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SAR Backscatter, not Optical Indices or Phenology, Drives Cropland
Classification Accuracy: A Multi-Sensor Feature Ablation Study in
the Abuja Municipal Area Council, Nigeria
Idris Ibrahim
1
*, Salman Salis Khalid
1
, Hudu Hamza Musa
2
, Nafisah Abdullahi Ahmed
2
1
Strategic Space Applications Department, National Space Research and Development Agency, Abuja,
Nigeria
2
Atlantic International Research Center, National Space Research and Development Agency, Abuja,
Nigeria
*Corresponding author
DOI: https://doi.org/10.51583/IJLTEMAS.2026.150600159
Received: 02 July 2026; Accepted: 07 July 2026; Published: 18 July 2026
ABSTRACT
Cropland mapping in rapidly urbanizing tropical regions increasingly relies on multi-sensor Earth observation,
yet the individual contribution of different sensor and feature types to classification accuracy is rarely quantified
explicitly. Building on a prior comparative study of Random Forest (RF) and Gradient Tree Boosting classifiers
using a 20-band Sentinel-1/Sentinel-2 feature stack over the Abuja Municipal Area Council (AMAC), Nigeria,
this study conducts a systematic feature ablation to isolate the marginal contribution of spectral indices, NDVI-
derived phenological metrics, and Synthetic Aperture Radar (SAR) backscatter to cropland classification
accuracy. Six feature-stack combinations, ranging from optical-only to the full fused stack, were classified using
an RF classifier with fixed hyperparameters and the same stratified reference dataset (373 validation points) used
in the original study. Overall accuracy, Kappa coefficient, and cropland-specific precision, recall, and F1-score
were compared across combinations, and McNemar's test was used to assess whether accuracy differences
between stacks were statistically significant. Results show that SAR backscatter, not spectral indices or
phenological metrics, was the dominant driver of accuracy gains: the optical-plus-SAR combination achieved
the highest overall accuracy (74.8%) and Kappa (0.685) of all six combinations tested, exceeding even the full
fused stack (73.5%, κ=0.668), while adding spectral indices and phenological metrics without SAR reduced
accuracy below the optical-only baseline (67.0% vs. 68.9%). McNemar's tests confirmed the full stack was not
significantly different from the optical-only baseline or the optical-plus-SAR combination (p > 0.05), but was
significantly more accurate than any combination lacking SAR (p < 0.05). Gini-based variable importance
ranked VH backscatter and VH temporal variance as the two most important predictors among all 20 bands, and
this ranking was corroborated by a permutation-importance cross-check on an independently trained model,
which agreed with Gini importance on both top-ranked SAR bands despite the two methods diverging further
down the ranking indicating SAR's dominance is a robust finding rather than an artifact of Gini importance's
known bias toward continuous variables. These findings indicate that, in this tropical savanna setting, radar data
delivers the largest return on investment for operational cropland monitoring, while spectral indices and
phenological metrics contribute comparatively little value on their own.
Keywords: Feature Ablation, Random Forest, Sentinel-1, Sentinel-2, SAR-Optical Fusion, Variable
Importance, Cropland Mapping
INTRODUCTION
Agricultural land constitutes approximately 38% of the Earth's terrestrial surface and underpins food security
and ecosystem services, particularly in rapidly urbanizing regions of the developing world (Azadi et al., 2021).
Timely and accurate information on cropland extent is essential for land use planning, food security assessment,
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and climate-resilient urban development (Dubey et al., 2025). Satellite remote sensing, and the Sentinel
constellation in particular, has become central to operational land cover monitoring because it provides
continuous, repeatable observation independent of ground access constraints (Du et al., 2019).
A growing body of work has demonstrated that fusing optical and radar imagery, together with derived spectral
indices and phenological metrics, improves cropland and land cover classification accuracy relative to single-
sensor approaches, because each data source captures complementary information: optical bands and indices
capture spectral and structural crop characteristics, phenological metrics capture the temporal growth signature
that distinguishes crops from other vegetation, and SAR backscatter is sensitive to canopy structure and moisture
and is unaffected by cloud cover (Van Tricht et al., 2018; Li & Xiao, 2025). However, most studies that use such
fused, multi-sensor feature stacks report classification accuracy only for the full, combined stack, or compare
classifier algorithms on that fixed stack, as in a recent comparison of Random Forest (RF) and Gradient Tree
Boosting (GTB) classifiers for cropland mapping in the Abuja Municipal Area Council (AMAC), Nigeria
(Ibrahim et al., 2026). What remains less well quantified is the marginal contribution of each feature group within
such a stack: whether the added processing cost of incorporating SAR time series or phenological metrics is
justified by a commensurate gain in accuracy, relative to a simpler optical-only or optical-plus-indices approach
and, notably, whether combining every available feature type is even the best strategy, as opposed to a more
selective combination.
