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GIO-GL Lot 1, GMES Initial Operations
Date Issued: 30.06.2015
Issue: I2.10
Gio Global Land Component - Lot I
”Operation of the Global Land Component” Framework Service Contract N° 388533 (JRC)
PRODUCT USER MANUAL
WATER BODIES (WB)
VERSION 1 (SPOT-VGT, PROBA-V)
AFRICA
Issue I2.10
Organization name of lead contractor for this deliverable: VITO
Book Captain: Bruno Smets (VITO)
Contributing Authors: Davy Wolfs (VITO)
R. D’Andrimont (UCL)
Jacobs Tim (VITO)
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Dissemination Level PU Public X
PP Restricted to other programme participants (including the Commission Services)
RE Restricted to a group specified by the consortium (including the Commission Services)
CO Confidential, only for members of the consortium (including the Commission Services)
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Document Release Sheet
Book captain: Bruno Smets Sign Date 30.06.2015
Approval Roselyne Lacaze Sign Date 03.07.2015
Endorsement: Michael Cherlet Sign Date
Distribution: Public
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Change Record
Issue/Rev Date Page(s) Description of Change Release
28.03.2013 All Geoland2 document, Issue I1.13, 08.06.2011 I1.00
I1.00 10.03.2015 All Updated to Copernicus template, removed
GWW layer, added PROBA-V
I2.00
I2.00 30.06.2015 All Update after external review and according to
release I2.10 of the ATBD
I2.10
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TABLE OF CONTENTS
1 Background of the document ................................................................................................ 9
1.1 Executive Summary .................................................................................................................... 9
1.2 Scope and Objectives ................................................................................................................. 9
1.3 Content of the document ........................................................................................................... 9
1.4 Related documents .................................................................................................................. 10
1.4.1 Applicable documents ................................................................................................................................ 10
1.4.2 Input ............................................................................................................................................................ 10
1.4.3 External document ...................................................................................................................................... 10
2 Review of Users Requirements ............................................................................................ 11
3 Algorithm ............................................................................................................................ 14
3.1 Overview ................................................................................................................................. 14
3.2 Retrieval Methodology ............................................................................................................ 15
3.2.1 Background ................................................................................................................................................. 15
3.2.2 Input data ................................................................................................................................................... 15
3.2.3 Processing steps .......................................................................................................................................... 19
3.2.4 Limitations .................................................................................................................................................. 26
4 Product Description ............................................................................................................. 28
4.1 File Format ............................................................................................................................... 28
4.2 Product Content ....................................................................................................................... 30
4.2.1 Image Files .................................................................................................................................................. 30
4.2.2 ‘WB’ quicklook image ................................................................................................................................. 32
4.3 Product Characteristics ............................................................................................................ 32
4.3.1 Projection and Grid Information ................................................................................................................. 32
4.3.2 Spatial information ..................................................................................................................................... 33
4.3.3 Temporal Information ................................................................................................................................. 33
4.3.4 Data Policies ................................................................................................................................................ 34
4.3.5 Access and Contacts ................................................................................................................................... 34
5 Validation ........................................................................................................................... 35
6 References ........................................................................................................................... 36
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List of Figures
Figure 1: Algorithm overview .......................................................................................................... 15
Figure 2: Spectral Response Functions of VGT1, VGT2, and the three PROBA-V cameras,
superimposed with a spectrum of green grass. ....................................................................... 18
Figure 3 : Coastal erode (arid mask), blue = sea, white = detection area, grey = erode area ........ 19
Figure 4 : SWB algorithm representation. T means that a threshold is applied. ............................. 20
Figure 5 : Data flow of the seasonality detection ............................................................................ 23
Figure 6: Zone for which the VGT4AFRICA was designed (in black) ............................................. 26
Figure 7: Region of Interest. Blue (inner) rectangle indicates water bodies algorithm boundary. Red
(outer) rectangle indicates product delivery boundary. ............................................................ 29
