The Barossa and Eden Valleys are renowned viticultural regions which produce premium wines. Water availability and security are the major impediments in long-term sustainable production of their irrigated vineyards. Apart from a hot and dry climate and low water allocation, quality of native and imported water resources in the Barossa region is declining which will potentially have severe adverse impact on the soil and irrigated industries. The climate-soil-crop continuum-based estimation of irrigation requirements is the most efficient way of applying appropriate amount of water to maintain long-term sustainability for this irrigated cropping system. It not only computes the correct amount of water but also helps in restricting off-site movement of water and maintains a congenial environment in the rootzone.
In the current study, six prominent and widely distributed soil types (sand over clay, SOC; shallow soil on rock, SSR; cracking clay soil, CCS; hard red brown soil, HRB; calcareous and gradational soil, CGS; acid and shallow soil on rock, ASR) were identified in the Barossa and Eden Valley regions to evaluate the irrigation requirement and water quality induced risks under different irrigation water sources. Representative local soil, climate, crop, and irrigation system design specific parameters were gathered from selected study sites. Water demand for irrigated vineyards was estimated for the Barossa and Eden Valley regions separately following FAO-56 dual crop coefficient approach for major soil types under the current climate (2000-2023). Subsequently, the long-term (2023-24 to 2050-51) impact of use of various available irrigation water sources in the Barossa region was evaluated in different soils under the median climate change prediction (RCP 4.5) data (NARCliM 1.5) employing multi- component major ion chemistry model HYDRUS-UNSATCHEM. The model was equilibrated with the measured soil solution and exchange parameters for 72 years (1951- 2023) to achieve a quasi-equilibrium state for soil solution and ion exchange behaviour of different soils. Available water quality sources tested are BIL (Barossa Infrastructure Limited) water (Bw), SA water supply (SAw), blended BIL water (Bbw), recycled water (Rew) from Bolivar, and groundwater (Gw) with wide range of salinity (0.35- 3.3 dS/m) and chemical composition (SAR, 3.3- 11.1). A total of 56 scenarios were tested to evaluate the impact of various quality water sources used for irrigation on six soil types (SOC, SSR, CCS, HRB, CGS, ASR) and sustainable management options were explored under four soil indicators i.e., pH, ECsw, SAR and ESP and relative yield reduction in response to rootzone salinity.
Model projections demonstrated that the irrigation requirement of vineyards varied with climate and soil types. In the Barossa Valley region, average annual irrigation requirement varied from 111- 184 mm with a regional average of 136 mm, being higher for sand over clay and calcareous gradational soils and lower for hard red brown and cracking clays. Similar patterns of the average annual irrigation requirement in different soils was observed in the Eden Valley region, however the annual irrigation varied from 79- 157 mm with an average of 103 mm. Annual regional irrigation demand estimated for the cropped area and soil type distribution in the Barossa and Eden Valley was highly correlated with annual (R2 = 0.71- 0.72) and in-season (R2 = 0.76- 0.77) rainfall and showed large year to year variability. Average annual demand over the 23 years for Barossa and Eden was 14.22 Gl/year and 2.04 GL/year, respectively.
Long-term risk assessment (2023-24 to 2050-51) of different quality irrigation waters were performed and model simulations showed that BIL, SA water and blended (15% of CWMS, Community Wastewater Management Scheme) BIL water maintained the rootzone soluble salts (ECsw, 2- 4.5 dS/m) close to the grapevine tolerance threshold (ECsw = 4.2 dS/m) in all soil types over 28 years of irrigation. In heavy textured soils such as cracking clays rootzone salinity of 4.2 dS/m (average tolerance threshold) can have adverse impact on grapevines. Soil solution salinity (ECsw) in different soils was in the order (low to high) ASR > HRB > CGS > SOC > SSR >CCS. Maximum amounts of salts are deposited in the deeper part of the soil profile (1m). Other water sources such as recycled water (EC = 1.8 dS/m) and groundwater (EC = 3.3 dS/m) were observed to increase the ECsw > 10 dS/m, especially at the lower depths of soil profile after 5-10 years of irrigation in the Barossa Valley. In the Eden Valley, irrigation water salinity of 3.3 dS/m (groundwater), maintained the soil solution salinity in the ASR soils below the impact threshold for grapevines signifying the importance of high rainfall induced natural leaching in the soil. Soil pH showed a marginal response to the quality of irrigation water and remained within 7.5- 8.6 range in all the soils and under all irrigation water qualities.
