Molecular weight fractionation of dissolved organic matter in coastal seawater by ultrafiltration

Fractionation of molecular weight of dissolved organic matter (DOM) in coastal seawater of Tokyo Bay (Japan) was performed by ultrafiltration. Ultrafiltration membranes Diaflo UM-05, UM-10 and XM-100 were used for DOM fractionation, and dissolved organic carbon (DOC) was determined for ultrafiltrates of each membrane. In surface water of Station 1, near the center of Tokyo Bay, low-molecular weight DOM (molecular weight less than 500) which passed through a Diaflo UM-05 membrane was 0.3 to 2.6 mgC/l (24 to 42% of the total DOC) during August, 1971 to September, 1972. The macromolecular DOM (molecular weight greater than 100,000) retained on an XM-100 membrane, ranged from 0.1 to 1.0 mgC/l. These fractions accounted for 8 to 23% of the total DOC. The precision of the method was within ± 0.1 mgC/l, and therefore may be employed for coastal seawater of high DOC content.     

Pollution taxes and standards: A continuum of quasi-optimal solutions

A generalized second-best problem, involving a perfectly competitive industry which produces a pollution type of externality, is examined. The pollution tax is allowed to assume an arbitrary value (possibly zero), while a pollution standard, set as a ratio of pollution to output, is determined by a first-order optimizing condition. The general condition for a set of quasi-optimal solutions includes the Pareto-optimal solution as a special case. It is also found that when the pollution tax is below the optimal level, the usual implication is that the standard should be set so that the marginal cost of pollution reduction exceeds the marginal external damage.     

Atmospheric deposition of polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans, and dioxin-like polychlorinated biphenyls in the Kanto Region, Japan

The atmospheric bulk (dry and wet) deposition of dioxins was investigated at four locations (Tokyo, Yokohama, Tsukuba, and Tanzawa) in the Kanto region (in Japan) over one year using a stainless-steel pot. Annual average polychlorinated dibenzo-p-dioxins/polychlorinated dibenzofurans (PCDD/PCDF) deposition fluxes were estimated to be from 450 to 1300 ng/m2/yr, and the annual average TEQ fluxes from 5.7 to 17 ng-TEQ/m2/yr at the four locations. The PCDD/PCDF deposition flux was higher in winter than in summer. The deposition flux could be related to ambient temperature, particularly for less chlorinated PCDDs/PCDFs, while the deposition flux is not necessarily related to the amount of precipitation. The PCDD/PCDF deposition flux increased as the particle deposition flux increased, for the winter samples. Based on the ratio of the PCDD/PCDF deposition fluxes to the particle deposition fluxes, the contribution of the reentrainment of soil particles to the TEQ of PCDD/PCDF deposition was considered to be negligible in this region. Based on the air concentrations monitored near our deposition sampling points by the municipalities, the ratio of the annual deposition flux to the annual average air concentration was roughly estimated to be 0.082 cm/s. The range of deposition flux in the Kanto region was estimated to be from 1.5 to 31 (median: 9.8) ng-TEQ/m2/yr based on the range of air concentration data measured by the municipalities. The total annual deposition flux in the entire Kanto region was estimated to range from 50 to 900 g-TEQ/yr (median 320 g-TEQ/yr). This estimated flux was of the same order as the sum of estimated emissions from municipal solid waste incinerators and industrial waste incinerators in the Kanto region. The contributions of dioxin-like PCBs in Yokohama, Tsukuba, and Tanzawa depositions were less than 10% of the total TEQ; however, in Tokyo it was almost equal to or more than 50%.     

Acute toxicity of disinfection by-products from chlorination of algal organic matter to the cladocerans Ceriodaphnia silvestrii and Daphnia similis: influence of bromide and quenching agent

Environmental Science and Pollution Research - Algal organic matter (AOM) in water reservoirs is a worldwide concern for drinking water treatment; once it is one of the main precursors for...     

