The present invention relates to a treatment system having a barium carbonate (BaCO.sub.3) dispersed alkaline substrate (BDAS) for use in the remediation or at least partial remediation of mine drainage (MD) and/or environmental media contaminated with a source of MD. The invention utilizes chemical, biological and combined treatment systems remove high concentrations of sulfates, hardness, heavy metals and N-compounds, that may exist in the MD as well as high concentrations of alkalinity produced during the remediation process. The invention further extends to a process for treating MD and/or environmental media contaminated with MD and to an apparatus for use in this process.

The present disclosure provides aromatic-cationic peptide compositions and methods of using the same. The methods comprise use of the peptides in electron transport and electrical conductance.

The present disclosure provides aromatic-cationic peptide compositions and methods of using the same. The methods comprise use of the peptides in electron transport and electrical conductance.

Chemically oxidizing a wide range of targeted contaminants in soils, sludges, groundwater, process water, and wastewater and assisting in the eventual (over time) biological attenuation of the contaminants utilizing persulfates activated by trivalent metals, such as ferric iron. The use of trivalent metal activated persulfate results in a chemical oxidation process that yields degradation compounds which facilitate further attenuation via biological processes.

The present disclosure discloses a method for preparing a labelled plant and a method for preparing a labelled biochar. The method for preparing a labelled plant includes the following steps: preparing a box; placing a plant that is capable of photosynthesis in the box; preparing a labelled gas in the box, the labelled gas being an isotope-labelled carbon dioxide gas; and leaving the box standing for a preset period of time, during which the plant absorbs the labelled gas to obtain a labelled plant. In the present disclosure, the carbon element in the plant is labelled during the growth of the plant, and the concentration of .sup.13CO.sub.2 in the box is controlled by controlling the concentration of Na.sub.2.sup.13CO.sub.3, where .sup.13CO.sub.2 is prepared by chemical methods, which could improve the utilization rate of .sup.13C.

Microbial reactors are provided for ammonium oxidation. Briefly, a reactor comprises a medium including an ammonium component and a Feammox bacterium and/or enzyme(s) thereof capable of oxidizing ammonium with electron transfer to an anode in contact with the medium. As described further herein, use of the anode as an electron acceptor can mitigate or overcome the disadvantages associated Fe(III) acceptor. In some embodiments, for example, ammonium oxidation in the reactor can proceed in the absence of Fe(III) and/or other metal compounds operable to function as an electron acceptor in the medium. Moreover, the medium may further comprise one more contaminants in addition to the ammonium component.

Microbial reactors are provided for ammonium oxidation. Briefly, a reactor comprises a medium including an ammonium component and a Feammox bacterium and/or enzyme(s) thereof capable of oxidizing ammonium with electron transfer to an anode in contact with the medium. As described further herein, use of the anode as an electron acceptor can mitigate or overcome the disadvantages associated Fe(III) acceptor. In some embodiments, for example, ammonium oxidation in the reactor can proceed in the absence of Fe(III) and/or other metal compounds operable to function as an electron acceptor in the medium. Moreover, the medium may further comprise one more contaminants in addition to the ammonium component.

Systems and methods for performing bioremediation using the Geobacillus sp. bacterial strain are provided which are capable of effectively degrading Benzo[a]pyrene (BaP) and efficiently degrading other ring-based organic contaminants. The exemplary bioremediation methods include steps for administering an effective, degrading amount of the bacteria to soil containing excess amounts of BaP and incubating the bacteria administered to the soil at a given temperature and for a duration that are suitable for promoting incubation and reducing and the concentration of BaP below a maximum concentration, as might be specified by a regulatory body.

Systems and methods for performing bioremediation using the Geobacillus sp. bacterial strain are provided which are capable of effectively degrading Benzo[a]pyrene (BaP) and efficiently degrading other ring-based organic contaminants. The exemplary bioremediation methods include steps for administering an effective, degrading amount of the bacteria to soil containing excess amounts of BaP and incubating the bacteria administered to the soil at a given temperature and for a duration that are suitable for promoting incubation and reducing and the concentration of BaP below a maximum concentration, as might be specified by a regulatory body.

A method for enhancing in situ bioremediation of a volume containing groundwater and a quantity of contaminant, the method comprising the steps of: quantifying the mass of the contaminant; and amending the volume by adding thereto a compound that provides a source of NO.sub.3.sup.−. The method is characterized in that the compound is added such that the mass of the NO.sub.3.sup.− source is provided at the ratio of about 1 mg NO.sub.3.sup.− per 0.21 mg contaminant. The contaminant can be BTEX or petroleum-related VOC.