Relationship between soil physiochemistry and land degradation in the lower Heihe River basin of northwestern China

Abstract

Monitoring of soil-water physiochemistry (pH, total salt content, ion types, and ion ratios) across the lower Heihe River basin of northwestern China indicated that the distribution of different soil hydrochemical types typically correlated with that of different levels of soil desertification, specifically: 1) lands with the potential for desertification showed a Cl⁻-SO ²⁻₄ -Na⁺-Mg²⁺ soil-water ion complement, 2) those under on-going desertification a SO ²⁻₄ -Cl⁻-Mg²⁺-Na⁺ ion complement, 3) those under severe desertification a HCO ⁻₃ -Cl⁻-Ca²⁺-Na⁺ ion complement, and 4) those under very severe desertification a Cl⁻-SO ²⁻₄ -Mg²⁺-Na⁺ ion complement. The total soil N, P, and K, pH and organic matter of desertified lands tend to be relatively spatially concentrated, whereas available N, P and K are scattered. Based on an analysis of the main nutrients, the cumulative percent contribution of total N, total P, organic matter, and available N reached 76.24% of ecosystem needs and basically reflect the level of soil fertility. According to a low-dimensional cluster analysis of principal components and the differentiation and alikeness of integrated nutrient gradients, the soils in the study region were classified into four types, which coincided spatially with the four desertification land types. With a decrease in the quantity of water exiting the upper and middle reaches of the Heihe River basin, the salinity of surface waters and shallow water table depth (WTD) in the lower reaches have significantly increased through evaporation. The changes in the hydrological process have caused an imbalance in water distribution across the basin, and altered the state of oasis-supporting water resources. The deterioration of soil water and expansion of desertification progress from non-salinized soils in the oasis, to soils slightly salinized through periodic salt accumulation, salinized Chao soils, and salinized forest shrub meadow soils along the riverbanks and on lake shores. These can then evolve into moderately to heavily salinized soils and eventually into alkali lands. All together, these degradative processes constitute the complex dynamics of oasis desertification, whereby the natural oases’ surface biotic productivity system is degraded, leading to oasis shrinkage, ecosystem deterioration, and land desertification. Consequently, there is an urgent need to extend the study of soil and surface water chemistry in the region.