Use of15N/14N rations to evaluate the food source of the mysid,Neomysis intermedia Czerniawsky,in a eutrophic lake in Japan

The stable isotope ratios of nitrogen were measured in the mysid,Neomysis intermedia, together with various biogenic materials in a eutrophic lake, Lake Kasumigaura, in Japan throughout a year of 1984/85. The mysid, particulate organic matter (POM, mostly phytoplankton), and zooplankton showed a clear seasonal change in ¹⁵N with high values in spring and fall, but the surface bottom mud did not. A year to year variation as well as seasonal change in ¹⁵N was found in the mysid. The annual averages of ¹⁵N of each material collected in 1984/85 are as follows: surface bottom mud, 6.3 (range: 5.7–6.9); POM, 7.9 (5.8–11.8); large sized mysid, 11.6 (7.7–14.3); zooplankton, 12.5 (10.0–16.4); prawn, 13.2 (9.9–15.4); goby, 15.1 (13.8–16.7). The degree of¹⁵N enrichment by the mysid was determined as 3.2 by the laboratory rearing experiments. The apparent parallel relationship between the POM and the mysid in the temporal patterns of ¹⁵N with about 3 difference suggests the POM (mostly phytoplankton) as a possible food source ofN. intermedia in this lake through the year.     

Flow regime alters body size but not the use of aquatic subsidies in a riparian predatory arthropod

Alterations to river flow conditions have wide impacts on riparian organisms in terms of behavior and biomass. However, little is known about natural flood impacts on prey use and individual growth of riparian predators. Using stable carbon isotope analysis, we investigated flood impacts on aquatic-prey use and the size structure of an orb-web spider, Nephila clavata, during 3 years under different flood conditions in a black locust forest in the middle reaches of the Chikuma River. Large floods depressed aquatic-prey abundance, but did not affect terrestrial-prey abundance in the riparian forest. Consequently, spider growth was stunted after large floods. Spider body size was positively correlated with the body sizes of both aquatic and terrestrial insects in spider webs, where terrestrial insects were significantly larger than aquatic insects. The δ¹³C of aquatic insects was about 8‰ higher than that of terrestrial insects, and the δ¹³C of both insect groups did not vary significantly between months or among years. A negative relationship was found between body size and δ¹³C in spiders under different subsidies levels. Our results showed that flow regime altered spider growth through changes in aquatic subsidies level, but not aquatic-prey use by the spiders due to relative body sizes of predators and prey. Changes in relative body sizes of predator and prey may be an important factor in understanding nutrients, materials, and energy flows in aquatic and terrestrial linkages in the context of flow regime.     

Nitrogen stocks in a riparian area invaded by N-fixing black locust (Robinia pseudoacacia L.)

Fixation of river flow passages and riverbed degradation may facilitate the development of higher floodplains with the establishment of exotic species such as black locust (Robinia pseudoacacia L.). We quantitatively evaluated the relationship between nitrogen (N) levels in black locust trees and in sediments under different flood disturbance regimes in a riparian area of the Chikuma River. In this study, allometric equations were developed for relating leaf N content to diameter at breast height of black locust. The amount of leaf N in black locust increased with distance from the river, reaching 159 kg N ha⁻¹ at 180 m from the river. There was a small difference in N content between green and fallen leaves (0.2%), and so the leaf N was almost equivalent to N input to riparian sediments. Fine sediments accumulated on the riparian area, where the amount of sediments N increased with distance from the river, ranging from 1091 ± 767 to 4953 ± 2953 kg N ha⁻¹. The N accumulation rates also increased with distance from the river, corresponding with the amount of leaf N in black locust per unit area, but the former exceeded the latter. The sediment N accumulation might be accelerated by sediment trapping effect due to riparian vegetation itself. A large input of N provided by invaded black locust might alter nutrient dynamics and native plant community structure in the riparian area.     

Transport and release of chemicals from plastics to the environment and to wildlife

Plastics debris in the marine environment, including resin pellets, fragments and microscopic plastic fragments, contain organic contaminants, including polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons, petroleum hydrocarbons, organochlorine pesticides (2,2′-bis(p-chlorophenyl)-1,1,1-trichloroethane, hexachlorinated hexanes), polybrominated diphenylethers, alkylphenols and bisphenol A, at concentrations from sub ng g^–1 to µg g^–1. Some of these compounds are added during plastics manufacture, while others adsorb from the surrounding seawater. Concentrations of hydrophobic contaminants adsorbed on plastics showed distinct spatial variations reflecting global pollution patterns. Model calculations and experimental observations consistently show that polyethylene accumulates more organic contaminants than other plastics such as polypropylene and polyvinyl chloride. Both a mathematical model using equilibrium partitioning and experimental data have demonstrated the transfer of contaminants from plastic to organisms. A feeding experiment indicated that PCBs could transfer from contaminated plastics to streaked shearwater chicks. Plasticizers, other plastics additives and constitutional monomers also present potential threats in terrestrial environments because they can leach from waste disposal sites into groundwater and/or surface waters. Leaching and degradation of plasticizers and polymers are complex phenomena dependent on environmental conditions in the landfill and the chemical properties of each additive. Bisphenol A concentrations in leachates from municipal waste disposal sites in tropical Asia ranged from sub µg l^–1 to mg l^–1 and were correlated with the level of economic development.     

Establishment and characterization of tartrate-resistant acid phosphatase and alkaline phosphatase double positive cell lines

Morphologically macrophage-like cells were cloned from hamster bone marrow cells by coculturing bone marrow cells with hamster chondrocytes. One of the clones (CCP-2) was characterized in the present study. CCP-2 cells were positive in an osteoclast marker enzyme, tartrate-resistant acid phosphatase (TRAP), alkaline phosphatase (ALP) and non-specific esterase (NSE). We showed CCP-2 cells degraded cartilage matrix and hydroxyapatite coated on Osteologic disks. A gelatinase secreted from CCP-2 cells was observed and purified from serum-free conditioned medium of the cells. N-terminal amino acid sequencing of the purified enzyme revealed it was matrix metalloproteinase-9. However, CCP-2 cells failed to express calcitonin receptors, a mature osteoclast marker, even after coculture with osteoblast ST2 cells in the presence of 1alpha, 25-dihydroxyvitamin D3 [1alpha, 25-(OH)2D3]. The cells showed high affinity to types X and I but not to type II collagen. In addition, histochemical studies have shown the presence of tartrate-resistant acid phosphatase and alkaline phosphatase double positive cells at the secondary ossification site of the hamster humerus. From these observations, we concluded that CCP-2 cells are similar to osteoclast but not the same. CCP-2 cells are therefore important tools for investigating chondroclastogenesis/osteoclastogenesis and endochondral ossification.     

Distribution and fluxes of fluorescent whitening agents discharged from domestic wastewater into small rivers with seasonal changes of flow rates

Distributions of fluorescent whitening agents (FWAs) in the waters of a small river system in Japan were surveyed in summer when the water volume rose following high precipitation and in winter when it subsided as precipitation declined. The main source of FWAs in the river system was domestic wastewater, and fluxes in the tributaries depended on the size of the residential population and the elimination rates of sewage treatment systems in their catchments, although FWA concentrations in the river itself fluctuated, largely as a consequence of dilution by heavy precipitation and unstable water flows in the small-sized river system. The FWA concentrations in the river waterduring summer decreased not only by the dilution of river water but also by photodegradation because of more prolonged exposure to sunlight.