular Fisheye  using a VANGUARD Aluminium Alloy  Tripod Alta 263AGH     GPR System  Grip  Position  Release      3 2 Camera settings     exposure    and resolution    Make sure the camera is in fine mode  Jpeg  or Hi mode  Tiff   with the highest resolution  The    camera needs to be set to    manual    and    fisheyel    modes  if applicable  Check your camera manual     Exposure settings  The correct exposure is to make the sky appear white  Using automated exposure  may result in unreliable LAI estimates  Zhang et al   2005   Thus  use the hereafter called    Zhang  method      Two stops of overexposure relative to the sky reference     This sky reference reading should  be made in a large opening outside the forest stand  which provides an unobstructed sky view in all  azimuthal directions  With experience in angular variations of sky radiance  this reference reading can  also be made in small openings  When the camera   s aperture size is fixed to ensure a consistent field  of view  a decrease of the camera   s shutter speed by 2   3 stops will provide the desired exposure   Meaning  if the sky reference exposure time were determined to be 1 1000 s  F5 3   a series of    photographs would be taken with the aperture fixed at F5 3 and the shutter speed decreasing to 1 250  
11. les    Contents    1 Sampling Design on landscape scale    Sampling follows a stratified sampling protocol with random point selection within strata   disproportionate stratification   Pre selection of strata takes place according to following criteria   e Rainfall classes  e g    lt  500  500   800  800  1100  1100     1500  1500 1800   gt  1800 mm    e Disturbance levels  no     low intensity     moderate     high intensity  optional  disturbance  categories  fire     logging     charcoal   e Plant functional types  Bushland     Woodland     Forest     Plantation   Cropland  e WDPA  World Database on Protected Areas  http   www wdpa org   categories  forest  reserves  national parks  nature reserves  unprotected  game management parks  e Age classes  e g  forests  depending on previous disturbances     if known     e Crop types  Corn  Rice  Sisal     Woody  savannah vegetation and croplands are highly seasonal in tropical East Africa  driven by  fire  rainfall and human land use  Thus  ideally  measurements will be repeated within the season to  measure intra annual variability of vegetation canopy structure as a base for correlations with    environmental parameters later on     Field plots should be placed in uniform vegetation of a specific biome  e g  forest  at a distance of  gt   100 m from the edge  to allow for coarse pixel validation in subsequent satellite image analyses    This will apply mostly to forests  woodlands and woody  savannah  systems  since many cropl
12. nckheere et al   2004   The aim is to avoid sun glares or    sunflecks when taking upward hemispherical images to avoid very over exposed parts in the image    6    which may make the class allocation more difficult in subsequent image processing  If there are some     it is still possible to mask then during the post processing     Be sure that the camera is the most horizontal  camera body levelled     best done with a level  as  possible when acquiring a hemispherical image  If the image is taken in the upward direction  tall  canopy   use a tripod  The upper picture margin should be facing exactly northward at each image   take a compass   at 1m above ground  or another height as long as you always use the same   Ideally   you got a full frame sensor camera body and a nice fisheye lens on it  Don t forget to take the adapter    linking camera body and tripod into the field with you     Slope  Slope affects LAI estimation using hemispherical images  Gonsamo  amp  Pellika  2009   Take  take pictures on the flat ground so that the point spread contribution of the surrounding landscape to    remote sensing pixel is minimal if the field is large and uniform     When working on slopes  always take picture levelled to horizontal ground  Gonsamo  amp  Pellikka   2008  and measure the slope and its orientation  And again the forest patch should at least be more  than 1 pixel  1 km2  on uniform slope  for upscaling to moderate spatial resolution sensors such as  MODIS and SPOT VEGE
13. ons by the user and  to identify the optimal brightness threshold to distinguish vegetation from sky  Jonckheere et al   2005  b   We use the global Ridler method  Ridler  amp  Calvard  1978  for image thresholding  see Pfeifer et  al   2012   because of reliable results in hemispherical photography studies  Jonckheere et al   2005 a   Gonsamo  amp  Pellikka  2008   The resulting binary images are analysed using the canopy analysis  software CAN EYE  Weiss  amp  Baret 2010  http   www paca inra fr can  eye  limiting the field of view  of the lens to values between 0 and 60   to avoid mixed pixels and thus misclassifications  Certain sky  conditions can complicate classification of image pixels into vegetation and non vegetation  e g     sunflecks and dark clouds  Images can be edited in processing software to mask such areas     CAN EYE estimates mean effective LAI for each plot  LAIgpr  LAI assuming randomly located  foliage  based on a series of  at least 8  images from measured gap fraction  Weiss  amp  Baret  2010    LAlgpr is derived by inversion of the Poisson model using look up tables and assuming an ellipsoidal  distribution of leaf inclination  Weiss et al   2000   A clumping index is computed using the Lang  amp   Yueqin  1986  logarithm gap fraction averaging method and used in a modified Poisson model  which  is then inverted to estimate LAIrygug  the LAI taking into account canopy clumping  Note that  estimated LAI rug includes not foliage materials such as stem
