Enhanced Photodegradation of PNP on Soil Surface under UV Irradiation with TiO2

Photodegradation of p-nitrophenol (PNP) on soil surface was investigated to explore the photochemical remediation of soil polluted by nitrophenols. Soil samples spiked with PNP were irradiated by UV light with and without the addition of TiO ₂ . The addition of 0.5–2 wt% TiO ₂ enhanced PNP photodegradation with approximately 1.36 times increase in apparent rate of PNP disappearance. Soil moisture, humic acid and soil pH were important factors influencing the rate of PNP photodegradation. Increase in soil moisture improved the degradation significantly, whereas humic acid reduced the degradation rate. Changes in soil pH resulted in different degradation rates, and higher degradation efficiencies were observed under alkaline condition.     

Identification of vertebrate volatiles stimulating olfactory receptors on tarsus I of the tick Amblyomma variegatum Fabricius (Ixodidae)

Bovine odour excites olfactory receptor(s) in a wall-pore olfactory sensillum on the anterior pit of Haller's organ in Amblyomma variegatum. Gas chromatography-coupled electrophysiology recordings from this sensillum reveal the presence of 4 active compounds in bovine odour. The two strongest stimulants were identified as 2-nitrophenol and 4-methyl-2-nitrophenol by gas chromatography-coupled mass spectrometry, and by matching electrophysiological activity of synthetic analogues. Synthetic analogues of known vertebrate-associated volatiles also stimulate other olfactory receptors in sensilla on the surface of tarsus I: a lactone receptor responding to -valerolactone and 6-caprolactone; different fatty acid receptor types responding best to either pentanoic acid, 2-methylpropanoic acid or to butanoic acid; three receptors responding to NH₃; and one receptor responding to 3-pentanone. Gas chromatography-coupled mass spectrometry analysis of vertebrate volatiles revealed presence of a number of these olfactory stimulants in concentrates of rabbit and steer odour, i.e. 2-methylpropanoic acid, butanoic acid, 3-methylbutanoic acid, pentanoic acid, and -valerolactone.Abbreviations GC-EL gas chromatography-coupled electrophysiological recording - GC-MS gas chromatography-coupled mass spectrometry     

Influence of cobalt substitution on the activity of iron-type nitrile hydratase: are cobalt type nitrile hydratases regulated by carbon monoxide?

Comamonas testosteroni Ni1 nitrile hydratase is a Fe-type nitrile hydratase whose native and recombinant forms are identical. Here, the iron of Ni1 nitrile hydratase was replaced by cobalt using a chaperone based Escherichia coli expression system. Cobalt (CoNi1) and iron (FeNi1) enzymes share identical Vmax (30 nmol min(-1) mg(-1)) and Km (200 microM) toward their substrate and identical Ki values for the known competitive inhibitors of FeNi1. However, nitrophenols used as inhibitors do display a different inhibition pattern on both enzymes. Furthermore, CoNi1 and FeNi1 are also different in their sensitivity to nitric oxide and carbon monoxide, CO being selective of the cobalt enzyme. These differences are rationalized in relation to the nature of the catalytic metal center in the enzyme.     

Metabolism of compounds with nitro-functions by Klebsiella pnuemoniae isolated from a regional wetland

Metabolism of nitroaromatic compounds by a Klebsiella pneumoniae isolated from a regional wetland was studied. When it was grown with nitrophenol as the sole nitrogen source, the isolate had the metabolic capability of transforming nitrophenol to phenol; however, it did not use nitrophenol as the sole carbon source. The metabolic pathway showed that the K. pneumoniae reduced the nitro group to an amino group forming aminophenol as a major metabolite. This aminophenol was oxidatively deaminated to phenol. For every mole of nitrophenol metabolized, 1 mol of phenol was produced and the phenol did not undergo further metabolism. The isolate also used several other nitroaromatic compounds including nitrotoluenes and nitrobenzenes as its nitrogen source. Even though this organism did not degrade the nitroaromatics completely, it may be useful in degrading nitroaromatics in contaminated soil and water containing other aromatic degraders in a syntrophic condition in nature.     

Inductive and resonance effects of substituents adjust the microalgal biodegradation of toxical phenolic compounds

The type and the position of the substituent in the phenolic ring, the bond dissociation energy and the exogenously supplied carbon source as well as the inductive and resonance effect phenomena of the substituents adjust the biodegradability of the phenolic compounds. The comparative biodegradation study of mono-nitrophenols (electron acceptors) and mono-methylphenols (electron donors) revealed that it is a completely photoregulated process. The closer the donor group (OH(-)) of the phenolic ring is to the acceptor group (NO(2)(-)), the higher the biodegradation values are (2-nitrophenol>3-nitrophenol>4-nitrophenol); the further the donor group (OH(-)) of the phenolic compound is from the second donor group (CH(3)(+)), the higher the biodegradation values are (2-methylphenol<3-methylphenol<4-methylphenol). However, there are compounds without a specific role of acceptor or donor such as mono-iodophenols, where a type of counteraction between the inductive and resonance effect determines the behavior of the substituent. This fact combined with the presence of the hydroxyl group in the phenolic ring gave the observed stabilization in the biodegradation results of mono-iodophenols (2-iodophenol approximately 3-iodophenol approximately 4-iodophenol).