| Research article |
|
|
|
|
| Assessment of organic carbon stock and labile carbon in soils of the Gataaya Oasis, Tunisia |
Noura BCHATNIA1, Manel ALLANI1,*( ), Hatem IBRAHIM2, Ines BOUZRIBA1, Mohamed Amine MAAOUI1, Nadhem BRAHIM1 |
1University of Tunis El Manar, Faculty of Sciences of Tunis, Department of Geology, Plants Soils and Environment Laboratory, El Manar II 2092, Tunisia 2Faculty of Sciences of Bizerte, University of Carthage, Department of Earth Sciences, Plants Soils and Environment Laboratory, Jarzouna 7021, Tunisia |
|
|
|
Abstract Oasis soils in Tunisia are characterized by low soil organic carbon (SOC) stocks, primarily due to their coarse texture and intensive irrigation practices. In the Gataaya Oasis, soils receive 3.000 to 4.000 L/m2 annually through submersion irrigation, leading to a rapid decline in SOC stocks. Despite their sandy texture, which promotes good water infiltration, these soils are enriched with clay, dissolved materials, and fertilizers in deeper horizons. This study aimed to assess SOC content in the Gataaya Oasis soils, investigate the transport of labile carbon in drainage water, and clarify the destiny of this transported carbon. Soil samples were collected systematically at three depths (0-10, 10-20, and 20-30 cm), focusing on the top 30 cm depth, which is most affected by amendments. Two sampling points (P1 and P2) were selected, i.e., P1 profile near the trunk of date palms (with manure input) and P2 profile between two adjacent date palms (without manure input). Water samples were collected from drainage systems within the oasis (W1, W2, and W3) and outside the oasis (W4). A laboratory experiment simulating manure application and irrigation was conducted to complement field observations. Physical-chemical analyses revealed a significant decrease in SOC stocks with soil depths. In P1 profile, SOC stocks declined from 17.71 t/hm2 at the 0-10 cm depth to 7.80 t/hm2 at the 20-30 cm depth. In P2 profile, SOC stocks were lower, decreasing from 6.73 t/hm2 at the 0-10 cm depth to 3.57 t/hm2 at the 20-30 cm depth. Labile carbon content in drainage water increased outside the oasis, with chemical oxygen demand (COD) values rising from 73 mg/L in W1 water sample to 290 mg/L in W4 water sample, indicating cumulative leaching effects from surrounding oases. The laboratory experiment confirmed field observations, showing a decline in soil organic matter (SOM) content from 3.27% to 2.62% after 12 irrigations, highlighting the vulnerability of SOC stocks to intensive irrigation. This study underscores the low SOC stocks in the Gataaya Oasis soils and their rapid depletion under successive irrigations. The findings provide insights into the dynamics of labile carbon transport and its contribution to regional carbon cycling, offering valuable information for sustainable soil management and ecological protection in arid ecosystems.
|
|
Received: 24 March 2025
Published: 30 November 2025
|
|
Corresponding Authors:
*Manel ALLANI (E-mail: manel.allani@fst.utm.tn)
|
|
|
| [1] |
Abbas K, Deroin J P, Bouaziz S. 2018. Monitoring of playa evaporates as seen with optical remote sensing sensors: Case of Chott El Jerid, Tunisia, from 2003 to present. Arabian Journal of Geosciences, 11(5): 92, doi: 10.1007/s12517-018-3410-0.
|
|
|
| [2] |
AFNOR (Association Française de Normalisation). 1994. Soil Quality: Determination of Specific Electrical Conductivity. Paris: French Standards Association. (in French)
|
|
|
| [3] |
AFNOR (Association Française de Normalisation). 1995. Soil Quality: Determination of Carbonate Content, Volumetric Method. Paris: French Standards Association. (in French)
|
|
|
| [4] |
AFNOR (Association Française de Normalisation). 2003. Soil Quality: Determination of Particle Size Distribution. Paris: French Standards Association. (in French)
|
|
|
| [5] |
Al-Kayssi A W, Mustafa S H. 2016. Modeling gypsifereous soil infiltration rate under different sprinkler application rates and successive irrigation events. Agricultural Water Management, 163: 66-74.
doi: 10.1016/j.agwat.2015.09.006
|
|
|
| [6] |
Al-Quraishi A M F. 2024. Geoinformatics approaches to climate change-induced soil degradation in the Mena region:A review. In: Al-Quraishi A M F, Negm A, Benzougagh B. Climate Change and Environmental Degradation in the MENA Region. The Handbook of Environmental Chemistry. Cham: Springer, 131-152.
