[Performance and Mechanisms of Advanced Nitrogen Removal via FeS-driven Autotrophic Denitrification Coupled with ANAMMOX].

Synergy among members of complex microbial communities in the transformation of elements is a key ecological regulation strategy in nature. Making full use of this phenomenon and achieving functional combinations of different microorganisms may have a significant effect on developing new wastewater treatment processes. In this study, nitrogen-containing pollutants were applied in a static batch experiment. The dosage of FeS, the ratio of NO3--N/NO2--N, and the ratio of ANAMMOX (AN) to autotrophic denitrification (AD) biomass were the controlled reaction conditions. The cooperation mechanism resulting from the metabolic complementation of AN and AD is discussed, and the concept of a (AN+AD)TN 0 nitrogen removal process is proposed. This study showed that the excessive dosage of FeS could ensure the more thorough reaction of AD without significantly affecting the metabolic activity of AN bacteria. A complex microbial community was involved in the competition for metabolic substrates when the proportion of NO2--N in the electron acceptor was increased, resulting in a negative impact on the removal of TN. The increase of AN biomass contributed to the strengthening of the cooperation between AN and AD. When the stoichiometric ratio of NH4+-N to NO3--N was less than 0.85, TN could be completely removed. The results showed that a more effective wastewater treatment process may be established by understanding the interactions between microorganisms, and by manipulating or regulating complex microbial communities. This could achieve the efficient removal of pollutants under low material consumption conditions.

[Evaluation of Advanced Nitrogen Removal from Coking Wastewater Using Sulfide Iron-containing Sludge as a Denitrification Electron Donor].

In general, it is difficult to reach the total nitrogen discharge standard in the effluent after municipal and industrial wastewater treatment. The problems hindering advanced denitrification include an unstable C/N ratio in the influent wastewater, increased hydraulic loading with increasing reflux ratio, reduced reaction kinetics, high energy consumption, and secondary pollution and high sludge yield resulting from addition of organic carbon sources. Therefore, deep denitrification with the advantages of energy savings and easy operation is urgently needed. To address these issues, chemical iron sulfide sludge, collected after the pretreatment of sulfur-containing industrial wastewater, was used as a solid-phase electron donor to perform advanced denitrification using autotrophic denitrifiers. In this study, the secondary biological effluent of coking wastewater was the influent for denitrification and the performance of denitrification, transformation of sulfide and iron in the sludge, and microbial community changes were investigated. The optimal reaction conditions and effect range of the technology for deep denitrification of wastewater were then calculated. When the concentrations of NO3--N and NO2--N in the influent were (74.54±0.57) and (1.11±0.19) mg·L-1, respectively, the corresponding concentrations in the effluent were reduced to (2.78±1.08) and (2.87±0.71) mg·L-1, respectively, with a hydraulic retention time (HRT) of 18 h. The removal rate of TON (NO3--N+NO2--N) was as high as 90.0%, of which the reduction rate of NO3--N and the accumulation rate of NO2--N were 12.06 and 7.74 mmol·(L·d)-1, respectively. This study showed that the use of chemical sulfide iron sludge as an electron donor for deep denitrification is of practical importance, as it could simplify the subsequent treatment of sulfur- and iron-rich chemical sludge, finally reaching the goal of resource utilization.

2-(Pyrimidin-2-ylsulfan-yl)acetic acid.

The mol-ecule of the title compound, C(6)H(6)N(2)O(2)S, lies on a crystallographic mirror plane with the methyl-ene H atoms related by mirror symmetry. In the crystal packing, mol-ecules are linked into layers by inter-molecular O-H⋯N and C-H⋯O hydrogen bonds.

4-[4-(Diethyl-amino)benzyl-ideneamino]-4H-1,2,4-triazole.

The title compound, C(13)H(17)N(5), is a Schiff base synthesized by the reaction of 4-amino-4H-1,2,4-triazole and 4-(diethyl-amino)benzaldehyde. The triazole ring forms a dihedral angle of 5.77 (16)° with the benzene ring. The crystal structure is stabilized by an inter-molecular C-H⋯N hydrogen bond.