Figure 8: The cut-out of tiles ........................................................................................................... 33
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List of Tables
Table 1: GCOS requirements for water bodies as Essential Climate Variables (GCOS-154, 2011)
................................................................................................................................................. 12
Table 2: geoland2 User Requirements for Water Bodies ( 1 the relative accuracy; 2 absolute
accuracy) ................................................................................................................................. 13
Table 3: Spectral characteristics of VEGETATION-2 sensor .......................................................... 16
Table 4: Spectral characteristics of the PROBA-V sensor .............................................................. 17
Table 5: SWB thresholds description .............................................................................................. 21
Table 6 : Consecutive detection rule ............................................................................................... 22
Table 7 : List of flags for the seasonality detection. ........................................................................ 26
Table 8: Definition of the continents. ............................................................................................... 29
Table 9: WB layer legend ................................................................................................................ 30
Table 10: WBFLAG legend ............................................................................................................. 31
Table 11: MVM legend .................................................................................................................... 31
Table 12: PW legend ...................................................................................................................... 31
Table 13: Quicklook color coding scheme ...................................................................................... 32
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List of Acronyms
ATBD Algorithm Theoretic Basis Document
CCD Charged Coupled Device
CLDVW Contrast Local of the Difference NDVI-NDWI
CLMIR Contrast Local of MIR
CLV Contrast Local of NDVI
CLW Contrast Local of NDWI
Dekad 1/3th of a month, starting at day 1, 11 or 21
ECV Essential Climate Variables
EumetCast EUMETSAT’s Broadcast System for Environmental Data
FP Framework Program of the European Community for research, technological
development and demonstration activities
GCOS Global Climate Observing Systems
Geoland2 FP7 funded project on land monitoring
GIO GMES Initial Operations
GL Global Land
GMES Global Monitoring for Environment and Security
GTN-L Global Terrestrial Network Lakes
IFOV Instantaneous Field of View
JRC Joint Research Centre of the European Union at Ispra, Italy
MIR Middle Infrared
MODIS Moderate Resolution Imaging Spectroradiometer
MVM Manually Validated Map
NDVI Normalized Difference Vegetation Index
NDWI Normalized Difference Water Index
NIR Near Infrared
NRT Near-real time
PROBA-V satellite for earth observation
PUM Product User Manual
RGB Red, Green and Blue
S1 1 day Synthesis product from PROBA-V
SMAC Simplified Method for the Atmospheric Correction
SRTM Shuttle Radar Topography Mission
SPOTx Satellite for earth Observation
SWIR Short Wavelength Infrared
TOC Top Of Canopy
VGT VEGETATION sensor on SPOT platform
WB Water Bodies
XML eXtensible Markup Language
ZIP compression format
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1 BACKGROUND OF THE DOCUMENT
1.1 EXECUTIVE SUMMARY
The Global Land (GL) Component in the framework of GMES Initial Operations (GIO) is earmarked
as a component of the Land service to operate “a multi-purpose service component” that will
provide a series of bio-geophysical products on the status and evolution of land surface at global
scale. Production and delivery of the parameters are to take place in a timely manner and are
complemented by the constitution of long term time series.
The Global Land service currently provides a Water Bodies version 1 product that monitors
the dynamics of water bodies over Africa at 1km resolution. This product results from the
algorithm calibrated over semi-arid regions and developed at African continental scale: the
Small Water Bodies (SWB) algorithm. In addition, a Permanent Water mask is provided as a
static layer. The algorithm was run on images from SPOT-VEGETATION (SPOT-VGT) but
the sensor is terminated as Earth Observation mission by May 2014. The algorithm was
tuned to the PROBA-V 1km datasets to ensure the continuity of the service.
The Product User Manual (PUM) is a self-contained document which gathers all necessary
information to use the product on an efficient and reliable way.
This document describes the Water Bodies V1 products from SPOT-VEGETATION or PROBA-V
data. The product is calculated on a 10-daily basis, and made available to the user in near-real
time every 10 days. The product is provided for the entire Africa continent, although it has been
primary designed for the semi-arid region (Sahel).
1.2 SCOPE AND OBJECTIVES
The Product User Manual (PUM) is the primary document that users have to read before handling
the products.
It gives an overview of the product characteristics, in terms of algorithm, technical characteristics,
and main validation results.
1.3 CONTENT OF THE DOCUMENT
This document is structured as follows:
Chapter 2 recalls the users requirements
Chapter 3 presents a description of the algorithm.
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Chapter 4 describes the technical characteristics of the product.
Chapter 5 summarizes the validation procedure and the results.
1.4 RELATED DOCUMENTS
1.4.1 Applicable documents
AD1: Annex II – Tender Specifications to Contract Notice 2012/S 129-213277 of 7th July 2012
AD2: Appendix 1 – Product and Service Detailed Technical requirements to Annex II to Contract
Notice 2012/S 129-213277 of 7th July 2012
1.4.2 Input
Document ID Descriptor
GIOGL1_SSD Service Specifications of the Copernicus Global Land
Service
GIOGL1_ATBD_WB-V1 Algorithm Theoretical Basis Document of the Water Bodies
Version 1
GIOGL1_ATBD_PROBA2VGT Algorithm Theoretical Basis Document of PROBA-V pre-
processing
GIOGL1_SVP Service Validation Plan Copernicus Global Land Service
GIOGL1_QAR_WBV1 Quality Assessment Report of the SPOT/VGT and
PROBA-V WB V1 products
1.4.3 External document
Document ID Descriptor
SPOT-VGT http://www.spot-vegetation.com/index.html
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2 REVIEW OF USERS REQUIREMENTS
According to the applicable document [AD2], the users’ requirements define the features required
for the water bodies.
Definition: permanent and seasonal water bodies, natural and man-made, independently
of their size. Include but are not restricted to the lakes of the Global Terrestrial Network for
lakes (GTN-L).
