•The solid controlled-release inhibitor showed a long term anticorrosion performance for Q235-b in 1 M HCl solution.•A FeOB passive film is found to form on the Q235-b surface in the presence of the inhibitor.•The passivation-breakdown-repassivation process is detected on the Q235-b surface.Borate was regarded as an interesting material for a broad range of applications. Here, we had prepared a novel borate-based controlled-release inhibitor to improve the anticorrosion performance of Q235-b in 1 M HCl. The effective components released by the inhibitor were boron and sodium, and its anticorrosion performance was investigated by various electrochemical methods The potentiodynamic polarization curve results indicated that the borate-based inhibitor showed a clear anodic-type inhibitor characteristic, and a great improvement of the resistance was obtained from the electrochemical impedance spectroscopy, resulting from the formation of a passive film with FeOB structure on the Q235-b surface. The formation process followed the Langmuir isotherm well, and the passive film showed a self-healing capability, which confirmed by the electrochemical noise. Further, the anticorrosion capability of the inhibitor gradually increased with the increasing release time. After 21 days of release, the boron concentration reached 125 mg L−1, the anticorrosion efficiency was over 97%, and a smooth surface was observed on the Q235-b surface from electron microscopy. According to these results, we believed that the borate-based controlled-release inhibitor displayed a satisfactory capability to suppress corrosion on the Q235-b surface in 1 M HCl. The present work provided a novel concept for the development of corrosion inhibitor.Download high-res image (225KB)Download full-size image

Chlorpyrifos can be effectively adsorbed by drinking water treatment residuals (WTR), ubiquitous and non-hazardous by-products of potable water production. The major metabolite 3,5,6-trichloro-2-pyridinol (TCP) was found to be much more mobile and toxic than its parent chlorpyrifos. To assess the feasibility of WTR amendment for attenuation of chlorpyrifos and TCP pollution, the sorption/desorption and degradation behavior of chlorpyrifos and TCP in WTR-amended agricultural soils was examined in the present study.Two representative agricultural soils were sampled from southern and northern China, respectively. The soils were amended with WTR at the rates of 0, 2, 5, and 10 % (w/w). Batch sorption/desorption test were applied to investigate the sorption/desorption characteristics of chlorpyrifos and TCP in WTR-amended soils. The influence of WTR amendment on chlorpyrifos degradation and TCP formation was evaluated using the incubation test, and its effect on the soil bacterial abundance was further studied through DNA extraction and PCR amplification.Results showed that WTR amendment (0–10 %, w/w) significantly enhanced the retention capacity of chlorpyrifos and TCP in both soils examined (P < 0.05). Fractionation analyses further demonstrated that the bioavailability of chlorpyrifos was considerably reduced by WTR amendment, resulting in a decreased chlorpyrifos degradation rate. The WTR amendment also significantly reduced the mobility of TCP formed in chlorpyrifos-contaminated soils (P < 0.001). The chlorpyrifos toxicity to soil bacteria community was largely mitigated following WTR amendment, resulting in increased total bacterial abundance.Results obtained in the present study indicate a great deal of potential for the beneficial reuse of WTR as soil amendments for chlorpyrifos and TCP pollution control.

The riparian zone is an active interface for nitrogen removal, in which nitrogen transformations by microorganisms have not been valued. In this study, a three-stage system was constructed to simulate the riparian zone environments, and nitrogen removal as well as the microbial community was investigated in this ‘engineered riparian system’. The results demonstrated that stage 1 of this system accounted for 41–51 % of total nitrogen removal. Initial ammonium loading and redox potential significantly impacted the nitrogen removal performances. Stages 1 and 2 were both composed of an anoxic/oxic (A/O) zone and an anaerobic column. The A/O zone removed most of the ammonium load (6.8 g/m2/day), while the anaerobic column showed a significant nitrate removal rate (11.1 g/m2/day). Molecular biological analysis demonstrated that bacterial diversity was high in the A/O zones, where ammonium-oxidizing bacteria and nitrite-oxidizing bacteria accounted for 8.42 and 3.32 % of the bacterial population, respectively. The denitrifying bacteria Acidovorax sp. and the nitrifying bacteria Nitrosospira/Nitrosomonas were the predominant microorganisms in this engineered riparian system. This three-stage system was established to achieve favorable nitrogen removal and the microbial community in the system was also retained. This investigation should deepen our understanding of biological nitrogen removal in engineered riparian zones.