|
|
|
| [7] |
Aubert G. 1978. Soil Analysis Methods (2nd ed.). Marseille: French National Center for Pedagogical Documentation. (in French)
|
|
|
| [8] |
Ayers R S, Westcot D W. 1985. Water Quality for Agriculture. Rome: Food and Agriculture Organization of the United Nations.
|
|
|
| [9] |
Brahim N, Ibrahim H, Hatira A. 2014. Tunisian soil organic carbon stock: Spatial and vertical variation. Procedia Engineering, 69: 1549-1555.
doi: 10.1016/j.proeng.2014.03.154
|
|
|
| [10] |
Brahim N, Ibrahim H, Mlih R, et al. 2022. Soil OC and N stocks in the saline soil of Tunisian Gataaya Oasis eight years after application of manure and compost. Land, 11(3): 442, doi: 10.3390/land11030442.
|
|
|
| [11] |
Buerkert A, Dix B A, Al Rawahi M N, et al. 2021. Agro-ecological land use transformation in oasis systems of Al Jabal Al Akhdar, northern Oman. Scientific Reports, 11(1): 7709, doi: 10.1038/s41598-021-85515-9.
pmid: 33833256
|
|
|
| [12] |
Devau N, Le Cadre E, Hinsinger P, et al. 2009. Soil pH controls the environmental availability of phosphorus: Experimental and mechanistic modelling approaches. Applied Geochemistry, 24(11): 2163-2174.
doi: 10.1016/j.apgeochem.2009.09.020
|
|
|
| [13] |
Dhaouadi L, Besser H, Karbout N, et al. 2021. Assessment of natural resources in Tunisian Oases: Degradation of irrigation water quality and continued overexploitation of groundwater. Euro-Mediterranean Journal for Environmental Integration, 6(1): 36, doi: 10.1007/s41207-020-00234-3.
|
|
|
| [14] |
FAO (Food and Agriculture Organization of the United Nations). 2020. World Reference Base for Soil Resources. Rome: Food and Agriculture Organization of the United Nations.
|
|
|
| [15] |
Gao Y J, Tariq A, Zeng F J, et al. 2024. Drying and rewetting affect the chemical speciation and bioavailability of soil phosphorus in a hyper-arid desert ecosystem. Pedosphere, 34(4): 652-667.
doi: 10.1016/j.pedsph.2023.03.018
|
|
|
| [16] |
Hachicha M, Khaskoussy K, Abdelgawad G. 2023. Water and salt regimes under irrigation with brackish/saline water in Tunisian semi-arid context. In: Choukr-Allah R, Ragab R. Biosaline Agriculture as a Climate Change Adaptation for Food Security. Cham: Springer, 195-209.
|
|
|
| [17] |
Hayes-Rich E, Levy J, Hayes-Rich N, et al. 2023. Searching for hidden waters: The effectiveness of remote sensing in assessing the distribution and status of a traditional, earthen irrigation system (khettara) in Morocco. Journal of Archaeological Science: Reports, 51: 104175, doi: 10.1016/j.jasrep.2023.104175.
|
|
|
| [18] |
Heckmann M, Brugeron A O, Dochartaigh B, et al. 2022. Groundwater resources in the ECOWAS region: Expected aquifer productivity. [2025-02-06]. https://nora.nerc.ac.uk/id/eprint/532448/1/GWR_ECOWAS_Technical_Note_en%5B1%5D.pdf.
|
|
|
| [19] |
Johannes A, Matter A, Schuling R, et al. 2017. Optimal organic carbon values for soil structure quality of arable soils: Does clay content matter? Geoderma, 302: 14-21.
doi: 10.1016/j.geoderma.2017.04.021
|
|
|
| [20] |
Kang L F, Wu J M, Zhang C F, et al. 2024. Alterations of soil aggregates and intra-aggregate organic carbon fractions after soil conversion from paddy soils to upland soils: Distribution, mineralization and driving mechanism. Pedosphere, 34(1): 121-135.
doi: 10.1016/j.pedsph.2023.05.011
|
|
|
| [21] |
Kraiem Z, Zouari K, Hleimi A, et al. 2025. Reassessment of Plio-Quaternary aquifer mineralization (Sidi Mansour plain, Southern Tunisia): A machine learning approach. Acque Sotterranee, 14(1): 804, doi: 10.7343/as-2025-804.
|
|
|
| [22] |
Lal R. 2024. Carbon farming in global drylands. In: El-Beltagy A, Lar R, Malik K. Climate Change and Sustainable Agro-ecology in Global Drylands. Wallingford: CAB International, 56-76.