Geometric properties:
o The baseline pixel size shall be 1km.
o The target baseline location accuracy shall be 1/3 of the at-nadir instantaneous field
of view.
o Pixel co-ordinates shall be given for centre of pixel
Geographical coverage:
o Geographic projection: regular lat-long
o Geodetical datum: WGS84
o Pixel size: 1/112° - accuracy: min 10 digits
o Coordinate position: centre of pixel
o Global window coordinates:
Upper Left:180°W-74°N
Bottom Right: 180°E 56°S
o African window coordinates:
Upper Left: 26°W – 38°N
Bottom Right: 60°E - 35°S
Time definitions:
o As a baseline, the biophysical parameters are computed by and representative of
dekad, I.e. for ten-day periods (“dekad”) defined as follows: days 1 to 10, days 11 to
20 and days 21 end of the month for each month of the year
o The output data shall be delivered in a timely manner, i.e. within 3 days after the
end of each dekad.
Ancillary information:
o The number of measurements per pixels used to generate any synthesis period
o the per-pixel date of the individual measurements or the start-end dates of the
period actually covered
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o quality indicators, with explicit per-pixel identification of the cause of anomalous
parameter result
Accuracy requirements:
o Baseline: wherever applicable the bio-geophysical parameters should meet the
internationally agreed accuracy standards laid down in the document “Systematic
Observation Requirements for Satellite-Based Products for Climate”. Additional
details to the satellite based component of the Implementation Plan for the Global
Observing System for Climate in Support of the UNFCCC are available in the
document WMO GCOS-#154, 2011 (see Table 1)
o Target: considering data usage by that part of the user community focused on
operational monitoring at (sub-) national scale, accuracy standards may apply not
on averages at global scale, but at a finer geographic resolution and in any event at
least at biome level.
Regarding this latter accuracy requirement, the water surface biophysical variable corresponds to
two different Essential Climate Variables (ECV), i.e. the “land cover” and the “lakes”.
Variable/ Parameter
Horizontal Resolution
Vertical Resolution
Temporal Resolution
Accuracy Stability
Maps of land-cover type
250 m N/A 1 year
15% (maximum error of omission and commission
in mapping individual
classes), location accuracy better than 1/3 IFOV
with target IFOV 250m
15% (maximum error of omission and commission
in mapping individual
classes), location accuracy better than 1/3 IFOV
with target IFOV 250m
Areas of GTN-L
Equivalent to 250 m
N/A monthly
5% (maximum error of omission and commission
in lake area maps), location accuracy better than 1/3 IFOV
with target IFOV 250m
5% (maximum error of omission and commission
in lake area maps), location accuracy better than 1/3 IFOV
with target IFOV 250m
Table 1: GCOS requirements for water bodies as Essential Climate Variables (GCOS-154, 2011)
Additional user requirements
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The users requirements expressed during geoland2/BioPar are shown in Table 2. Three accuracy
levels were defined: Optimal, Target and Threshold.
Table 2: geoland2 User Requirements for Water Bodies ( 1 the relative accuracy;
2 absolute accuracy)
Accuracy
Threshold Target Optimal
Water Bodies 1 20% 15% 10%
Seasonality 2 1 dekad
The above requirements are indicative. They have to be adapted to the Global Land products and
clarified by the user board of the Global Land service.
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3 ALGORITHM
3.1 OVERVIEW
The Water Bodies product identifies pixels covered by water. The areas of water bodies are
understood here with respect to the instrument resolution, i.e. surfaces more or less covered by
water with a size of about 1 km2 (Bartholomé and Combal, 2006).
At continental scale, it is difficult to expect a water body to have sufficiently specific properties to be
recognized easily, everywhere and in any condition from space. Indeed, from an ecological point of
view, the only thing that is sure is that a water body is characterized by permanent or seasonal
water logging. Due to the large geographical context, a large range of vegetation conditions may
be expected over these surfaces. Moreover the spectral behavior of water may vary according to
sediment load and the development of micro-organisms. Therefore there is no particular spectral
signature to confidently rely on for water body identification.
The termination of SPOT-VGT on May 2014 and the use of datasets from a different sensor
(PROBA-V) imply the adaptation of the methods to detect water.
Erreur ! Source du renvoi introuvable. shows that the algorithm is performing two algorithm
steps:
1. Detection of the water body, based on the 10-daily Top Of Canopy reflectance input and
the previous dekad reflectances. It provides the Small Water Bodies (SWB) layer using the
ARID mask input to filter out coastal effects.
2. Calculation of the seasonality parameters from the water body, based on the temporal
profile of 45 dekads. It calculates the Water Bodies Start Date (WBSTARTDATE), Water
Bodies End Date (WBENDDATE) and Water Bodies Flag (WBFLAG) layers.
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Figure 1: Algorithm overview
Both processing steps are described in more details in the next paragraphs.