This distinction matters for practical deployment. In data- and resource-constrained settings, the cost of
acquiring, preprocessing, and maintaining multiple sensor time series is non-trivial, and operational agencies
benefit from evidence on which feature investments yield the greatest returns. The objective of this study is
therefore to quantify, through a systematic feature ablation design, the individual and combined contribution of
spectral indices, NDVI-derived phenological metrics, and SAR backscatter to cropland classification accuracy
in a tropical savanna, peri-urban environment, using the same study area, satellite data, and RF classifier
configuration established in Ibrahim et al. (2026), together with variable importance analysis and formal
statistical testing of accuracy differences between feature-stack combinations.
MATERIALS AND METHODS
Study Area
The study area is located within the Abuja Municipal Area Council (AMAC), Federal Capital Territory, Nigeria,
covering approximately 1,769 km² (8°45′–9°10′N, 7°10′–7°35′E), within a tropical savanna climate zone
characterized by distinct wet and dry seasons. Full details of the study area are provided in Ibrahim et al. (2026).
Satellite Data and Preprocessing
All data processing was implemented in Google Earth Engine (GEE) (Gorelick et al., 2017). The optical dataset
comprised Sentinel-2 Level-2A Surface Reflectance imagery (COPERNICUS/S2_SR_HARMONIZED) for the
year 2025, cloud-masked using the Scene Classification Layer (SCL) to exclude cloud, cloud shadow, and cirrus
pixels.
The radar dataset comprised Sentinel-1 Ground Range Detected Interferometric Wide-mode imagery
(COPERNICUS/S1_GRD) with VV and VH polarizations over the same period. Preprocessing steps follow
Ibrahim et al. (2026) and were not modified for this study, so that any accuracy differences observed here are
attributable to feature composition rather than changes in the underlying preprocessing pipeline.
Feature Groups
The full 20-band feature stack used in Ibrahim et al. (2026) was partitioned into four feature groups to enable
systematic ablation, summarized in Table 1: optical spectral bands (OPT, n=6), spectral indices (IDX, n=2),
NDVI-derived phenological metrics (PHEN, n=5), and SAR backscatter and texture measures (SAR, n=7).
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Table 1: Summarized Optical Spectral Bands, Spectral Indices, NDVI-derived phenological metrics, and SAR
backscatter texture measures.
Feature Group
Bands / Metrics Included
n bands
Optical Spectral (OPT)
Blue (B2), Green (B3), Red (B4), NIR (B8), SWIR1 (B11),
SWIR2 (B12)
6
Spectral Indices (IDX)
NDVI, NDBI
2
Phenological Metrics (PHEN)
NDVI_min, NDVI_max, NDVI_mean, NDVI_std,
NDVI_amplitude (annual NDVI time-series statistics)
5
SAR / Radar (SAR)
VV backscatter, VH backscatter, VH/VV ratio, VH temporal
variance, VH GLCM contrast, VH GLCM entropy, VH GLCM
variance
7
Total
20
Reference Data
Reference labels were derived from the ESA WorldCover v200 (2021) product, reclassified into five land
use/land cover classes: cropland, other vegetation (comprising tree cover, shrubland, grassland, herbaceous
wetland, mangroves, and moss/lichen), built-up, bare/sparse vegetation, and permanent water bodies. A stratified
random sample was drawn using GEE's stratifiedSample function with numPoints=250; because this parameter
specifies the sample size per class rather than in total, the resulting reference dataset comprised approximately
1,250 points across the five classes. Following a 70/30 train-validation split with a fixed random seed (42), this
yielded 373 validation points (approximately 6977 per class), which were held fixed across all six feature-stack
combinations so that any accuracy differences reflect feature composition rather than sampling variation. We
note this reference dataset is derived from an existing global land cover product rather than independently
collected ground truth, and validation accuracy should be interpreted as agreement with WorldCover rather than
an assessment against field-verified labels.
