Photochemistry and environment. VII- The photohydrolysis of chlorobenzene: Studies of the excited state involved

Chlorobenzene excited in dilute aqueous solution is transformed quantitatively into phenol ($\text{ф= 0.10±0.02}$). This reaction involves a triplet state, since it is quenched by biacetyl and sensitized by ketones. Based on quenching experiments, the lifetime of the lowest triplet of chlorobenzene was measured as 30 ns. From the sensitized phosphorescence of biactyl, the quantum yield of intersystem crossing (S₁→T₁) was found to be 0.6 ±0.1. The photophysical characteristics of chlorobenzene are identical in acetonitrile (). Photosensitization of the photohydrolysis is observed with acetone and acetone D6 in aqueous solution. The quantum yield of the sensitized photohydrolysis is limited to 0.06±0.01. Hexadeuterated acetone appeared to be a more specific photosensitizer than acetone.     

Effects of carcinogens on the partition of cells in aqueous polymeric two-phase systems

Discrimination between malignant cells and their normal counterparts by surface properties has been demonstrated by means of two-phase aqueous polymer systems. Primary cultures of normal rat fibroblasts were treated with carcinogens DMBA and DEN. Nonmaliguant mouse fibroblasts of permanent line $\text{C}{}_3\text{HlOTl}\text{2}$ were treated with carcinogen DB(a,h)A. These treatments change their partition in the direction of their malignant counterparts. Noncarcinogenic phenanthrene affected the cell partition in the reverse direction. The possibility of using two-phase aqueous polymer systems for testing carcinogenic chemicals is discussed.     

Bioaccumulation of pentachlorophenol by killifish (Fundulussimilus)

Killifish ($\text{Fundulus}$$\text{similis}$) were exposed in the laboratory to pentachlorophenol (PCP) at concentrations of 57 to 610 μg PCP/L. Bioaccumulation reached a plateau value of about 53 by 168 hrs and remained at this level for at least 72 hrs. One-half the plateau value was reached in about 25 hrs. Following exposure, fish placed in PCP-free aquaria lost PCP rather slowly ($\text{t}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{～ 4.7}\text{days}$). The depuration data were suggestive of a pool of PCP which was lost more rapidly ($\text{t}{}_{\mathrm{<mtext>1</mtext><mtext>2</mtext>}}\text{～ 4.2}\text{hrs}$). The results of this study are compared to similar studies in other species. The bioaccumulation factors measured in this study agree relatively well with those in other marine species, but are lower than reported for fresh water species. Possible reasons for this difference are discussed.     

Sorption of atrazine and phenanthrene by organic matter fractions in soil and sediment

Atrazine and phenanthrene (Phen) sorption by nonhydrolyzable carbon (NHC), black carbon (BC), humic acid (HA) and whole sediment and soil samples was examined. Atrazine sorption isotherms were nearly linear. The single-point organic carbon (OC)-normalized distribution coefficients (K_OC) of atrazine for the isolated HA1, NHC1 and BC1 from sediment 1 (ST1) were 36, 550, and 1470 times greater than that of ST1, respectively, indicating the importance of sediment organic matter, particularly the condensed fractions (NHC and BC). Similar sorption capacity of atrazine and Phen by NHC but different isotherm nonlinearity indicated different sorption domains due to their different structure and hydrophobicity. The positive relationship between (O + N)/C ratios of NHC and atrazine log K_OC at low concentration suggests H-bonding interactions. This study shows that sediment is probably a less effective sorbent for atrazine than Phen, implying that atrazine applied in sediments or soils may be likely to leach into groundwater.