The product is associated with a separate product package, representing two static layers:
1. Manual Validation Mask (MVM) (see )
2. Permanent Water Mask (PW) derived from the 90m SRTM SWBD Water Body Data PSG
v2.0 [Caroll et al., 2009] and the MOD44W product.
3.2 RETRIEVAL METHODOLOGY
3.2.1 Background
The original algorithm (Gond et al., 2004) was developed for the VGT4AFRICA WB (SWB)
products by the JRC as part of the FP4 “improvements for the VEGETATION mission” shared cost
action project.
3.2.2 Input data
Two different sets of input data are used in the Water Bodies Detection Algorithm, i.e. 10-dailyTop
Of Canopy reflectances (S10-TOC) and a coastal erode mask (ARID mask).
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3.2.2.1 S10 Top Of Canopy reflectances
3.2.2.1.1 SPOT-VGT
The VGT-S10 (Top of Canopy 10-daily synthesis reflectance) products are generated and provided
by the SPOT VEGETATION program through VITO (http://free.vgt.vito.be/).
Since April 1998 and till May 2014, the VEGETATION sensor has been operational on board the
SPOT 4 and 5 earth observation satellite system. It provides a global observation of the world on a
daily basis. The instrumental concept relies on a linear array of 1728 CCD detectors with a large
field of view (101°) in four optical spectral bands described in Table 3. Although very similar, some
differences between VEGETATION 1 and VEGETATION 2 instruments have to be noticed [SPOT-
VGT], particularly regarding the spectral sensitivity (Table 3).
Acronym Centre (nm) Width (nm) Potential Applications
B0 450 40 Continental ecosystems - Atmosphere
B2 645 70 Continental ecosystems
B3 835 110 Continental ecosystems
SWIR 1665 170 Continental ecosystems
Table 3: Spectral characteristics of VEGETATION-2 sensor
The spatial resolution is 1.15 km at nadir and presents minimum variations for off-nadir
observations. The 2200 km swath width implies a maximum off nadir observation angle of 50.5°.
About 90% of the equatorial areas are imaged each day, the remaining 10% being imaged the next
day. . For latitudes higher than 35° (North and South), all regions are acquired at least once a day.
The multi-temporal registration is about 300 meters.
The 10-day synthesis (S10) provides surface reflectance values based on a selection of the “best”
measurements on the entire period. The actual selection is based on the maximum NDVI value
from the clear observations within the compositing period (Holben, 1986).
3.2.2.1.2 PROBA-V
PROBA-V Top Of Canopy (S10-TOC) 10-daily synthesis products are generated and provided by
the PROBA-V project through VITO (http://proba-v.vgt.vito.be/ ).
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The PROBA-V satellite was launched at 6 May 2013 and was designed to bridge the gap in space-
borne vegetation measurements between SPOT-VGT (March 1998 – May 2014) and the upcoming
Sentinel-3 satellites, scheduled for launch in 2015/2016. The mission objective is to ensure
continuity with the heritage of the SPOT-VGT mission.
PROBA-V flies at an altitude of 820 km in a sun-synchronous orbit with a local overpass time at
launch of 10:45 h. Because the satellite has no onboard propellant, the overpass times are
expected to gradually differ from the at-launch value. The instrument has a Field Of View of 102o,
resulting in a swath width of 2295 km. This swath width ensures a daily near-global coverage
(90%) and full global coverage is achieved every 2 days.
The optical design of PROBA-V consists of three cameras. Each camera has two focal planes, one
for the short wave infrared (SWIR) and one for the visible and near-infrared (VNIR) bands. The
VNIR detector consists of four lines of 5200 pixels. Three spectral bands were implemented,
comparable with SPOT-VGT: BLUE, RED, and NIR (see Table 4). The SWIR detector contains the
SWIR spectral band and is a linear array composed of three staggered detectors of 1024 pixels.
The spectral response functions of the four spectral bands from the three PROBA-V cameras are
compared to those of SPOT/VEGETATION1 and 2 in Figure 2.
The PROBA-V S10-TOC synthesis product provides the ground surface reflectance in the four
spectral bands corresponding to the selected measurement, the atmospheric correction being
performed using SMAC 4.0 [Rahman et Dedieu, 1994]. The selection of the pixel in the 10-days
composite is done using the maximum NDVI value from the clear observations within the
composite period (Holben, 1986).
To provide a consistent time-series with the SPOT-VGT dataset, the PROBA-V reflectance bands
are spectrally corrected before applying the algorithm [GIOGL1_ATBD_PROBA2VGT].
Acronym Centre (nm) Width (nm) Potential Applications
B0 463 46 Continental ecosystem - Atmosphere
B2 655 79 Continental ecosystem
B3 845 144 Continental ecosystem
SWIR 1600 73 Continental ecosystem
Table 4: Spectral characteristics of the PROBA-V sensor
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Figure 2: Spectral Response Functions of VGT1, VGT2, and the three PROBA-V cameras,
superimposed with a spectrum of green grass.
