High Concentrator Photovoltaic Thermal (HCPV/T) systems produce both electrical and thermal energy and they are efficient in areas with high Direct Normal Irradiance (DNI). This paper estimates the lifecycle environmental impact of the HCPV/T 2000x system for both electrical and thermal functionalities. Process-based attributional method following the guidelines and framework of ISO 14044/40 was used to conduct the Life Cycle Assessment (LCA). The midpoint and endpoint impact categories were studied. It was found that the main hotspots are the production of the thermal energy system contributing with 50% and 55%, respectively, followed by the production of the tracking system with 29% and 32% and the operation and maintenance with 13% and 7%. The main contributor to the lifecycle environmental impact category indicators was found to be the raw materials acquisition/production and manufacturing of the thermal energy and tracking systems. The results indicate that the lifecycle environmental impact of the HCPV/T 2000x system is lower compared to fuel-based Combined Heat and Power (CHP) and non-Renewable Energy Sources (non-RES) systems.Sustainability 2019, 11, 7213 2 of 21 and HCPV/T systems include low Energy Payback Time (EPBT), land use reduction, and the potential increase in power density. CSP converts DNI into electrical and thermal energy by using concentrators and conventional power block such as steam turbines, gas turbines and Stirling engines [5].Concentrator solar energy technologies could be directly applied to the buildings or utility-scale and potentially contribute to the global electricity requirements with 7 and 25% by 2030 and 2050, respectively [6][7][8]. However, the application of those technologies could be limited in the regions of high DNI such as MENA (Middle East and North Africa), Mediterranean and the Sun Belt (vast areas of the United States and New Mexico) [6]. In terms of environmental impact, those technologies demonstrated much lower Global Warming Potential (GWP) in comparison to the fossil fuels sources [8,9]. Life Cycle Assessment (LCA) as a useful tool for assessing environmental impact has been applied on the LCPV, LCPV/T, HCPV, HCPV/T and CSP [8][9][10][11][12]. It was found that the use of HCPV/T system for domestic application replacing the traditional systems like electric national grid, boiler and electric heat pump, could reduce annual carbon dioxide (CO 2 ) by 3376 kg [10], while LCPV in building application by 93-101 g /kWh with 2.4 years EPBT and less than 142 g/kWh with 0.7 years EPBT [11,12]. The low values of EPBT are mainly as a result of reduced primary energy demand required for production of the HCPV/T and LCPV systems and their increased efficiency during energy production [10,13,14]. The GWP for HCPV was reported to vary between 16 and 45 g CO 2 -eq/kWh [8,9,15]. The lifecycle CO 2 emission of a parabolic trough and CSP power plant was estimated to be 26 g CO 2 -eq/kWh [16], and 36.3 g CO 2 -eq/kWh [17], respectively. All those studies carried out an environm...