Increases in the soil ammonia oxidizing phylotypes and their rechange due to long-term irrigation with wastewater.

Wastewater irrigation is a common practice for agricultural systems in arid and semiarid zones, which can help to overcome water scarcity and contribute with nutrient inputs. Ammonia-oxidizing bacteria (AOB) and archaea (AOA) are key in the transformation of NH4+-N in soil and can be affected by variations in soil pH, EC, N and C content, or accumulation of pollutants, derived from wastewater irrigation. The objective of this study was to determine the changes in the ammonia oxidizing communities in agricultural soils irrigated with wastewater for different periods of time (25, 50, and 100 years), and in rainfed soils (never irrigated). The amoA gene encoding for the catalytic subunit of the ammonia monooxygenase was used as molecular reporter; it was quantified by qPCR and sequenced by high throughput sequencing, and changes in the community composition were associated with the soil physicochemical characteristics. Soils irrigated with wastewater showed up to five times more the abundance of ammonia oxidizers (based on 16S rRNA gene relative abundance and amoA gene copies) than those under rainfed agriculture. While the amoA-AOA: amoA-AOB ratio decreased from 9.8 in rainfed soils to 1.6 in soils irrigated for 100 years, indicating a favoring environment for AOB rather than AOA. Further, the community structure of both AOA and AOB changed during wastewater irrigation compared to rainfed soils, mainly due to the abundance variation of certain phylotypes. Finally, the significant correlation between soil pH and the ammonia oxidizing community structure was confirmed, mainly for AOB; being the main environmental driver of the ammonia oxidizer community. Also, a calculated toxicity index based on metals concentrations showed a correlation with AOB communities, while the content of carbon and nitrogen was more associated with AOA communities. The results indicate that wastewater irrigation influence ammonia oxidizers communities, manly by the changes in the physicochemical environment.

Exploring the polyurethanolytic activity and microbial composition of landfill microbial communities.

The microbial composition of polyurethane degrading communities has been barely addressed, and it is unknown if microenvironmental conditions modify its composition, affecting its biodegradative capacity. The polyurethanolytic activity and taxonomic composition of five microbial communities, selected by enrichment in the polyether-polyurethane-acrylic (PE-PU-A) coating PolyLack®, from deteriorated PU foams collected at different microenvironments in a municipal landfill (El Bordo Poniente, BP) were explored. All BP communities grew similarly in PolyLack® as the sole carbon source, although BP1, BP4, and BP5 showed better performance than BP2 and BP7. FTIR spectroscopy showed that ester, urethane, ether, aromatic and aliphatic groups, and the acrylate component were targets of the biodegradative activity. Extracellular esterase activity was higher at 5 days of cultivation and decreased at 21 days, while urease activity showed the opposite. Microbial composition analysis, assessed by 16S rDNA V3 region PCR-DGGE, revealed a preponderance of Rhizobiales and Micrococcales. The reported PU-degrading genera Paracoccus, Acinetobacter, and Pseudomonas were identified. In contrast, Advenella, Bordetella, Microbacterium, Castellaniella, and Populibacterium, some of them xenobiotics degraders, can be considered potentially PU-degrading genera. Correspondence analysis identified independent groups for all communities, except the BP4 and BP5. Although partial taxonomic redundancy was detected, unique OTUs were identified, e.g., three members of the Weeksellaceae family were present only in the BP4/BP5 group. These results suggest that the microenvironmental conditions where the landfill microbial communities were collected shaped their taxonomical composition, impacting their PE-PU biodegradative capacities. These BP communities represent valuable biological material for the treatment of PU waste and other xenobiotics. KEY POINTS: • Landfill microbial communities display slightly different capacities for growing in polyether-polyurethane-acrylic. • Ester, urethane, ether, aromatic, aliphatic, and acrylate groups were attacked. • Esterase activity was more significant at early culture times while urease activity at latter. • Landfill microenvironments shape partial taxonomical redundancy in the communities. • Best communities' performance seems to be related to unique members' composition.