3.2.2.2 ARID Mask
To avoid confusion of detected water bodies at the coastal area, an erode zone of 25 km (being
approximately half of a detection cell, see paragraph Erreur ! Source du renvoi introuvable.) has
been installed, as shown in Figure 3. This erode zone is named ‘arid’ mask. Through this arid
mask, the detection of contrast between sea and land pixels, resulting in false detections, is
removed.
The water body detection is performed across the full continent, however any detected bodies at
the eroded area (25 pixels around the coast and permanent big lakes) are ignored and represented
by a sea value. The big lakes have a size larger than 45km2 and similarly as the coastal border,
false detections are removed through applying the arid mask.
As shown in Figure 3, the East African Great Lakes are coded as sea in SWB due to the arid
mask.
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Figure 3 : Coastal erode (arid mask), blue = sea, white = detection area, grey = erode area
3.2.3 Processing steps
As shown previously in Erreur ! Source du renvoi introuvable. there are two main processing
steps to generate the WB v1 product:
1. Water body detection
2. Seasonality calculation
The following sections briefly outline these steps. More information can be found in
[GIOGL1_ATBD_WB-V1].
3.2.3.1 Water Body detection
Water body identification is carried out each time a new 10-days synthesis (S10) product is made
available. Surface water is detected using the spectral “anomalies” of the water pixels according to
their surrounding environment, as shown in Figure 4. This is done by computing the difference
between “regional” average of the channels and each pixel value for specific spectral bands or
indexes such as NDVI and NDWI. Considering that we are looking for targets that are more or less
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the size of instrument ground resolution, i.e. 1 km2 and that water bodies are rather rare features in
the landscape, it was assumed that a “region” of about 2000 km2 would be sufficient to minimize
the weight of water body spectral properties in the average. Therefore, for each pixel, the average
value of the channels and derived indices are computed on a 45 × 45 km cells, then the difference
between the pixel’s original value and the average are computed. Water body identification is
finally obtained by simply applying thresholds on these final values.
Figure 4 : SWB algorithm representation. T means that a threshold is applied.
Normalized Difference Vegetation Index (NDVI) is a ratio used to characterize the vegetation
amount. It is defined as “NDVI = (NIR-Red) / (NIR+Red)”. The average (mean) of NDVI computed
on 45 pixels x 45 pixels cells is known as NDVIMEAN.
Normalized Difference Water Index (NDWI) is a ratio used to characterize the water and moisture
in the pixel. It is defined by Gao (1996) as “NDWI= (NIR-MIR) / (NIR+MIR)”. The average (mean)
of NDWI computed on 45 pixels x 45 pixels cells is known as NDWIMEAN.
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The Shortwave InfraRed (SWIR) variable corresponds to the reflectance in the middle infrared, i.e.
in our case to the band of VGT or PROBA-V (MIR). The average (mean) of SWIR computed on 45
pixels x 45 pixels cells is known as SWIRMEAN.
Four difference values are calculated per pixel, before classifying the pixel through applying
threshold values, as shown in Table 5:
1. Contrast Local Vegetation (CLV) is the difference between the NDVIMEAN and the NDVI
pixel value.
2. Contrast Local Water (CLW) is the difference between the NDWIMEAN and the NDWI pixel
value
3. Contrast Local Difference Vegetation Water (CLDVW) is the difference between NDVIMEAN
and NDWIMEAN
4. Contrast Local Mid InfraRed (CMIR) is the difference between SWIRMEAN and the SWIR
pixel value.
Table 5: SWB thresholds description
Indices Description Thresholds
VGT
Thresholds
PROBA-V
Classification
CLDVW The difference between the mean of NDVI-
NDWI on the 45x45 pixels window and its
value for each pixel [Gond et al., 2004]
CLDVW >
0.08
CLDVW > 0.09 Water
CLMIR Mean of MIR channel on 45x45 km centred
sliding window minus MIR pixel value [Gond
et al.,2004]
CLMIR > 0.05 CLMIR > 0.06
NDWI (NIR-MIR)/(NIR+MIR) [Gao, 1996] NDWI > - 0.05 NDWI > -0.041
CLV Mean of NDVI on 45x45 km centred sliding
window minus NDVI pixel value [Gond et
al.,2004]
CLV < -0.1 CLV < -0.11 Humid
Vegetation
CLW Mean of NDWI on 45x45 km centred sliding
window minus NDWI pixel value [Gond et al.,
2004].
CLW < -0.1 CLW < -0.11
To avoid commission errors, the algorithm evaluates the consecutive detection result of the current
and previous dekad (see
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Table 6).
