Remote sensing monitoring of land restoration interventions in semi-arid environments

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MultiTemp 2017 Remote sensing monitoring of land restoration interventions in semi-arid environments M. Meroni 1, A. Schucknecht 1, D. Fasbender 1, F. Rembold 1, L. di Lucchio 1,5, F. Fava 2, M. Mauclaire 3, D. Goffner 4, U. Leonardi 6 1 European Commission, Joint Research Centre (JRC), Food Security Unit, Ispra (VA), Italy 2 International Livestock Research Institute, Nairobi, Kenya 3 University of Bordeaux 3, Labex DRIIHM and Les Afriques dans le monde (LAM), Bordeaux, France 4 French National Centre for Scientific Research, CNRS/UMI, Marseille, France 5 University of Copenhagen, Geosciences and Natural Resource Management, Frederiksberg, Denmark 6 FAO-SWALIM, Nairobi, Kenya

Background info Restoration interventions > stop desertification/land degradation > improve land productivity > plantations, improved land management, run-off control infrastructures Evaluating the success of an intervention is challenging (lack of standardized and affordable methodologies) > success is rarely checked Objective Provide a first, standardized and objective assessment of the biophysical impact of a intervention, in terms of vegetation cover

Method NDVI as a proxy of vegetation cover (response to restoration) changes in vegetation are natural (seasonal vegetation cycle, the inter-annual climate variability) success cannot be assessed focusing on the intervention only Rely on comparative methods and use a state-of-art statistical design borrowed from the ecology domain: BACI (Before/After-Control/Impact) design

Method BACI (Before/After-Control/Impact) design NDVI Before Time After Control Impact to account for natural changes, the impact site is compared to another site, the control site it is the differential change (after vs. before) with respect to control that matters

Method Multiple controls extends this idea and avoids that the BACI results are due to a poor choice of control sites Similarly, multiple temporal sampling before and after ensures that temporal fluctuations do not confound the detection of the impact t 1 t 2 t 3 t 4 t 5 t 6 Before Time After

Method BACI: Linear mixed-effects model on NDVI site-level averages as in Schwarz, 2015. Fixed effects: period (before/after), class (impact/control), period x class. Random effect: site, sampling time. BACI contrast = (µ CA - µ CB ) (µ IA - µ IB ) Difference (control-impact) of the mean NDVI variation (after-before) NDVI Before Time After Control Impact Contrast= Negative difference = improvement (or reduced degradation) of the impact Significance (P-value) of BACI effect Used in testing the (null) hypothesis of no change (due to intervention)

Automatic selection of control areas Requirements 1) relatively close in space to impact to experience the same weather variability 2) land cover before the intervention similar to impact 3) randomly selected 4) not subjected to anthropogenic changes

Automatic selection of control areas 1) close in space to experience the same weather variability Impact search area/impact area = 600 * Striping due to the use of LS7 data affected by SLC-off

2) similar land cover before the intervention Unsupervised classification on the imagery before the intervention to find out areas similar to impact

2) similar land cover before the intervention Unsupervised classification on the imagery before the intervention to find out areas similar to impact Candidate controls: all possible square windows (area equal to impact) in the search area (other interventions masked out) Each of them characterized by a similarity (s=1-rmse in class composition) to impact area

Controls Impact 3) randomly selected Among those similar (s>0.9), 20 controls are randomly selected using probability proportional to size

Controls Impact 3) randomly selected Among those similar (>0.9), 20 controls are randomly selected using probability proportional to size 4) not subjected to anthropogenic changes Controls are visually checked in the period analyzed Avg NDVI (Impact/Controls Before/After) is used in BACI statistical framework

Test area Matam region, Senegal Great Green Wall for the Sahara and the Sahel Initiative (GGWSSI), a pan-african project to combat desertification creating a green belt south of the Sahara Mainly tree plantations and rangeland restoration (fencing) Cash for work activities

Data Remote sensing Moderate spatial resolution emodis NDVI @ 250 m and 10-day frequency High resolution Landsat 7 and 8 NDVI @ 30 m Maximum NDVI during the growing season Availability of cloud-free imagery VERY limited (exp. with LS7). One per season, not all the year of interest NDVI at time of observation BACI design: MODIS: Multiple controls and multiple time sampling (5 yrs B/A) Landsat: Multiple controls, single time

Data Delineation of intervention areas Field missions Consistency check of BACI results Qualitative evaluation of intervention success during field missions Very High Resolution imagery from Google Earth

Results, examples Project 9, BACI significant, improvement Landsat P=0.007 RC= -18% MODIS P=0.048 RC=-32% Project 4, BACI non significant, degradation Landsat P=0.07 RC=18% MODIS P=0.17 RC=6%

Results, overview Intervention Id Qualitative information Field mission Google Earth VHR 4 5 9 14 15 16 17 18 43 44 48 57 58 59 81 n.a. n.a. n.a. n.a. n.a. n.a. n.a. n.a. n.a. Failure Partial success Success BACI results MODIS 5 years before/after P -value 0.17 0.80 0.01 0.00 0.01 0.06 0.64 0.63 0.02 0.08 0.92 0.09 0.53 0.67 0.00 Contrast 0.03 0.01-0.08-0.12-0.07-0.06 0.01-0.01-0.08-0.04 0.00-0.04-0.01-0.01-0.12 n.s. P < 0.05 Relative contrast (%) 6.3 1.6-17.3-27.7-17.6-12.7 2.4-3.1-16.3-8.3-0.5-8.2-3.0-1.8-20.9 Landsat 1 year before/after P -value 0.07 0.79 0.05 0.01 0.04 0.42 0.41 0.70 0.04 0.26 0.59 0.38 0.46 0.33 0.06 Contrast 0.08 0.01-0.11-0.15-0.10-0.06 0.06-0.02-0.05-0.07-0.03-0.04-0.02-0.04-0.12 Relative contrast (%) 18.2 3.1-32.4-36.4-25.1-13.8 16.2-5.9-12.3-17.4-6.6-8.5-5.0-7.0-27.9 Good agreement with qualitative information Large agreement between MODIS and Landsat No biophysical impact detected for 10 out of 15 projects!

Conclusions BACI applied to RS data cost-effective method to provide a first screening of restoration interventions agreement with VHR photointerpretation and field information with other RS-derived variables (e.g. soil moisture, surface roughness, fragmentation, VHR plant species mapping) may be applied to other impacts (soil conservation, habitat fragmentation, biodiversity) requires multiple undisturbed controls (no major and widespread changes) Landsat vs. MODIS MODIS: high temporal frequency makes - > BACI multi -site -year, spatial resolutions may not be sufficient for small interventions LS: poor cloud-free availability (LS7). Positive prospects for more recent interventions using LS8 and Sentinel2