Haloxylon ammodendron (C.A.Mey.) Bge. is crucially important for stabilizing sand dunes in the desert area of the Junggar Basin and has thus been widely planted in the oasis–desert ecotone for windbreak and sand fixation purposes since the 1980s. The spatial distribution and structural characteristics of Haloxylon ammodendron plantations of three different ages—planted in 1983 (36a), 1997 (22a), and 2004 (15a)—on the southwestern edge of the Gurbantünggüt Desert were studied. The results showed that the spatial distribution patterns for the different stages of growth showed a trend of cluster that was random during the transformation from seedlings to juvenile and mature trees. Forest density for the 15a, 22a, and 36a plantations was, respectively, 1110, 1189, and 1933 plants ha⁻¹; the base stem diameter for the main forest layer was 5.85, 8.77, and 6.17 cm, respectively, and the tree height was concentrated in the range of 1.5–3.0 m, 2.0–3.5 m, and 1.5–2.5 m. In the regeneration layers, the proportion of seedlings was the largest in all three stand ages, followed by juvenile trees, and mature trees only appeared in the 22a plantation. The proportion of deadwood in the 36a forest was the highest, and there were no mature trees in the regeneration layer. These results indicate that the three Haloxylon ammodendron plantation stages were in the period of rising at 15a, stable and degenerate with increasing age at 22a, and at 36a the regeneration ability was very weak and presented degradation due to species competition for soil moisture, because of too many seedlings and mature plants. In this case, measures such as thinning could be taken to prevent rapid degradation and to accelerate regeneration when the stand age exceeds 20 years. Considering the sand fixation effect, the pressure of competition for water resources, and forest capacity for renewal and sustainability, the most suitable forest density in the Haloxylon ammodendron plantation would be 8.5–9 m² per plant.

Haloxylon ammodendron is a perennial xerophyte that can survive in extremely harsh desert conditions of Central Asia. This study evaluated the effect of salinity, and their ability to recover on seed germination of H. ammodendron, which were collected at three different desert areas, Bakanas takyr plain (H1), Gurbantüngüt Desert (H2), and Gobi Desert (H3), respectively. Seeds were treated with different concentrations of NaCl and Na₂SO₄ (0.00 (control), 0.05, 0.10, 0.20, 0.40, 0.60, 0.80, 1.00, 1.20, and 1.40 mol/L) to detemine the germination and recover ability to salt stress. The results of the study were that H. ammodendron were more resistant to Na₂SO₄ than to NaCl. Regarding inhibition of seed germination H. ammodendron was in the following order: H3 > H2 > H1. Based on the tolerance and recovery, seeds can be demonstrated as follows: NaCl: H3 > H1 > H2; Na₂SO₄: H1 = H2 = H3. Non-germinated seeds in all salt treatments with low osmotic potential showed high recovery when transferred to distilled water, indicating that these treatments were not too toxic to affect seed viability. These results suggest that H. ammodendron can withstand high levels of salinity at three desert environments. Thus, H. ammodendron could be used to reconstruct vegetation and sustanbility development in the desert areas with high salinity.

Coal mining has significantly degraded the ecological environment, and the ecosystem structure of the southern slopes of the Tianshan Mountains is complex, with drought, low rainfall, and ecological fragility increasing the difficulty of ecological restoration. There are few studies on the selection of suitable pioneer species for the restoration of mining areas on the south slope of Tianshan Mountain. In this study, we investigated the artificial restoration of vegetation in the damaged areas of nine representative coal mines on the south slope of the Tianshan Mountains. We categorized the coal mines into three classes based on elevation. Using a combination of the entropy weight method and the technique for order preference by similarity to ideal solution (TOPSIS), indicators such as the diversity index and vegetation cover were selected to compare the recovery of vegetation in the mining area and screen for suitable pioneer species in ecologically damaged areas. The results show the following: (1) Based on the entropy weight TOPSIS findings, Run Hua coal mine, Da Wanqi coal mine, and Ke Xing coal mine are the highest-scoring coal mines among different types of coal mines. (2) Based on the score results and species rankings, species combinations including Agropyron cristatum, Achnatherum splendens, Medicago sativa Linn, and Halogeton glomeratus are recommended for altitudes below 1500 m. For altitudes between 1500 m and 2000 m, combinations including Festuca elata Keng ex E, Agropyron cristatum, Halogeton glomeratus, and Artemisia sieversiana Ehrhart ex Willd are recommended; similarly, combinations including Agropyron cristatum, Achnatherum splendens, Seriphidium kaschgaricum, and Halogeton glomeratus are recommended for elevations above 2000 m. This study discusses the recovery of artificial vegetation communities within 2 years, with a view to providing a theoretical basis and data support for the recovery of the remaining ecologically damaged areas of the same types.