Table 6 : Consecutive detection rule
Dekad ‘N-1’ Dekad ‘N’ Output
Water Water Water
Water or humid vegetation Water Water
Water or humid vegetatoin Humid Vegetation Humid Vegetation
Humid Vegetation Humid Vegetation Humid Vegetation
Land Water or Humid Vegetation Land
3.2.3.2 Seasonality detection
The detection of seasonality is organized in three main steps, as depicted on Figure 5,
1. The first step consists in organizing the detections of small water bodies in time series. For
each pixel, a history of 45 dekads (1 Year + 3 months) is available.
2. In the second step, the date detection algorithm searches for the most recent start and end
of season. Depending on the type of season, a flag value is also defined.
3. In a third step, the dates are assigned to each pixel and saved to files. The output of the
seasonality are three dynamic images representing start date, end date and status flag.
The detection of the seasonality (Step 2 in Figure 5) is made by analyzing time series for each
pixel. A season must have at least two detections out of three in a row. The seasonality algorithm
detects time frames during which these conditions are met. The start of season corresponds to the
first date of the most recent identified period of detections. The end of season is not necessarily
visible at the time of the observation.
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Figure 5 : Data flow of the seasonality detection
Across the season period, the flag status is updated whenever applicable as shown in Table 7:
If the end of the current season was detected, flag is set to 1. In this situation the season is
said to be complete.
After a complete season, a positive detection may occur at the date of the observation. In
this case, another positive detection, or a negative immediately followed by a positive
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detection will be need to classify the detection as a start of season (or to discard it). Hence,
the detection receives the flag 2, but the start and end of season maps still store the dates
of the preceding start and end of season.
In the case where a detection, candidate for validation as a start of season, and that no
valid detection occurred before (during the 45 dekads of observations), the detection
receives flag 3 (two examples are given in Table 7). In this situation the season end date is
identical to start season and should be ignored.
If the start of the current season was detected, however the end has not been detected,
flag is set to 4. In this situation the season end date is set to current decade (running
towards end of season) and should be ignored.
If only single date events were seen in the time series, the pixel receives flag 5, and the
date of this single date event is stored in the products.
In the case where the end of season is still visible but the start too ancient (older than 45
dekads), and no new valid season occurred, the season receives flag 6. The start season
date should be ignored.
Flag 0 corresponds to the ocean and flag 255 corresponds to dry land. They are used to
display the images with different colors for these two no-data types.
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0 Ocean
255 Land
1 Season start and end available, season length ≥2dekads
2 New possible start in the most recent dekad, products start and end give date of the former validated season
3 Start of season to be confirmed by next observation, no valid season was observed before
4 Season still going on, ends in future
5 Only single date events were visible
Flag 2
1 2 3 4 5 6 7 8 9 10 11
Dekad
De
tec
tio
n
Flag 3
1 2 3 4 5 6 7 8 9 10 11
Dekad
De
tec
tio
n
Flag 3
1 2 3 4 5 6 7 8 9 10 11
Dekad
De
tec
tio
n
Flag 4
1 2 3 4 5 6 7 8 9 10 11
Dekad
De
tec
tio
n
Flag 5
1 2 3 4 5 6 7 8 9 10 11
Dekad
Det
ectio
n
Flag 1
1 2 3 4 5 6 7 8 9 10 11 Dekad
Detection
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6 Start of season falls out of the time series scope
Table 7 : List of flags for the seasonality detection.
3.2.4 Limitations
The algorithm was validated over a large area in Sahel (Gond et al., 2004). Key conclusions of the
authors are that commission errors are in the order of 10%, whereas omission errors can be
higher, due to the low resolution of the instrument used.
Other limitation of the algorithm is the extent of the zone for which it was designed. To overcome
this limitation, a mask corresponding to the validated zone (named MVM) is available for the user
to mask the extent were the algorithm is not relevant (see Figure 6).
Figure 6: Zone for which the VGT4AFRICA was designed (in black)
The size of the sliding window in comparison with the size of the water body to detect doesn’t allow
the detection of large water bodies. Further, they indicate negative NDWI due to coppery soils.
However, besides the problems mentioneed by the authors, the major issue is that this method
was developed for local application over specific bioclimatic area and is not suited for continental
detection. Nevertheless, this method was taken into account for the development of a more generic
algorithm.
Flag 6
1 2 3 4 5 6 7 8 9 10 11
Dekad
Det
ectio
n
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Another limitation is on the edges of the coast (25km) where the pixels are masked out using a
mask to avoid detection of contrast between sea and land pixels at the coastal zone. Also any
detection on the shore of the big lakes are similarly masked out.
Despite the adjustment of the threshold values, the agreement between SPOT-VGT and PROBA-V
SWB products reaches a probability of only 60%.
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4 PRODUCT DESCRIPTION
The Water Bodies V1 (WB1) product follows the following naming standard:
g2_BIOPAR_WB_<YYYYMMDDHHmm>_<AREA>_<SENSOR>_V<Major.Minor.Run>
where
<YYYYMMDDHHmm> gives the temporal location of the file. YYYY, MM, DD, HH, and mm
denote the year, the month, the day, the hour, and the minutes, respectively.
