Elsevier

Geoderma

Volume 363, 1 April 2020, 114152
Geoderma

Terrace agriculture in a mountainous arid environment – A study of soil quality and regolith provenance: Jabal Akhdar (Oman)

https://doi.org/10.1016/j.geoderma.2019.114152Get rights and content

Hightlights

  • The anthropogenic infill of mountainous soil terraces is of lacustrine provenance.

  • Recurring wet/arid climate alternations enhanced calcrete formation.

  • Younger Dryas event is responsible for the sedimentation of the soil regolith in Oman.

  • The soil quality of abandoned mountainous soil terraces in arid environments considerably deteriorated.

Abstract

In the Sultanate of Oman remnants of deteriorating terrace agricultural systems offer important insights into long-term human adaptation in the arid tropics. Irrigation and terrace agriculture in the mountainous Jabal Akhdar region reveal historic agricultural practices in a rugged, high elevation context. The present study examines soil quality and regolith provenance in abandoned agricultural soil terraces. Three soil profiles in each of the Villages of Hadash and Wijma were excavated and analyzed. Physical, chemical and mineralogical analyses were conducted for all soil horizons. In addition, six other soils, 3 possible soil parent rocks (regolith) and soil’s bedrock were collected. Soil ages were constrained by 14C assays and stable isotope, (13C and 18O) on the bulk carbonates in the calcrete (caliche). The results demonstrate that both sites display poor soil quality with very low average total organic carbon (TOC) (6.2–5.0 g kg−1) and mean weight diameter (MWD; 0.27–0.48 mm), with low water stable aggregate content (<42%). All the geochemical, mineralogical and the thin section analyses show that the soils exhibit unique characteristics that differ from those of other sediments (possible parent regolith) and soils in the vicinity. The finding of ostracod shells in the soil terraces in both areas and 14C dating of calcrete (10.193 ± 30–13.887 ± 40 a BP) indicate that regolith was human-transported to terraces to create soil. The 14C ages of the bulk carbonates match well with a dry period of high calcite precipitation contemporaneous to the Younger Dryas. The Hadash and Wijma soil terraces are located ~45 km away from each other, but still display significant similarities in terms of regolith provenance and soil development and were likely filled with regolith from the same source. These results offer new perspective on agricultural terrace development and oasis agriculture in a rugged, high-elevation, arid environment.

Introduction

Soil terraces are a mode of agriculture found in many regions worldwide (Varotto et al., 2019). Constructing soil terraces to create arable land in rugged terrain is one of the most labor-intensive forms of agriculture practice in arid regions. In semi-arid circum-Mediterranean areas, soil terraces are still a common form of agriculture (Moraetis et al., 2015, Tarolli et al., 2014). However, large areas of terraced landscapes in the Mediterranean area and elsewhere (Bolivia, Peru etc.) have been abandoned, often for social-economic reasons (Koulouri and Giourga, 2007, Tarolli et al., 2014). Cultivation abandonment can have positive or negative influences on soil fertility and erosion (Kosmas et al., 2000b, Novák et al., 2014). There are several studies on soil abandonment resulting in improved soil quality under Mediterranean climatic conditions and with specific site conditions of slope and soil lithology (Dunjó et al., 2003, Kosmas et al., 2000a, Kosmas et al., 2000b). On the contrary, abandonment of soil terraces in more arid environments can be detrimental to soil quality given limited precipitation and the risk of mineral precipitate accumulation. In Yemen, soil terraces, which appear as early as 5000 BP (Wilkinson, 1999), are threatened in many areas due to deterioration and abandonment (Pietsch and Mabit, 2012, Varisco, 1991, Vogel, 1988). Overall, in most other cases adverse environmental impacts have been shown to follow terrace abandonment, including examples in southern Peru (Londoño, 2008), on the Greek islands (Koulouri and Giourga, 2007, Moraetis et al., 2015) and in Spain (Lasanta et al., 2001).

In Oman and on the southern flanks of the Jabal Akhdar, agriculture and eco-tourism in mountainous high elevation areas (up to 1980 m) offer significant economic opportunities. However, some land abandonment is still taking place, which threatens agricultural sustainability and cultural landscapes (Al-Rawahi et al., 2014, Buerkert et al., 2010). In 2008, Luedeling and Buerkert identified the water shortages in the mountain oases of Oman as a contributing factor to soil terrace abandonment. The same study also indicates that shifts toward irrigation demanding crops (roses and fruits) and precipitation pattern changes have contributed to land abandonment. In an extremely arid environment like Oman, terrace abandonment leads to soil desertification, erosion and terrace wall collapse (Luedeling, 2007).