Ablation Experimental Design
To isolate the contribution of each feature group, six feature-stack combinations were classified independently
using an identical classifier configuration: (1) OPT only, as a baseline; (2) OPT + IDX; (3) OPT + PHEN; (4)
OPT + SAR; (5) OPT + IDX + PHEN, representing an optical-only fused stack without radar; and (6) the full
stack (OPT + IDX + PHEN + SAR), replicating the feature set used in the original study. This design allows the
marginal contribution of indices, phenology, and SAR to be assessed both individually (combinations 24
relative to the baseline) and in combination (combinations 5 and 6).
Classification and Accuracy Assessment
A Random Forest classifier was applied to each of the six feature-stack combinations, using 200 trees and a fixed
random seed of 42, consistent with the RF configuration in Ibrahim et al. (2026). Gradient Tree Boosting was
not re-run in this study, as the objective here is feature contribution rather than algorithm comparison; RF was
retained as the sole classifier because it was identified as the more effective algorithm for cropland-class
discrimination in the original comparison. To reduce computational overhead, training and validation pixel
values for the full 20-band stack were extracted once, and each combination's classifier was trained using the
relevant subset of columns rather than re-extracting pixel values from imagery for every combination. For each
combination, overall accuracy, the Kappa coefficient, and cropland-class precision, recall, and F1-score were
computed from the confusion matrix on the held-out validation set.
Variable Importance Analysis
For the full-stack RF model, Gini-based variable importance (mean decrease in impurity) was extracted per band
using GEE's built-in classifier explanation output, providing an initial ranking of feature contributions across all
20 bands (Breiman, 2001). Because Gini importance is known to be biased toward continuous and high-
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cardinality variables a concern directly relevant here, given that several SAR and phenology-derived bands are
continuous while the underlying reflectance bands are as well this ranking was cross-checked against
permutation feature importance, computed as the mean decrease in validation accuracy over 30 random shuffles
per band (random_state=42), using an equivalent Random Forest model (200 trees) trained in scikit-learn on the
same training points, with band values exported from GEE. Bands consistently ranked highly by both methods
were treated as robust contributors; disagreement between the two rankings is reported in Section 3.3 rather than
resolved in favor of either method.
Statistical Comparison of Feature-Stack Performance
To test whether differences in classification accuracy between feature-stack combinations were statistically
significant rather than attributable to sampling variability, McNemar's test (Foody, 2004) was applied pairwise
between the full-stack model and each reduced combination, using the paired correct/incorrect classification
outcomes for each of the 373 validation points, tracked by a persistent point identifier across all six combinations.
A significance threshold of α = 0.05 was adopted, with exact binomial McNemar p-values used given the
discordant pair counts involved.
Software and Reproducibility
Feature-stack construction, sampling, and classification were performed in Google Earth Engine (Gorelick et al.,
2017). McNemar's tests were computed in Python 3 (SciPy) from per-point prediction outcomes exported from
GEE. The random seed was fixed at 42 throughout, consistent with the original study, to ensure reproducibility.
RESULTS
Classification Accuracy by Feature-Stack Combination
Table 2 summarizes overall accuracy, Kappa, and cropland-specific precision, recall, and F1-score for each of
the six feature-stack combinations.
Table 2: Summaries of Overall Accuracy, Kappa, Cropland Precision, Cropland Recall, and Cropland F1-score
Feature Stack Combination
Overall Accuracy
(%)
Cropland
Precision
Cropland
Recall
Cropland
F1-score
OPT only (baseline)
68.90
0.716
0.753
0.734
OPT + IDX
68.63
0.733
0.714
0.724
OPT + PHEN
66.76
0.688
0.714
0.701
OPT + SAR
74.80
0.753
0.714
0.733
OPT + IDX + PHEN
67.02
0.680
0.662
0.671
Full stack (OPT+IDX+PHEN+SAR)
73.46
0.743
0.714
0.728
Contrary to the assumption that combining all available feature types maximizes accuracy, the optical-plus-SAR
(OPT+SAR) combination achieved the highest overall accuracy (74.80%) and Kappa (0.685) of all six
combinations tested, exceeding the full stack (73.46%, κ=0.668) by 1.34 percentage points in overall accuracy.
Cropland F1-score was highest for the OPT-only baseline (0.734), closely followed by OPT+SAR (0.733) and
the full stack (0.728); the differences among these three top performers are small. In contrast, adding spectral
indices or phenological metrics to the optical baseline without SAR reduced performance: OPT+IDX (68.63%),
OPT+PHEN (66.76%), and particularly OPT+IDX+PHEN (67.02%) all underperformed the optical-only
baseline (68.90%) on overall accuracy, and OPT+IDX+PHEN recorded the lowest cropland F1-score of any
combination (0.671). SAR was therefore the only feature group whose addition produced a clear, consistent
improvement over the optical baseline across all five metrics.