Nitrification plays a significant role in the global nitrogen cycle, and this concept has been challenged with the discovery of ammonia-oxidizing archaea (AOA) in the environment. In this paper, the vertical variations of the diversity and abundance of AOA in the hyporheic zone of the Fuyang River in North China were investigated by molecular techniques, including clone libraries, phylogenetic analysis and real-time polymerase chain reaction. The archaeal amoA gene was detected in all sediments along the profile, and all AOA fell within marine group 1.1a and soil group1.1b of the Thaumarchaeota phylum, with the latter being the dominant type. The diversity of AOA decreased with the sediment depth, and there was a shift in AOA community between top-sediments (0–5 cm) and sub-sediments (5–70 cm). The abundance of the archaeal amoA gene (1.48 × 107 to 5.50 × 107 copies g−1 dry sediment) was higher than that of the bacterial amoA gene (4.01 × 104 to 1.75 × 105 copies g−1 dry sediment) in sub-sediments, resulting in a log10 ratio of AOA to ammonia-oxidizing bacteria (AOB) from 2.27 to 2.69, whereas AOB outnumbered AOA in top-sediments with a low log10 ratio of (−0.24). The variations in the AOA community were primarily attributed to the combined effect of the nutrients (ammonium-N, nitrate-N and total organic carbon) and oxygen in sediments. Ammonium-N was the major factor influencing the relative abundance of AOA and AOB, although other factors, such as total organic carbon, were involved. This study helps elucidate the roles of AOA and AOB in the nitrogen cycling of hyporheic zone.

Recent efforts have increasingly focused on the development of low-cost adsorbents for pesticide retention. In this work, the novel reuse of drinking water treatment residuals (WTRs), a nonhazardous ubiquitous byproduct, as an adsorbent for chlorpyrifos was investigated. Results showed that the kinetics and isothermal processes of chlorpyrifos sorption to WTRs were better described by a pseudo-second-order model and by the Freundlich equation, respectively. Moreover, compared with paddy soil and other documented absorbents, the WTRs exhibited a greater affinity for chlorpyrifos (log Koc = 4.76–4.90) and a higher chlorpyrifos sorption capacity (KF = 5967 mg1–n·L·kg–1) owing to the character and high content of organic matter. Further investigation demonstrated that the pH had a slight but statistically insignificant effect on chlorpyrifos sorption to WTRs; solution ionic strength and the presence of low molecular weight organic acids both resulted in concentration-dependent inhibition effects. Overall, these results confirmed the feasibility of using WTRs as a novel chlorpyrifos adsorbent.

Both β-proteobacterial aerobic ammonium-oxidizing bacteria (AOB) and anaerobic ammonium-oxidizing (ANAMMOX) bacteria were investigated in the hyporheic zone of a contaminated river in China containing high ammonium levels and low chemical oxygen demand. Fluorescence in-situ hybridization (FISH), denaturing gradient gel electrophoresis (DGGE) and cloning-sequencing were employed in this study. FISH analysis illustrated that AOB (average population of 3.5 %) coexisted with ANAMMOX bacteria (0.7 %). The DGGE profile revealed a high abundance and diversity of bacteria at the water–air–soil interface rather than at the water–soil interface. The redundancy analysis correlated analysis showed that the diversity of ANAMMOX bacteria was positively related to the redox potential. The newly detected sequences of ANAMMOX organisms principally belonged to the genus Candidatus “Brocadia”, while most ammonia monooxygenase subunit-A gene amoA sequences were affiliated with Nitrosospira and Nitrosomonas. These results suggest that the water–air–soil interface performs an important function in the nitrogen removal process and that the bioresources of AOB and ANAMMOX bacteria can potentially be utilized for the eutrophication of rivers.