|
|
|
| [23] |
Lu T, Luo P P, Wang J C, et al. 2025. Soil salinity accumulation and groundwater degradation due to overexploitation over recent 40-year period in Yaoba Oasis, China. Soil and Tillage Research, 248: 106398, doi: 10.1016/j.still.2024.106398.
|
|
|
| [24] |
Luo Y, Xiao M L, Yuan H Z, et al. 2021. Rice rhizodeposition promotes the build-up of organic carbon in soil via fungal necromass. Soil Biology and Biochemistry, 160: 108345, doi: 10.1016/j.soilbio.2021.108345.
|
|
|
| [25] |
Masoud A A, El-Horiny M M, Atwia M G, et al. 2018. Assessment of groundwater and soil quality degradation using multivariate and geostatistical analyses, Dakhla Oasis, Egypt. Journal of African Earth Sciences, 142: 64-81.
doi: 10.1016/j.jafrearsci.2018.03.009
|
|
|
| [26] |
McCauley A, Jones C, Olson-Rutz K. 2017. Soil pH and organic matter. Nutrient Management Module No. 8. Montana State University Extension. [2025-01-19]. https://landresources.montana.edu/nm/.
|
|
|
| [27] |
Mlih R, Bol R, Amelung W, et al. 2016. Soil organic matter amendments in date palm groves of the Middle Eastern and North African region: A mini-review. Journal of Arid Land, 8(1): 77-92.
doi: 10.1007/s40333-015-0054-8
|
|
|
| [28] |
Poeplau C, Vos C, Don A. 2017. Soil organic carbon stocks are systematically overestimated by misuse of the parameters bulk density and rock fragment content. Soil, 3(1): 61-66.
doi: 10.5194/soil-3-61-2017
|
|
|
| [29] |
Qadir M, Drechsel P, Salcedo F P, et al. 2023. Chemical risks and risk management measures of relevance to crop production with special consideration of salinity. In: Drechsel P, Zadeh S M, Saldedo F P. Water Quality in Agriculture:Risks and Risk Mitigation. Rome: Food and Agriculture Organization of the United Nations, 41-46.
|
|
|
| [30] |
Santoro A. 2023. Traditional oases in Northern Africa as multifunctional agroforestry systems: A systematic literature review of the provided Ecosystem Services and of the main vulnerabilities. Agroforestry Systems, 97(1): 81-96.
doi: 10.1007/s10457-022-00789-w
|
|
|
| [31] |
Tang J H, Gong L, Ma X Y, et al. 2024. The oasisization process promotes the transformation of soil organic carbon into soil inorganic carbon. Land, 13(3): 336, doi: 10.3390/land13030336.
|
|
|
| [32] |
Védère C, Lebrun M, Honvault N, et al. 2022. How does soil water status influence the fate of soil organic matter? A review of processes across scales. Earth-Science Reviews, 234: 104214, doi: 10.1016/j.earscirev.2022.104214.
|
|
|
| [33] |
Weil R R, Brady N C. 2017. The Nature and Properties of Soils (15th ed.). London: Pearson Press.
|
|
|
| [34] |
Weiner E R. 2008. Applications of Environmental Aquatic Chemistry:A Practical Guide. Boca Raton: CRC Press.
|
|
|
| [35] |
Wichern F, Joergensen R G. 2009. Soil microbial properties along a precipitation transect in Southern Africa. Arid Land Research and Management, 23(2): 115-126.
doi: 10.1080/15324980902817071
|
|
|
| [36] |
Xu L, He N P, Yu G R. 2016. Methods of evaluating soil bulk density: Impact on estimating large scale soil organic carbon storage. CATENA, 144: 94-101.
doi: 10.1016/j.catena.2016.05.001
|
|
|
| [37] |
Zhang L M, Zhuang Q L, Zhao Q Y, et al. 2016. Uncertainty of organic carbon dynamics in Tai-Lake paddy soils of China depends on the scale of soil maps. Agriculture, Ecosystems and Environment, 222: 13-22.
doi: 10.1016/j.agee.2016.01.049
|
|
|
| [38] |
Zhang P P, Shao M A. 2014. Spatial variability and stocks of soil organic carbon in the Gobi Desert of Northwestern China. PLoS ONE, 9(4): e93584, doi: 10.1371/journal.pone.0093584.
|
|
|
|
Viewed |
|
|
|
Full text
|
|
|
|
|
Abstract
|
|
|
|
|
Cited |
|
|
|
|
| |
Shared |
|
|
|
|
| |
Discussed |
|
|
|
|