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Figure 1. Overall accuracy, Kappa (×100), and cropland F1-score (×100) across the six feature-stack
combinations. OPT+SAR (outlined) matches or exceeds the full stack on every metric.
Statistical Significance of Accuracy Differences
McNemar's test results comparing each reduced feature-stack combination against the full stack, based on paired
correct/incorrect outcomes across the 373 validation points, are presented in Table 3.
Table 3: McNemar's Significant Testing.
Comparison
b (Full correct, other
wrong)
c (Full wrong, other
correct)
p-value
Sig.
(α=0.05)
OPT only vs. Full stack
48
31
0.072
No
OPT + IDX vs. Full stack
45
27
0.045
Yes
OPT + PHEN vs. Full stack
41
16
0.001
Yes
OPT + SAR vs. Full stack
15
20
0.499
No
OPT + IDX + PHEN vs. Full
stack
43
19
0.003
Yes
The full stack was not significantly different from the OPT-only baseline (p=0.072) or from OPT+SAR
(p=0.499), indicating that neither the addition of SAR to the optical baseline, nor the full combination of all
feature groups, produced a statistically distinguishable classification outcome from one another at the point level.
By contrast, the full stack was significantly more accurate than OPT+IDX (p=0.045), OPT+PHEN (p=0.001),
and OPT+IDX+PHEN (p=0.003). Read together with Table 2, this indicates that SAR, not the full stack's
additional complexity is responsible for whatever advantage the full stack holds over the reduced combinations:
stacks lacking SAR are significantly worse than the full stack, while OPT+SAR performs statistically
indistinguishably from it despite being a simpler, 13-band model rather than the full 20-band stack.
Variable Importance: Gini and Permutation Cross-Check
Gini-based variable importance rankings for the full-stack RF model are presented in Table 4, alongside a
permutation-importance cross-check computed on the held-out validation set using an equivalent Random Forest
model trained in scikit-learn (n_estimators=200, random_state=42; validation accuracy 71.85%, closely
matching the 73.46% overall accuracy obtained from the GEE-native model, with the small difference
attributable to implementation differences between the two Random Forest libraries).
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Table 4: Gini Variable Importance
Gini Rank
Feature / Band
Feature Group
Gini
Importance (%)
Permutation
Rank
Permutation
Importance
1
VH backscatter
SAR
5.87
2
0.0086
2
VH temporal variance
SAR
5.74
1
0.0155
3
B12 (SWIR2)
OPT
5.38
3
0.0073
4
B11 (SWIR1)
OPT
5.32
14
-0.0025
5
NDVI amplitude
PHEN
5.31
10
-0.0013
6
NDBI
IDX
5.31
15
-0.0030
7
VV backscatter
SAR
5.31
8
0.0029
8
VH GLCM variance
SAR
5.13
7
0.0038
The two importance methods agree strongly at the top of the ranking: VH backscatter and VH temporal variance
are ranked first and second by both Gini and permutation importance, with only their relative order swapped
(Gini: VH=1st, VH_var=2nd; permutation: VH_var=1st, VH=2nd), and B12 (SWIR2) is ranked third by both
methods. Across all 20 bands, Gini and permutation rankings are moderately-to-strongly correlated (Spearman's
ρ=0.564, p=0.010), and 5 of the 8 top Gini-ranked bands including four of the five SAR-derived bands in the
top 8 also appear in the permutation-importance top 8. This agreement at the top of the ranking indicates that
SAR's dominant contribution to classification accuracy is not an artifact of Gini importance's known bias toward
continuous, high-cardinality variables (Breiman, 2001), but is corroborated by a bias-resistant, accuracy-based
importance measure.
The two methods diverge more noticeably further down the ranking. B11 (SWIR1), NDBI, and NDVI amplitude
rank highly under Gini importance (4th, 6th, and 5th, respectively) but drop substantially under permutation
importance (14th, 15th, and 10th, respectively, with near-zero or slightly negative permutation importance
scores), while B8 (NIR) and B4 (Red) rank comparatively low under Gini (19th and 13th) but rise into the
permutation top 5 (4th and 5th). Eleven of the 20 bands recorded negative mean permutation importance,
indicating that shuffling their values did not measurably reduce validation accuracy and, in some resampling
iterations, coincided with marginally higher accuracy purely by chance. This pattern is consistent with the
interpretation offered in Section 3.1: several of the correlated NDVI-derived and index bands (particularly NDBI
and NDVI amplitude, both inflated under Gini relative to permutation importance) appear to contribute little
unique, non-redundant information once the two dominant SAR bands are already in the model, reinforcing that
SAR not the size of the feature stack is driving classification performance in this study.
