احمد سعيد فتحي يوسف أبو زيد
أستاذ
Abuzaid, A. S., El-Komy, M. S. Shokr, M. S., El Baroudy, A. A. Mohamed, E. S. Rebouh, N. Y., Abdel-Hai, M. S. 2023. Predicting dynamics of soil salinity and sodicity using remote sensing techniques: A landscape-scale assessment in the northeastern Egypt. Sustainability, 15: 9440, DOI: https://doi.org/10.3390/su15129440
Sustainability • 2023
معلومات البحث
المؤلفون
Abuzaid, A. S.; El-Komy, M. S.; Shokr, M. S.; El Baroudy, A. A.; Mohamed, E. S.; Rebouh, N. Y.; Abdel-Hai, M. S.
الكلمات المفتاحية
salt-affected soils; Seasonal variations; Drylands; Landsat 8 OLI; Soil sodicity; near-infrared (NIR); Stepwise regression models
المجلة العلمية
Sustainability
الناشر
Multidisciplinary Digital Publishing Institute (MDPI)
المجلد
15
العدد
Not Available
الصفحات
9440
publication.type
International
رابط البحث
Open Link
المواد المرفقة
Not Available
الملخص
Traditional mapping of salt affected soils (SAS) is very costly and cannot precisely depict
the space–time dynamics of soil salts over landscapes. Therefore, we tested the capacity of Landsat
8 Operational Land Imager (OLI) data to retrieve soil salinity and sodicity during the wet and
dry seasons in an arid landscape. Seventy geo-referenced soil samples (0–30 cm) were collected
during March (wet period) and September to be analyzed for pH, electrical conductivity (EC), and
exchangeable sodium percentage (ESP). Using 70% of soil and band reflectance data, stepwise linear
regression models were constructed to estimate soil pH, EC, and ESP. The models were validated
using the remaining 30% in terms of the determination coefficient (R2) and residual prediction
deviation (RPD). Results revealed the weak variability of soil pH, while EC and ESP had large
variabilities. The three indicators (pH, EC, and ESP) increased from the wet to dry period. During the
two seasons, the OLI bands had weak associations with soil pH, while the near-infrared (NIR) band
could effectively discriminate soil salinity and sodicity levels. The EC and ESP predictive models
in the wet period were developed with the NIR band, achieving adequate outcomes (an R2 of 0.65
and 0.61 and an RPD of 1.44 and 1.43, respectively). In the dry period, the best-fitted models were
constructed with deep blue and NIR bands, yielding an R2 of 0.59 and 0.60 and an RPD of 1.49 and
1.50, respectively. The SAS covered 50% of the study area during the wet period, of which 14 and 36%
were saline and saline-sodic soils, respectively. The extent increased up to 59% during the dry period,
including saline soils (12%) and saline-sodic soils (47%). Our findings would facilitate precise, rapid,
and cost-effective monitoring of soil salinity and sodicity over large areas.
the space–time dynamics of soil salts over landscapes. Therefore, we tested the capacity of Landsat
8 Operational Land Imager (OLI) data to retrieve soil salinity and sodicity during the wet and
dry seasons in an arid landscape. Seventy geo-referenced soil samples (0–30 cm) were collected
during March (wet period) and September to be analyzed for pH, electrical conductivity (EC), and
exchangeable sodium percentage (ESP). Using 70% of soil and band reflectance data, stepwise linear
regression models were constructed to estimate soil pH, EC, and ESP. The models were validated
using the remaining 30% in terms of the determination coefficient (R2) and residual prediction
deviation (RPD). Results revealed the weak variability of soil pH, while EC and ESP had large
variabilities. The three indicators (pH, EC, and ESP) increased from the wet to dry period. During the
two seasons, the OLI bands had weak associations with soil pH, while the near-infrared (NIR) band
could effectively discriminate soil salinity and sodicity levels. The EC and ESP predictive models
in the wet period were developed with the NIR band, achieving adequate outcomes (an R2 of 0.65
and 0.61 and an RPD of 1.44 and 1.43, respectively). In the dry period, the best-fitted models were
constructed with deep blue and NIR bands, yielding an R2 of 0.59 and 0.60 and an RPD of 1.49 and
1.50, respectively. The SAS covered 50% of the study area during the wet period, of which 14 and 36%
were saline and saline-sodic soils, respectively. The extent increased up to 59% during the dry period,
including saline soils (12%) and saline-sodic soils (47%). Our findings would facilitate precise, rapid,
and cost-effective monitoring of soil salinity and sodicity over large areas.
