Impact of Anthropic Activities on Soil Quality under Different Land Uses.

Anthropization often leads to land use transformation, causing deep changes to soil properties and its quality. Land use change could be an environmental and socioeconomic problem, as it impacts soil quality and ecosystem services. There is an urgent need to understand the pressures affecting soil quality. The aim of the work is to quantify the impact of different land uses on soil abiotic and biotic properties and on its quality. To achieve the aims, soils from different land uses (forest, urban and agricultural) were collected in the surroundings of Naples and analyzed for pH, water content, contents of C and N, C/N ratio and total and available concentrations of Cu, Ni and Pb, microbial and fungal biomasses, basal respiration and metabolic quotient. Then, a soil quality index (SQI) was calculated for each land use. The results showed that soil abiotic and biotic properties of the agricultural sites differed from those of forest and urban sites. At agricultural sites, microbial abundances decreased due to low amount of C and N and to high amount of Cu and Pb. This caused low use efficiency of energetic substrates and a reduced soil quality of agricultural sites as compared to forest and urban sites.

Wastewaters from citrus processing industry as natural biostimulants for soil microbial community.

Citrus fruit processing wastewaters (CWWs), being rich in organic matter, may be a valuable resource for agricultural irrigation and, possibly, for the improvement of soil organic carbon (TOC). This issue is becoming crucial for soils of arid and semiarid environments increasingly experiencing water scarcity and continuous decline of TOC towards levels insufficient to sustain crop production. However, before using CWWs in agriculture their effects on the soil living component have to be clarified. Therefore, in this study we assessed the impact of CWWs on soil chemical and biochemical properties. Under laboratory conditions, lemon, orange and tangerine wastewaters were separately added to a sandy clay soil reaching 1/3, 2/3 and 3/3 of its 50% water holding capacity. Then soils were incubated for 56 days at 22-24 °C in the dark and analyzed for total and extractable organic C, microbial biomass C and N, and the main microbial groups at days 7, 28 and 56, while microbial respiration kinetics was fitted to a first-order decay model by nine distinct daily rates measurements throughout incubation. During the first 3 days following the addition of CWWs, soil pH decreased by 2-3 units; however, afterwards the soil recovered its initial pH values. Total and extractable C pools, as well as microbial biomass C and N, were stimulated by CWWS with such a stimulation depending on CWWs type and added dose. Also microbial respiration kinetics was greatly affected by CWWs, although the effects were generally ephemeral at the lowest two doses, whereas at the highest dose still persisted up to day 56, especially in orange and lemon wastewaters. The concomitant general increase of both microbial and metabolic quotients after the addition of CWWs suggested that also under stress conditions, soil microorganisms were able to immobilize C. Both bacteria and fungi were stimulated by CWWs but the latter, at the beginning of incubation, were more favored probably due to a transient soil acidification by CWWs. In conclusion, CWWs when added to a sandy-clay soil increased total and labile C pools, stimulated soil microbial activity and biomass, i.e. improved the overall biological soil fertility, thus suggesting a possible role of CWWs in sustainable agriculture. However, soil electrical conductivity has to be monitored when CWWs are applied recurrently.

Clay beads as artificial trapping matrices for monitoring bacterial distribution among urban stormwater infiltration systems and their connected aquifers.

Stormwater infiltration systems (SIS) have been developed to limit surface runoff and flooding in urban areas. The impacts of such practices on the ecological and biological quality of groundwater ecosystems remain poorly studied due to the lack of efficient methodologies to assess microbiological quality of aquifers. In the present study, a monitoring method based on the incubation of artificial matrices (clay beads) is presented to evaluate microbial biomass, microbial activities, and bacterial community structure. Four microbial variables (biomass, dehydrogenase and hydrolytic activities, bacterial community structures) were measured on clay beads incubated in three urban water types (stormwater surface runoffs, SIS-impacted and non-impacted groundwaters) for six SIS. Analyses based on next-generation sequencing (NGS) of partial rrs (16S rRNA) PCR products (V5-V6) were used to compare bacterial community structures of biofilms on clay beads after 10 days of incubation with those of waters collected from the same sampling points at three occasions. Biofilm biomass and activities on clay beads were indicative of nutrient transfers from surface to SIS-impacted groundwaters. Biofilms allowed impacts of SIS on groundwater bacterial community structures to be determined. Although bacterial communities on clay beads did not perfectly match those of waters, clay beads captured the most abundant bacterial taxa. They also captured bacterial taxa that were not detected in waters collected at three occasions during the incubation, demonstrating the integrative character of this approach. Monitoring biofilms on clay beads also allowed the tracking of bacterial genera containing species representing health concerns.

Greenhouse gas emissions from a Cu-contaminated soil remediated by in situ stabilization and phytomanaged by a mixed stand of poplar, willows, and false indigo-bush.

Phytomanagement of trace element-contaminated soils can reduce soil toxicity and restore soil ecological functions, including the soil gas exchange with the atmosphere. We studied the emission rate of the greenhouse gases (GHGs) CO2, CH4, and N2O; the potential CH4 oxidation; denitrification enzyme activity (DEA), and glucose mineralization of a Cu-contaminated soil amended with dolomitic limestone and compost, alone or in combination, after a 2-year phytomanagement with a mixed stand of Populus nigra, Salix viminalis, S. caprea, and Amorpha fruticosa. Soil microbial biomass and microbial community composition after analysis of the phospholipid fatty acids (PLFA) profile were determined. Phytomanagement significantly reduced Cu availability and soil toxicity, increased soil microbial biomass and glucose mineralization capacity, changed the composition of soil microbial communities, and increased the CO2 and N2O emission rates and DEA. Despite such increases, microbial communities were evolving toward less GHG emission per unit of microbial biomass than in untreated soils. Overall, the aided phytostabilization option would allow methanotrophic populations to establish in the remediated soils due to decreased soil toxicity and increased nutrient availability.

High throughput sequencing analysis of the joint effects of BDE209-Pb on soil bacterial community structure.

Decabromodiphenyl ether (BDE209) and Lead (Pb) are the main pollutants at e-waste recycling sites (EWRSs). However, the impact on soil microorganism of joint exposure to the two chemicals remains almost unknown. Therefore, the indoor incubation tests were performed to determine the response of soil microbial biomass and activity as well as bacterial community structure in the presence of the two chemicals during 60 d incubation period. The results indicated that after Pb alone or BDE209-Pb exposure, soil microbial biomass C (Cmic) was significantly lower (p<0.01), and soil basal respiration (SBR) and metabolic quotient (qCO2) were enhanced, while BDE209 barely resulted in significant influence (p>0.05). 16S rRNA gene sequencing on the Illumina MiSeq platform demonstrated that a total 49,405 valid sequences widely represented the diversity of microbial community. Sequence analyses at phylum and genus taxonomic levels illustrated that 11 identified phyla and 297 genera were observed among all the soil samples, and the contaminants input had affected bacterial community structure, suggesting that Proteobacteria, Actinobacteria and Acidobacteria were the dominant phyla, and the genera Massilia and Bacillus were enriched in contaminated soil. BDE209 exposure alone in all the samples indicated a more similar community structure compared to the control. The results of these observations have provided a better understanding of ecotoxicological effects of BDE209 and Pb joint exposure on indigenous microorganisms in soil at EWRSs.