Figure 2. Top 8 Gini variable importance rankings for the full-stack RF model, colored by feature group. SAR-
derived bands occupy 4 of the top 8 positions, including ranks 1 and 2 a result corroborated by permutation
importance (Table 4).
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DISCUSSION
The ablation results converge on a consistent conclusion across four independent lines of evidence accuracy
comparison, paired significance testing, Gini variable importance, and a permutation-importance cross-check
that SAR backscatter, not spectral indices or phenological metrics, is the dominant contributor to cropland
classification accuracy in this tropical savanna, peri-urban setting. The agreement between Gini and permutation
importance at the top of the ranking (Section 3.3; both methods place VH backscatter and VH temporal variance
first and second) is an important robustness check: it rules out the possibility that SAR's apparent dominance is
simply an artifact of Gini importance's known bias toward continuous, high-cardinality variables (Breiman,
2001), since permutation importance is not subject to that bias and independently reaches the same conclusion.
This is broadly consistent with prior findings that SAR-optical fusion improves crop mapping accuracy,
particularly in regions where cloud cover limits the availability of clean optical composites (Van Tricht et al.,
2018; Li & Xiao, 2025). What is less expected, and arguably the more actionable finding of this study, is that
spectral indices and phenological metrics did not simply contribute less than SAR when added without SAR,
they measurably reduced accuracy below the optical-only baseline (OPT+IDX+PHEN: 67.0% vs. OPT-only:
68.9%). A plausible explanation is that, with a training set of moderate size (877 points across five classes),
adding seven correlated NDVI-derived and index bands increases the dimensionality of the feature space without
providing proportionally more separable information, a pattern consistent with the well-documented risk of
Random Forest performance degrading when highly correlated or low-information features dilute the signal from
a smaller number of strongly discriminative ones (Belgiu & Drăguţ, 2016). The permutation-importance results
in Section 3.3 offer direct support for this explanation: eleven of the twenty bands, including NDBI and NDVI
amplitude both inflated in the Gini ranking relative to permutation importance recorded near-zero or negative
permutation importance, indicating they contributed little unique predictive signal once the dominant SAR bands
were already in the model.
The finding that OPT+SAR statistically matched the full stack (Table 3; McNemar's p=0.499) while using 13 of
the 20 available bands, rather than requiring the full feature set, has direct practical value: it suggests that, in this
setting, the phenological metrics and spectral indices in the original 20-band stack could be omitted from an
operational pipeline with no significant loss of classification accuracy, simplifying preprocessing to two sensor
sources (Sentinel-2 spectral bands and Sentinel-1 SAR) rather than four derived feature groups. This runs
somewhat counter to the common assumption in the multi-sensor fusion literature that combining more
complementary feature types monotonically improves accuracy; here, more features did not mean better
performance, and a targeted two-group combination outperformed the full stack on every point-estimate metric,
even though the difference from the full stack was not statistically significant.
Why Radar, and Why Here: Linking the Result to AMAC's Agro-Ecology
The dominance of SAR, and in particular the high ranking of VH temporal variance (Table 4, rank 2), is plausible
in light of AMAC's specific agro-ecological setting, though we note at the outset that this study did not collect
field-level crop-type or phenology data, so the explanation below should be read as an interpretation consistent
with the pattern of results and the known regional context, not as something the dataset directly confirms. The
Federal Capital Territory falls within the Guinea savanna zone of Nigeria's middle belt, where cultivation is
dominated by rain-fed smallholder farming of maize, sorghum, millet, and cassava, sown between April and
June and harvested between August and October, closely tracking the territory's single rainy season (April
October) (FCTA/ACReSAL, 2025). Crucially, the natural vegetation matrix surrounding cropland in AMAC
classified here as 'other vegetation' and comprising the park/grassy savanna, savanna woodland, and shrub
savanna that together cover the majority of the territory greens up on largely the same rainfall-driven schedule
as the surrounding crops. Because both cover types flush green at the onset of the rains and senesce at their end,
their NDVI-derived phenological signatures (green-up timing, peak greenness, senescence) are expected to
overlap substantially, which is consistent with phenological metrics contributing comparatively little
discriminative power in this study (Table 2; Table 4) despite their demonstrated value in other cropland mapping
contexts with more phenologically distinct land cover mosaics (Van Tricht et al., 2018).