Rate and extent of decomposition of dissolved organic matter in surface seawater

An experiment on the decomposition of the dissolved organic matter (DOM) in surface seawater was carried out under controlled laboratory conditions during a cruise of the R.V. Hakuho-Maru in the North-Equatorial Pacific (August/November, 1969). Surface seawater was placed in 300 ml oxygen bottles and incubated in the dark at 25°C. After selected time intervals, the dissolved organic-carbon (DOC) and the dissolved oxygen (DO) were determined for each bottle. The DOM in the surface seawater was described in terms of two labile fractions and a refractory one. The DOC decreased from 0.96 to 0.74 mgC/l during the first 50 days of incubation. Approximately 20% of the initial DOC (Fraction F_I) was oxidized. The other labile fraction, F_II was assumed to be 30 to 40% of the total DOM. The remaining half of the total DOM (Fraction F_III) is probably refractory and resistant to biochemical oxidation. The rate constant for decomposition was 0.0052 day^–1 for the total DOM and 0.033 day^–1 for F _I.     

氟里昂12和氯仿在德瓦达合金上的氢分解

在碱性水溶液中的德瓦达合金上,氟里昂12和氯仿由于发生了氢分解,而转化成甲烷、乙烷、丙烷等生成物,氟里昂12的转化率为3.5％,甲烷和乙烷的生成活化能分别是5.4kJ/mol和4.23kJ/mol,氯仿的转化率为8.1％,甲烷生成的选择率在80％以上,氯仿的氢分解反应是基于兰格缪尔(Langmuir)吸附模型,通过求解而确定出了反应的吸附平衡常数k_o和速度常数k_r分别为2.72 1.mol~(-1)和8.55x10~(-6)umol.min~(-1)。     

Further studies on decomposition of dissolved organic matter in coastal seawater

Experiments were made on decomposition of dissolved organic matter (DOM) in coastal seawater (Sagami Bay and Tokyo Bay, Japan). Decomposition of DOM seems to proceed in two steps: a rapid decrease in DOM during the first several days, followed by a slow decrease after this time. The apparent rate constant for decomposition of the total DOM was calculated as 0.01 to 0.09 day^-1 for the first step and 0.001 to 0.009 day^-1 for the second step, assuming that such decomposition proceeds as a first-order reaction. A part of such utilizable fractions of DOM may be derived from excretion and decomposition products of phytoplankton, especially “red-tide” organisms occurring in summer. Molecular weight distribution of DOM changed with advancing decomposition. The low-molecular-weight DOM (mainly less than 500) in the surface water of Tokyo Bay was 0.67 mgC/l (24% of the total DOM) at the initiation of incubation; this decreased to 0.36 mgC/l (16% of the total DOM) after 2 days incubation at 20°C in the dark. Low-molecular-weight DOM was thought to be firstly utilized by micro-organisms. After 6 to 10 months incubation, the proportion of low-molecular-weight DOM decreased and that of high-molecular-weight DOM increased.     

Congener-specific characterization of PCDDs/PCDFs in atmospheric deposition: comparison of profiles among deposition, source, and environmental sink

In order to examine the input of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDDs/PCDFs) from various airborne sources to environmental sinks, the atmospheric deposition of congener-specific PCDDs/PCDFs was investigated. Homologue and congener profiles of atmospheric depositions were compared with those of sources and environmental sinks to identify the relationship among atmospheric depositions, sources, and environmental sinks. Moreover, factor analysis was used to detect similarities, differences, and relationships of the variations in deposition fluxes among congeners within the same and different homologues. The results showed that the congener profiles of the atmospheric depositions were primarily determined by those of combustion emissions. Several congeners in some specific samples showed higher proportions within each homologue compared with representative depositions. This result can be partly explained by the influence of impurities in herbicides, 1,3,5-trichloro-2-(4-nitrophenoxy) benzene (CNP) and pentachlorophenol (PCP). The congener profiles of combustion emissions, representative depositions, and urban soils were very similar although their homologue profiles varied. This implied that PCDDs/PCDFs in the urban soils originate from the deposition of combustion emissions and that all congeners within each homologue behave identically in air and soil. Although the congener profiles of the representative depositions were different from those of the sediments in Tokyo Bay and the soil of a paddy field, the combination of congener profiles of the representative depositions and of the impurities in herbicides. CNP and PCP, can explain the congener profiles of the sediments and the paddy field. This study showed that congener-specific data are useful for source identification.