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Field Studies on the Influence of High‐Voltage Direct Transmission Underground Cables on Soils Along the SuedLink Route in Southwest Germany

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ABSTRACT Background The SuedLink was planned as a high‐voltage direct‐current underground cable route. The construction itself is a massive intervention on soil, and during operation, the power cables emit up to 32 W of heat per cable meter at maximum load. Aims The study aimed to investigate the impact of the construction and the heat emission of the SuedLink on soils typical of Southwest Germany. Methods Four test sites, each covering approximately 0.6 ha, were established following best practice along the planned SuedLink route in 2021. Each test site was set up in a fully randomized split‐plot design. Heating pipes were installed at a depth of 1.5 m with a target heat emission of 32 W per meter of cable. Each test site was extensively instrumented with temperature, heat flux, and soil moisture sensors. Results Temperatures 5 cm above the heating pipes at a depth of 1.25 m were 14–16°C higher than the control. In the heated plots, soil temperatures in the center of the plowing horizon at 0.15 m depth were 1–3°C higher than in the control soil. The strip affected by the heat emission had a width of about 10 m. Negative impacts on bulk density, plant‐available water, and air capacity were not observed. Conclusions During regular operation at a load ≤75%, the average increase in temperature in the plowing horizon at a depth of 0.15 m is expected to be less than 1.6°C in the soils along the SuedLink route in Southwest Germany.

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Photo source: Flickr/WorldFish Arsenic is a widely distributed toxic element that naturally occurs in minerals. One of the most common pathways for exposure is when arsenic leaches into drinking water supplies, often through natural weathering/breakdown. People are also exposed to arsenic through food and dust. Long-term exposure is linked to health problems, including skin lesions, cardiovascular disease, and cancer. Research from Bangladesh shows long-term exposure through drinking water increases the rate of morbidity by up to 60% (http://bit.ly/2fFhq6w). Understanding exposure routes and minimizing human consumption and contact with arsenic has widespread human health benefits. One crop known to take up arsenic when the element is available in soils or irrigation water is rice (Oryza sativa L.). Arsenic accumulates throughout the plant tissues including the grain that is consumed. This is concerning for people whose diets include a high proportion of rice or rice products such as regions and cultures where rice is served with most meals, those on a gluten-free diet using rice substitutes (e.g., rice milk or rice flour), and young children who are given rice crackers and rice cereals. Rice plants may be exposed to arsenic through soil or irrigation water. Because of this, the hydrological and biogeochemical processes that take place in the rhizosphere, or the soil zone around the roots of plants, influence arsenic uptake, according to Rebecca Neumann, Assistant Professor in the Department of Civil and Environmental Engineering at the University of Washington. Specifically, rice plants release oxygen from their roots when flooded, which reacts with iron, forming “plaques” along root surfaces. The iron oxide plaques scavenge arsenic, and the plants take up arsenic released from the plaques or dissolved in the soil solution. 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Urbanization coincides with remarkable environmental changes including vegetation, soil and climate. An urban heat island is a well-known urban mesoclimatic anomaly, however its effect on functions of urban soils considering their spatial-temporal variability remain overlooked. The research aimed to explain the urban heat island effect on soil microbial respiration by linking meso-climatic CCLM and TERRA_URB models and the digital soil mapping approach for the case of Moscow megalopolis. Moscow megalopolis is the biggest city in Russia, which experiences on-going urbanization within the New Moscow project. As a result, a clear urbanization gradient was observed in land-use structure, climate and soil properties. For the study period (May–October 2019), the increase in average monthly temperature of urban soils compared to rural reached 1.7 and 2.0 °C in June and September with the maximal values obtained in the city center. The significant effect of soil temperature, carbon content and pH on soil microbial (basal) respiration was estimated based on the lab experiment with a representative sample of urban topsoils (n = 140). The resulting equation was integrated with the mesoclimatic data in two ways: i) considering urban heat islands (based on the modelled 500 m grid soil temperature maps) and ii) non-considering urban heat islands (based on the average monthly rural soil temperature). Comparison of the results showed that urban heat island increased microbial respiration by 5–10% on average and up to 25% in the most affected locations. The additional amount of CO2 which could be potentially emitted by soil microbes as a result of the urban heat island in Moscow megapolis was on average 0.2 Mg C ha−1 (0–10 cm layer; 1.1 g cm−3 bulk density). Small scale green zones in the city center (public gardens, residential court yards and green lawns along the roads) where high soil C contents coincided with the maximal urban heat island effect were the hotspots of microbial respiration. Although the estimated absolute values could be rather uncertain, the research highlights the vulnerability of urban topsoil C stocks to mineralization intensified by mesoclimatic anomalies.

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