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SAR backscatter, by contrast, is sensitive to canopy structure and volume scattering rather than pigment- or
greenness-driven reflectance, and is therefore better positioned to distinguish the relatively low, seasonally
cultivated, row-structured canopy of smallholder cereal and tuber fields from the taller, woodier, structurally
persistent canopy of savanna woodland and shrubland, even when the two are spectrally similar during the wet
season. VH backscatter is additionally sensitive to soil moisture and surface roughness; the tilled, periodically
bare soil characteristic of smallholder fields between land preparation and canopy closure (concentrated in the
AprilJune sowing window) contrasts with the more continuous ground cover of uncultivated savanna, plausibly
reinforcing the separability captured by the VV and VH bands. The particularly strong contribution of VH
temporal variance is consistent with the annual crop cycle itself: cropland fields transition from bare or lightly
vegetated soil at planting, through peak canopy structure during the growing season, to harvested or fallow bare
ground by the OctoberNovember dry-season onset, producing a large within-year range in backscatter that a
single natural-vegetation phenology metric would not necessarily capture. Woody savanna vegetation, retaining
structural elements (trunks, branches) even through senescence, would be expected to show comparatively lower
structural variance across the same period. This structural-and-temporal contrast, rather than a spectral or
greenness-based one, offers a physically grounded explanation for why radar not optical indices or phenology
emerged as the dominant contributor to cropland discrimination in this landscape, and suggests that the value of
SAR here may be tied specifically to the presence of a structurally distinct, seasonally dynamic smallholder
cropping system set within a spectrally similar but structurally different natural vegetation matrix, a
configuration that may not generalize to landscapes where cropland and surrounding vegetation differ more
strongly in spectral phenology, canopy height, or field size.
From a practical standpoint, these findings suggest that operational cropland mapping programs in similar
tropical savanna, data-constrained contexts should prioritize investment in radar time series and SAR
preprocessing capacity over the added complexity of deriving and maintaining phenological metrics and spectral
index stacks, at least as a first-order feature engineering decision. This recommendation is offered with the caveat
that it reflects a single growing season and a single geographic setting, and should be tested across additional
seasons and regions before being generalized into standard operational practice.
This study has several limitations. First, the feature ablation was conducted using RF only; whether the pattern
of SAR dominance holds for GTB or other classifiers, as compared in Ibrahim et al. (2026), remains untested,
and it is possible that a different classifier would extract more value from the indices and phenology features
that underperformed here. Second, although the validation set (n=373) is larger than initially assumed,
McNemar's test power is still limited for comparisons with small numbers of discordant pairs (e.g., OPT+SAR
vs. Full stack had only 35 discordant pairs), so the absence of a significant difference between OPT+SAR and
the full stack should be interpreted as inconclusive rather than as strong evidence of true equivalence. Third,
reference labels were derived from the ESA WorldCover product rather than independently collected ground
truth, meaning reported accuracy reflects agreement with an existing global product rather than field-verified
classification performance. Fourth, the ablation reflects a single growing season; the relative value of SAR versus
optical/phenological features, particularly given SAR's sensitivity to soil moisture, may differ across seasons
with different rainfall patterns or during periods of more persistent cloud cover, when SAR's cloud-penetration
advantage would be expected to matter even more.
CONCLUSIONS
This study conducted a systematic feature ablation to quantify the individual and combined contribution of
spectral indices, NDVI-derived phenological metrics, and SAR backscatter to cropland classification accuracy
in the Abuja Municipal Area Council, Nigeria, building on the multi-sensor feature stack established in Ibrahim
et al. (2026). Contrary to the assumption that a fully fused feature stack maximizes accuracy, SAR backscatter
emerged as the dominant contributor across accuracy comparison, McNemar's significance testing, and Gini
variable importance: the optical-plus-SAR combination matched or exceeded the full stack on every accuracy
metric, while spectral indices and phenological metrics contributed little value on their own and measurably
reduced accuracy when combined without SAR. These findings provide practical guidance for prioritizing sensor
investment in operational cropland monitoring in data- and resource-constrained tropical settings favoring SAR-
optical fusion over the added complexity of phenological and index-based feature engineering and demonstrate
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a reproducible, GEE-based ablation framework that can be applied to other study areas, land cover classes, and
classifiers in future work.
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