The characteristics of polycyclic aromatic hydrocarbons (PAHs) in water, suspended particulate matter (SPM), sediments, and hydrophytes from Lake Baiyangdian, a shallow freshwater lake in China were studied. The low-molecular-weight PAHs (2–3 ring PAHs) predominated (61.2 to 84.5%) in all samples. Principal component analysis (PCA) of individual PAHs and the ratios of selected PAHs showed that the PAHs in the lake were mainly petrogenic inputs. The solid-liquid distribution coefficient (Kd) in the water phase was much higher than the bioconcentration factor (BCF), and the leaf concentration factor (LCF) was higher than the root concentration factor (RCF) and stem concentration factor (SCF) in plant-sediment phase. Good linear log/log relationships were observed between the equilibrium partitioning coefficient (Koc) and the octanol–water partitioning coefficient (Kow), between RCF and Kow, and between LCF and the octanol–air partitioning coefficient (Koa). These results indicated that PAHs accumulated more easily in SPM than in submerged aquatic plants, and some low-molecular-weight PAHs could accumulate and be translocated in the lake's media. Media characteristics, contamination sources, and physicochemical properties all affect the partitioning of PAHs among water, SPM, sediments, and hydrophytes.

A study on the removal of Co(II) from aqueous solutions by water treatment residuals (WTR) was conducted in batch conditions. The sorption process of Co(II) followed pseudosecond-order kinetics, with 30 hr required to reach equilibrium. Using the Langmuir adsorption isotherm model, a relatively high maximum sorption capacity of 17.31 mg/g Co(II) was determined. The adsorption of Co(II) was dependent on pH values and was affected by the ionic strength. Results show that Co(II) adsorption was a spontaneous endothermic process and was favorable at high temperature. Most of the adsorbed Co(II) stayed on the WTR permanently, whereas only small amounts of adsorbed Co(II) were desorbed. The shifting of peaks in FT-IR spectra indicated that Co(II) interacted with the WTR surface through strong covalent bond formation with Fe(Al)–O functional groups. It was concluded that WTR can be a suitable material from which to develop an efficient adsorbent for the removal of Co(II) from wastewater.Recent efforts have increasingly focused on the development of low-cost adsorbents for Co(II) removal. In this work, the novel reuse of water treatment residuals (WTRs), a nonhazardous ubiquitous byproduct, as an adsorbent for Co(II) was investigated. This study was focused on the factors influencing Co(II) immobilization by WTR. Results showed that WTR as an adsorbent is suitable for removing Co(II) from aqueous solutions.Download high-res image (76KB)Download full-size image

Drinking water treatment residuals (WTRs) have a potential to realize eutrophication control objectives by reducing the internal phosphorus (P) load of lake sediments. Information regarding the ecological risk of dewatered WTR reuse in aquatic environments is generally lacking, however. In this study, we analyzed the eco-toxicity of leachates from sediments with or without dewatered WTRs toward algae Chlorella vulgaris via algal growth inhibition testing with algal cell density, chlorophyll content, malondialdehyde content, antioxidant enzyme superoxide dismutase activity, and subcellular structure indices. The results suggested that leachates from sediments unanimously inhibited algal growth, with or without the addition of different WTR doses (10% or 50% of the sediment in dry weight) at different pH values (8–9), as well as from sediments treated for different durations (10 or 180 days). The inhibition was primarily the result of P deficiency in the leachates owing to WTR P adsorption, however, our results suggest that the dewatered WTRs were considered as a favorable potential material for internal P loading control in lake restoration projects, as it shows acceptably low risk toward aquatic plants.Download high-res image (146KB)Download full-size image