14. overexposure     e AF  Autofocus   On  Switch on side of lens    e Av mode   e In Menu  settings      One Shot     File Numbering  Continuous     Quality  Raw   Large JPEG     Picture Style Standard     C Fn I  Exposure  4   Bracketing Autocancel  OFF     Expo comp  AEB  enter and mark the bracketing points to 0   1  Underexposure    1   Overexposure    e Set F to 9 0  Start switch to On and check F  Then start switch to line  Little wheel on top  of camera body  behind photo button      turn to change F to desired one  Then change  start switch back to On     Resolution  The image resolution and the compressing rate  if there is  will have a significant impact  on the image analysis  Results will be better with a high resolution and a low compressing rate  For  example  when the leaves are small  coniferous forest   it is recommended to increase the resolution    of the image so that less mixed pixels are present in the image     3 3 Tips and tricks in different vegetation structure    Very Short Canopy   lt  30 cm height   For very short canopies such as young crops  the digital camera  must be placed looking downward  not too close from the foliage  so that one leaf does not cover the  whole field of view  On the other hand  the camera should not be placed too high so that the user does  not observe a sky ring in the image  Therefore  an average height of 60 to 80 cm above the last leaf  appears reasonable  Note that the advantage of downward looking photographs is the pos
15. s  trunks  branches  twigs and plant    reproductive parts and is more accurately called plant area index  Breda et al   2003      Datasheet    LAI using hemispherical images in SAFE vegetation monitoring plots    Nama  Name      Block  Plot  e g  Fragment C  Plot 621         Vegetation Plot   SAFE Experiment  25 m x 25 m  Pictures  3 each  e g  when    reading 432 from camera  430   431  432      lt                        N A            ue un      7                  i     LAI Pictures            m            P d    e    Centre  6  o                   N        ma       7     I  ITI             GPS coordinates  LAI   GPS  Point  1 Lat   Long    4 Lat  Long    10 Lat    Long    7 Lat  Long       4 Sunscan Instrument     Measuring in the field    Fieldwork step by step     1     2   3     4     5     6     Switch the Psion on after connecting the probe  the thing with the 1 m long probe  to the  psion with the accompanying cable   Hold both symbols  V E and set remote link to off     when finished with measuring in field set remote link on for later readout into PC   Note  pressing both N  X will exit from any application that is running     Highlight Sunscan icon and enter the program  Continue by pressing enter    Done once when doing fieldwork in a specific region  Go to Menu  use the arrow tab to   change to Settings  Highlight Time and Date  e g  Tanzania  e g  GMT   3  depending on   time in year      Enter  Back to Settings and Highlight Display  LAI as display  check for
16. s the highest photodiode values to    10    calculate the Total incident  and uses these two values to calculate and display the Beam    Fraction     Thus  if the background light changes strongly  e g  sudden clouds in front of sun causing  different light      measure beam fraction again  Sometimes you may encounter errors and you  will have to re measure the beam fraction anyway  This may happen more often when you    think so don t lose your spirit     7  Go QUICKLY to S1 of plot  see plot setup above   at each sampling point take three Sunscan  readings from three different directions at about 80 to 100 cm above the ground  Make sure  your shadow does not appear on the 1 m probe  Hold the Probe levelled  no tilting or fancy  movements   All readings get appended one after the other  Go to S2 and take another three  readings from three different directions holding the Probe levelled  go to 53  etc      Check in between  finishing at sample 6 you should have taken 18 readings and be ready  for reading LAI number 19        f you went wrong  best start from beginning setting up new plot name  You will get very  confused otherwise  believe me       At the end  in case you have 12 sampling points  you should have done 36 LAI readings     If you are interested in getting the ground vegetation LAI you may want to run again through the  plot taking   at each Sample point     3 readings from three different directions but holding the  probe levelled just at ground level into the v
17. sibility to get  a better spatial representation by increasing the distance between the camera and the canopy while  keeping it not too far away to be able to get a clear image of vegetation elements  minimizing the    mixed pixels problem     Short canopy  between 30 and 70 cm   The digital camera can be placed looking downward with the  Same recommendations as for very short canopies  It can also be placed horizontally on the ground   looking upward  In this case  be sure that the presence of the camera on the ground does not change    the canopy structure     Tall canopy without understorey   gt  70 cm   The camera should be placed at ground level  looking  upward  It 1s necessary also to take care of not modifying the canopy structure when positioning the    camera on the ground     Tall canopy with understorey  Two series of hemispherical images can be acquired  one looking  downward to characterize understorey  the other looking upward to estimate tree characteristics  The  two kind of images must be processed as two separate series  The resulting characteristics can then be    recombined to represent the whole canopy     3 4 Measurements in the plot    Sky conditions  All images sampled in a subplot plot must be acquired in similar illumination  conditions  so that the colour dynamics does not vary a lot between all the images that are processed  together  Ideally measurements should be performed under overcast conditions to minimize  anisotropy of the sky radiance  Jo
    
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