<AREA> gives the spatial coverage of the file. In our case, <AREA> is HxxVyy, the name of
the 10°x10° tile or the continent short name
<SENSOR> gives the name of the sensor used to retrieve the product, so PROBAV or VGT
<Major.Minor.Run> gives the version number of the product. “Major” increases when the
algorithm is updated. “Minor” increases when bugs are fixed or when processing lines are
updated (metadata, colour quicklook, etc...). “Run” increases each time, for a given
Mayor.Minor version, a new processing run has been performed. This can happen when for
some reason the PROBA-V input data is updated. The current Major version is 1.
4.1 FILE FORMAT
The Water Bodies V1 products are delivered every 10 days as a ZIP archive containing following
files:
Four single band GEOTIFF format containing the following layers:
o SWB: Water Bodies Detection
o WBSTARTDATE: Water Bodies Season Start
o WBENDDATE: Water Bodies Season End
o WBFLAG: Water Bodies Season Flag
o A quicklook image (SWB_QL) in a coloured GEOTIFF format. The quicklook is sub-
sampled to 25% in both X and Y direction and based on the SWB layer.
An xml file containing the metadata conforms to INSPIRE2.1.
An xsl file for displaying a friendly view of the above metadata file.
A text file containing the copyright of the product.
Each ZIP archive is a self-contained package and hence is not dependent on any other files. A
dedicated typology has been chosen to locate easily each tile when reading its name. The globe is
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divided in 36 tiles in longitude and 18 tiles in latitude according to Figure 7. Only the green tiles
over Africa (red rectangle), covering land, are generated and hence available. The products are
also provided by continents (grouping of a set of tiles) as defined in Figure 7 (red rectangle), and
named as in Table 8.
Figure 7: Region of Interest. Blue (inner) rectangle indicates water bodies algorithm boundary. Red
(outer) rectangle indicates product delivery boundary.
Note the actual calculation of water bodies is done according the VGT4Africa region definition,
hence longitude -26° to 60° and latitude 38° to -35°. Pixels falling outside the VGT4Africa region
(longitude -30°E to -26°E, latitude 40°N to 38°N and latitude -35°N to -40°N) are indicated with a
251-value (missing).
Short name Continent
AFRI Africa: 30°W – 60°E, 40°N – 40°S
Table 8: Definition of the continents.
The product is accompanied with two separate ZIPs that are delivered once, containing the following files:
One single band GEOTIFF format containing one of the following layers:
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o MVM: Manual Validation Mask
o PW: Permanent Water mask
An xml file containing the metadata conform to INSPIRE2.1.
An xsl file for displaying a friendly view of the above metadata file.
A quicklook image in a coloured GEOTIFF format. The quicklook is sub-sampled to 25% in
both X and Y direction and based on the SWB layer.
A text file containing the copyright of the product.
4.2 PRODUCT CONTENT
4.2.1 Image Files
4.2.1.1 Water Bodies layer
The values of the digital numbers in the first layer (SWB) are listed in Table 9.
Value Label
0 Sea
70 Free Water
150 Humid vegetation
220 Mixed
251 No data
255 Dry land
Table 9: WB layer legend
4.2.1.2 Season layers
The three season layers are coded as follows:
WBSTARTDATE contains the start date of the season, represented as the number of
dekads since 1st January 1980.
WBENDDATE contains the end date of the season, represented as the number of dekads
since 1st January 1980.
WBFLAG represents a set of values describing the quality of the seasonality detection (
Table 10).
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Table 10: WBFLAG legend
4.2.1.3 MVM layer
The values of the digital numbers in the Manual Validation Mask layer (MVM) are listed in Table
11.
Table 11: MVM legend
Value Label
0 Ocean
64 Pixel within erode zone
128 Pixel within validated zone
255 Dry land
4.2.1.4 PW layer
The values of the digital numbers in the Permanent Water layer (PW) are listed in
Table 12.
Table 12: PW legend
Value Label
0 Ocean
70 Permanent Water
255 Dry land
Value Label
0 Ocean
1 Season start and end dates available
2 New possible start in the most recent dekad
3 Start of season to be confirmed by next observation
4 Season still ongoing, ends in future
5 One single date event was visible
6 Start of season falls out of the time series scope
255 Dry land
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4.2.2 ‘WB’ quicklook image
The quicklook GEOTIFF file is derived from the SWB image. The spatial resolution is sub-sampled,
using nearest neighbour resampling, to 25% in both directions, hence a quicklook is 1/16th of the
size of the data layer.
The quicklook is coded in 1 byte (no scaling or offset used) and provided with an embedded color
table as presented in Table 13.