•DWTR's solid particles promoted bacteria luminescence.•DWTR's aqueous/organic extracts had no toxic effect on bacteria.•DWTR reduced sediments' solid phase toxicity to bacteria luminescence.•DWTR addition had no effect on sediment's aqueous/organic extracts toxicity.Drinking water treatment residue (DWTR) seems to be very promising for controlling lake sediment pollution. Logically, acquisition of the potential toxicity of DWTR will be beneficial for its applications. In this study, the toxicity of DWTR and sediments amended with DWTR to Aliivibrio fischeri was evaluated based on the Microtox® solid and leachate phase assays, in combination with flow cytometry analyses and the kinetic luminescent bacteria test. The results showed that both solid particles and aqueous/organic extracts of DWTR exhibited no toxicity to the bacterial luminescence and growth. The solid particles of DWTR even promoted bacterial luminescence, possibly because DWTR particles could act as a microbial carrier and provide nutrients for bacteria growth. Bacterial toxicity (either luminescence or growth) was observed from the solid phase and aqueous/organic extracts of sediments with or without DWTR addition. Further analysis showed that the solid phase toxicity was determined to be related mainly to the fixation of bacteria to fine particles and/or organic matter, and all of the observed inhibition resulting from aqueous/organic extracts was identified as non-significant. Moreover, DWTR addition not only had no adverse effect on the aqueous/organic extract toxicity of the sediment but also reduced the solid phase toxicity of the sediment. Overall, in practical application, the solid particles, the water-soluble substances transferred to surface water or the organic substances in DWTR had no toxicity or any delayed effect on bacteria in lakes, and DWTR can therefore be considered as a non-hazardous material.Download high-res image (115KB)Download full-size image

Fe/Al drinking water treatment residuals (WTRs), ubiquitous and non-hazardous by-products of drinking water purification, are cost-effective adsorbents for glyphosate. Given that repeated glyphosate applications could significantly decrease glyphosate retention by soils and that the adsorbed glyphosate is potentially mobile, high sorption capacity and stability of glyphosate in agricultural soils are needed to prevent pollution of water by glyphosate. Therefore, we investigated the feasibility of reusing Fe/Al WTR as a soil amendment to enhance the retention capacity of glyphosate in two agricultural soils. The results of batch experiments showed that the Fe/Al WTR amendment significantly enhanced the glyphosate sorption capacity of both soils (p < 0.001). Up to 30% of the previously adsorbed glyphosate desorbed from the non-amended soils, and the Fe/Al WTR amendment effectively decreased the proportion of glyphosate desorbed. Fractionation analyses further demonstrated that glyphosate adsorbed to non-amended soils was primarily retained in the readily labile fraction (NaHCO3-glyphosate). The WTR amendment significantly increased the relative proportion of the moderately labile fraction (HCl-glyphosate) and concomitantly reduced that of the NaHCO3-glyphosate, hence reducing the potential for the release of soil-adsorbed glyphosate into the aqueous phase. Furthermore, Fe/Al WTR amendment minimized the inhibitory effect of increasing solution pH on glyphosate sorption by soils and mitigated the effects of increasing solution ionic strength. The present results indicate that Fe/Al WTR is suitable for use as a soil amendment to prevent glyphosate pollution of aquatic ecosystems by enhancing the glyphosate retention capacity in soils.Download full-size image

The characteristics of polycyclic aromatic hydrocarbons (PAHs) in water, suspended particulate matter (SPM), sediments, and hydrophytes from Lake Baiyangdian, a shallow freshwater lake in China were studied. The low-molecular-weight PAHs (2–3 ring PAHs) predominated (61.2 to 84.5%) in all samples. Principal component analysis (PCA) of individual PAHs and the ratios of selected PAHs showed that the PAHs in the lake were mainly petrogenic inputs. The solid-liquid distribution coefficient (Kd) in the water phase was much higher than the bioconcentration factor (BCF), and the leaf concentration factor (LCF) was higher than the root concentration factor (RCF) and stem concentration factor (SCF) in plant-sediment phase. Good linear log/log relationships were observed between the equilibrium partitioning coefficient (Koc) and the octanol–water partitioning coefficient (Kow), between RCF and Kow, and between LCF and the octanol–air partitioning coefficient (Koa). These results indicated that PAHs accumulated more easily in SPM than in submerged aquatic plants, and some low-molecular-weight PAHs could accumulate and be translocated in the lake's media. Media characteristics, contamination sources, and physicochemical properties all affect the partitioning of PAHs among water, SPM, sediments, and hydrophytes.