Relative grapevine yield reductions were estimated for the irrigation induced average rootzone salinity developed over 28 years of irrigation with different qualities of irrigation waters. Grapevine yield was reduced by 2.9- 11.5 and 11- 23%, respectively with recycled water and groundwater irrigation. The relative grapevine yield reduction in response to Rew and Gw irrigation in different soils was in the order (high to low) as CCS > SSR > CGS > SOC > HRB. No yield reductions were expected under BIL, SA water and blended BIL water irrigation as the average rootzone salinity remained below the average tolerance threshold (ECsw = 4.2 dS/m).
The irrigation water quality induced sodicity hazard in terms of increased SARsw and ESP was estimated in all the soils. Rapid SAR (high sodium levels compared to Ca and Mg) and ESP development was modelled in all soil types and with all irrigation water qualities including BIL and SA water. Soil solution SAR (SARsw) under BIL water (4-8) had the potential to increase the exchangeable sodium percentage (ESP) more than the threshold level (6%) for soil degradation. Maximum levels of average rootzone SARsw were observed under groundwater irrigation which varied from 6.5- 18 mmol/L1/2 in different soils. Comparatively, cracking clay (CCS) and acid soil on rocks (ASR) showed lower SARsw and ESP values than sand over clay (SOC), calcareous and gradational (CGS) and hard red brown (HRB) soils. The impact of high SARsw on ESP development was rapid in sand textured SOC soil while it was slow in cracking clay (CCS). The maximum level of ESP development was observed under groundwater irrigation ranging from 13.8- 52.0% followed by Rew irrigation (13.9- 31.7%). The ESP development with all other irrigation waters ranged between 3.8- 28.4%.
The critical level of SARsw to exceed the threshold ESP (6%) was estimated for the range of soil types. The average relationship between SARsw and ESP across different soils show that an SARsw of 2.1 can develop an ESP higher than the soil dispersion threshold (6%) in the Barossa region. Similarly, for individual soils an SARsw of 1.7, 3.3, 3.3, 1.2, 3.4 and 0.9, respectively for SOC, SSR, CCS, HRB, CGS and ASR soil was found to develop an ESP more than threshold for soil degradation. Low values for ASR, HRB and SOC soils were related to high ESP at the initial stage at lower soil depths.
Model simulations were performed to investigate options to ameliorate the salinity hazard posed by the long-term use of brackish water. Annual leaching irrigation of 30 mm in spring (early September) with good quality water (BIL) and subsequent irrigation with recycled water (1.8 dS/m) or groundwater (3.3 dS/m) reduced the ECsw below the grapevine tolerance threshold in the upper 40- 50 cm soil. Application of two 30 mm irrigations within a fortnight in September pushed the salts deeper in the soil profile. Salts remained high at lower depths especially in SOC, CCS, and CGS soils.
Model predictions revealed that leaching irrigation alone are not sufficient to ameliorate the irrigation induced high sodicity hazard in the soil solution (SARsw) and on the soil exchange (ESP). The appropriate amount of ameliorant such as gypsum should be applied in along with leaching irrigation to reduce the sodicity hazard which is an inherent character of soil minerology of most of the Barossa and Eden Valley region soils. Previous simulation suggest that the annual gypsum application of 1.7 and 4.3 t/ha can reduce the ESP in sand over clay soil by 20 and 50%, respectively. This application was less effective in other soil types especially heavy textured soils.
Modelling predictions in the current study improved our understanding of the fragile production system for irrigated vineyards in the Barossa and quality of available water resources has the potential to greatly impact on crop yield and soil health indicators. Management options such as leaching irrigation and annual gypsum application are crucial for enhancing the long-term sustainability of vineyards; but maintaining a secure source of good quality water is important to support the wine industry in this region.