With time, such techniques of soil agriculture in extreme environments are in danger of falling into oblivion especially when these areas are getting abandoned by young generation (Faccini et al., 2018). Investigations of ancient soil terrace landscapes contribute to knowledge of food production among ancient civilizations (Beach et al., 2002, Bevan and Conolly, 2011, Bevan et al., 2013: Charbonnier, 2017, Harrower and Nathan, 2018). Understanding ancient agricultural terracing requires an understanding of how soils form, including their regolith provenance. Natural soil development in countries like Oman is often poor due to aridity, resulting in a lack of vegetation and low TOC values, while extreme precipitation events often result in soil erosion (Ministry of Regional Municipalities, Environment, and Water Resources, 2005). Nagieb et al. (2004) suggested that in Oman mountainous areas, the sediment/regolith was brought in to soil terraces from nearby wadis after heavy rainfalls. However, no studies have demonstrated the regolith provenance in mountainous soil terraces in Oman. Details of such agricultural measures for terrace construction in harsh environments are significant for re-evaluation of ancient agricultural practices. The regolith provenance in such anthropogenically influenced landscapes is not only of local interest, but also of global importance. Such features have a special significance to settlements in extreme environments.

Since the lack of pedogenesis due to high aridity, mountainous terraced soils in Oman constitute a significant sedimentary record under an imminent risk of loss. Moreover, terrace abandonment leads to adverse impacts on the soil quality especially on those marginal areas. Herein, we demonstrate the unique natural value of those areas by studying the soil provenance and the complex pedogenesis in two mountain oases of Oman. We also add new findings on the impact of terrace abandonment on soil quality. To achieve the previous, we present geochemical, physical, mineralogical, microscope and 14C dating evidence of the regolith provenance and soil conditions.

Section snippets

Physical setting

The villages of Hadash and Wijma are located within the Jabal Akhdar Dome of the Central Oman Mountains (Fig. 1). The climatic conditions are characterized by general aridity throughout the year with some scattered and erratic rainfalls and storms (Abdalla and Al-Abri, 2011, Shahalam, 2001). For the assessment of the climatic conditions we have used data from meteorological stations of the Global Historical Climatology Network (GHCN) of the National Oceanic and Atmospheric Administration

Sampling strategy

Three soil pits were excavated in different abandoned soil terraces in Hadash and three in Wijma. We characterized and sampled each soil profile horizon. Hadash soil samples are labelled “H” and Wilma soil samples “W”. In addition, we sampled the bedrock of the two villages, tawny dolomite from Hadash and pinkish siltstone from Wijma. Furthermore, we collected nine samples from different localities of Wadi Mistal and Wadi Sahtan, representing unconsolidated, fine-grained sediments (possible

Hadash and Wijma soils and their physical characteristics

According to FAO (2006), the soils from both sampling areas represent anthrosols. Identified soil horizons are shown in Fig. 4a, b and pH, electrical conductivity, texture and TOC content are shown in and Table 1. The pH for the Hadash soils range between 7.55 and 8.11, and the electrical conductivity (EC) is mostly <300 μS cm−1, except for the Cm3 and Cm4 horizons in profile H2 where it ranges between 601 and 1680 μS cm−1. The texture of the Hadash soils varies in different soil horizons (

Soil quality and evolution in the mountainous abandoned terraces

The depths of the studied soil terraces are similar to that of others around the globe, including, for example, from circum-Mediterranean regions where terrace soil depths range from 30 to 80 cm (Zdruli et al., 2014, Moraetis et al., 2015). The profiles in the lower terraces (H3 and W3 in Fig. 4a, b) display lower soil depths which could reflect soil erosion in terraces of lower elevation. The low TOC content (2.1–1.1 g kg−1) shows that terrace abandonment has negatively affected soil quality

Conclusions

We present results of soil quality and soil provenance analyses for two areas with abandoned soil terraces. Our findings show that the abandoned soil terraces exhibit very low TOC and low soil aggregate stability. Longer lasting processes, like calcrete formation, further deteriorated the soil quality, particularly in terraces consisting of a unique composite soil. Our results indicate that the regolith in these composite soils, which shows a lacustrine origin (ostracods), arrived via human

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

We are thankful to Hamdan Al-Zindi for the thin section production and the technicians of the Earth Sciences Department at Sultan Qaboos University for their assistance. We are also thankful to the Center of Analytical Applied Unit (CAARU) at Sultan Qaboos University, for XRF analysis and mineralogical analysis.

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