Value Description Color RGB value
0 ocean 12, 88, 235
70 free water 173, 216, 230
150 humid vegetation 0, 120, 0
220 “free water” and “humid vegetation” 144, 238, 144
251 missing 255,255,255
255 dry land 165, 42, 0
Table 13: Quicklook color coding scheme
4.3 PRODUCT CHARACTERISTICS
4.3.1 Projection and Grid Information
The product is displayed in a regular latitude/longitude grid (plate carrée) with the ellipsoid WGS
1984 (Terrestrial radius=6378km). The resolution of the grid is 1/112° (approx. 1km at the equator).
The reference is the centre of the pixel. It means that the longitude of the upper left corner of the
pixel is (pixel_longitude – angular_resolution/2.)
Each tile covers an area of 10°x10°, while the continental tiles cover a multiple of these 10°x10°
tiles as defined in Figure 7.
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Figure 8: The cut-out of tiles
Starting from the upper left centre pixel and taking 10° or 1120 pixels into account, the final tile is
an array of 1121 lines and 1121 columns taking the bottom/right upper/left half pixel into account
(Figure 8). As such there is an overlap between the tiles. For example, the last column of tile
H18V4 is the first column of the tile H19V4, and the last line of H18V4 is the first line of the tile
H18V5.
4.3.2 Spatial information
As shown in Figure 7, the product is provided from longitude -30°W to +60°E and latitude +40°N to
-40°S.
4.3.3 Temporal Information
The WB V1 demonstration product is a 10 day composite. Each composite starts on day 01, 11 or
21, hence the last composite of each month is variable dependent on the number of days available
in the month.
10° = 1120 pixels
1121 pixels = 10.0089°
10° = 1120 pixels
1121 pixels = 10.0089°
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The products are provided from 1998-04-01 till Near Real Time. However the seasonality
information is only available from 1999-07-01 because it requires 45 months of pre-processed
inputs.
4.3.4 Data Policies
Any use of the Copernicus WB V1 products implies the obligation to include in any publication or
communication using these products the following citation for the SPOT-VGT derived products
"The product was generated by the land service of Copernicus, the Earth Observation programme
of the European Commission. The research leading to the current version of the product has
received funding from various European Commission Research and Technical Development
programmes. The product is based on VEGETATION data ((c) CNES).”
, and for the PROBA-V derived products:
"The product was generated by the land service of Copernicus, the Earth Observation programme
of the European Commission. The research leading to the current version of the product has
received funding from various European Commission Research and Technical Development
programmes. The product is based on PROBA-V 1km data ((c) ESA and distributed by VITO).”
The user accepts to inform the production and distribution centre of their publications through the
following address: [email protected].
4.3.5 Access and Contacts
The product is available through the Copernicus Global Land service website at the address:
http://land.copernicus.eu/global/products/WB
Accountable contact: European Commission Directorate – General Joint Research Centre
Email address: [email protected]
Scientific, Production and Distribution contact:
Email address: [email protected].
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5 VALIDATION
This original (SPOT-VEGETATION) Water Bodies product version 1 has been validated through
mapping the temporary surface water bodies in sub-Saharan western Africa [Haas et al., 2009].
The Quality Assessment of the SPOT/VGT and PROBA-V WB V1 is being performed following the
procedure described in the Service Validation Plan [Erreur ! Source du renvoi introuvable.SVP].
Omission and commission errors are both assessed [GIOGL1_QAR_WBV1].
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6 REFERENCES
Bartholomé, E., & Combal, B. (2006). Small water bodies - VGT4Africa User Manual (first Ed.). VGT4Africa User Manual (first ed.), Office for Official …. Retrieved from http://www.vgt4africa.org/PublicDocuments/VGT4AFRICA_user_manual.pdf
Carroll M.L., J. R. Townshend, C. M. DiMiceli, P. Noojipady, and R. A. Sohlberg, 2009, A new global raster water mask at 250 m resolution, International Journal of Digital Earth, vol. 2, 291-308.
Gao, B. G., 1996, NDWI — a normalized difference water index for remote sensing of vegetation
liquid water from space. Remote Sensing of Environment, 58, 257–266.
Gond, V., Bartholomé, E., Ouattara, F., Nonguierma, A., & Bado, L. (2004). Surveillance et cartographie des plans d’eau et des zones humides et inondables en régions arides avec l'instrument VEGETATION embarqué sur SPOT-4. International Journal of Remote Sensing. doi:10.1080/0143116031000139908
Haas, E., Bartholomé, E., Combal, B. , 2009, Time series analysis of optical remote sensing data
for the mapping of temporary surface water bodies in sub-Saharan western Africa. Journal of
Hydrology, 370, 52-63.
Holben, B.N., 1986. Characteristics of maximum-value composite images from temporal AVHRR
data. Int. J. Remote Sens. 7, 1417–1434.
Rahman, H., Dedieu, G., 1994. SMAC: a simplified method for the atmospheric correction of
satellite measurements in the solar spectrum. International Journal of Remote Sensing 15,
123-143.