Aquatic biota as potential biological indicators of the contamination,bioaccumulation and health risks caused by organochlorine pesticides in a large,shallow Chinese lake (Lake Chaohu)

Aquatic biota have long been recognized as bioindicators of the contamination caused by hydrophobic organic contaminants (HOCs) in aquatic environments. The primary purpose of the present study is to identify which species of aquatic biota are the most sensitive to organochlorine pesticides (OCPs) in Lake Chaohu and can therefore serve as indicators of the lake's health and assist in the assessment of OCPs risks to human health. OCP levels in eight species of aquatic biota were measured using GC–MS, and the relationships between the biota and OCP levels in the water and suspended solids were studied. DDTs pose potential human health risks and were the predominant OCP components found in the aquatic biota. DDT had the highest mean bioaccumulation factor (BAF) and biota suspended solids accumulation factor (BSSAF) of all of the studied OCP components. The food web magnification factors (FWMF) for p, p′-DDT were greater than 1, implying that biomagnification occurred. This finding indicates that DDTs still pose a serious threat to the ecosystem and human health in Lake Chaohu, even though the agricultural application of DDT powder has been officially banned since 1983. There were significant positive relationships between OCPs levels in Culter erythropterus and those in both water and suspended solids, as well as between OCPs levels in Protosalanx hyalocranius and those in suspended solids. This finding suggests that C. erythropterus and P. hyalocranius are the most sensitive aquatic biota to OCPs and may serve as the most effective bioindicators for monitoring OCP contamination in the water and suspended solids of Lake Chaohu. Megalobrama amblycephala, which contained the highest wet weight mean OCP concentration, is the most sensitive OCP indicator and can be used to assess the human carcinogenic risk of OCPs in Lake Chaohu.     

Phosphate biosorption characteristics of a submerged macrophyte Hydrilla verticillata

Phosphate biosorption of Hydrilla verticillata was investigated and compared with its bioaccumulation characteristics. Results obtained from the biosorption isotherms and kinetics showed that maximal phosphate biosorption was 286 mg kg⁻¹, approximately equal to 6–9% of the phosphate bioaccumulation. The biosorption mainly occurred within 5 h, and was highest during the first 30 min. The initial phosphate concentration was an important factor affecting the biosorption process. Phosphate biosorption on H. verticillata was not the main phosphate removal mechanism in our experiments, but it cannot be ignored.     

厦门海域两头中华白海豚体内铁的含量

铁是动物体的必需元素,是血红蛋白和肌红蛋白中氧的携带者。动物体内的含铁化合物主要为血红蛋白、肌红蛋白（Mb）、转铁蛋白、含铁血黄素和含铁酶（王夔,1992）。铁与水生哺乳动物的潜水能力密切相关。Wright和Davis（2006）对威德尔海豹（Leptonychotes weddellii）的研究表明,Mb是水生哺乳动物最重要的储氧部位,在胃肠吸收后状态下Mb从正常水平降低7％时,有氧潜水限度（Aerobic Dive Limit,ADL）下降39％;Mb增加两倍时,ADL则增加30％。     

Exocellular and intracellular accumulation of lead in Pseudomonas fluorescens ATCC 13525 is mediated by the phosphate content of the growth medium

Pseudomonas fluorescens appears to elicit disparate lead detoxification mechanisms in phosphate-rich and phosphate-deficient media. When grown in the presence of 0.1 mM Pb2+ complexed to citrate, the sole source of carbon, only a slight diminution in cellular yield was observed in the former medium. However, in a phosphate-deficient milieu, lead imposed approximately a 30% reduction in bacterial multiplication. At stationary phase of growth, 72% of the metal was found in the bacterial cells from the phosphate-deficient medium, while that from phosphate-rich broth contained only 12.5%. The latter medium was characterized by an insoluble pellet that accounted for 73.5% of the lead. Although no citrate was detected in the phosphate-rich media after 40 h of incubation, only 72% of citrate was consumed even after 70 h of growth in the phosphate-deficient cultures. The inclusion of lead did not appear to enhance the production of either extracellular proteins or carbohydrates.     

Uranium accumulation by a bacterium isolated from electroplating effluent

Pseudomonas MGF-48, a gram-negative, motile, oxidase-negative, catalase-positive, yellow-pigmented bacterium isolated from electroplating effluent, was found to accumulate uranium with high efficiency. Uptake of uranium was rapid and the amount increased in direct proportion to concentration, e.g., from 50 to 200 mg uranium per liter. The largest amount of uranium uptake was 174 mg per gram dry weight bacterial biomass and was observed to occur in stationary phase during incubation at 30 °C. Uptake was determined by flow injection analysis. Maximum uranium accumulation occurred at pH 6.5, with 86% of the uranium being taken up within 5 min of incubation. Release of uranium bound to the cells was accomplished by addition of sodium carbonate and EDTA solution (0.1 M), the cells were reusable, and served as a biosorbent. Cells immobilized in polyacrylamide gel took up 90% of the uranium. Pseudomonas MGF-48 showed excellent efficiency in biosorbing uranium, by both immobilized and free cells. The results of this study, compared with those of other reports of uranium accumulation by microorganisms, leads us to conclude that Pseudomonas MGF-48 shows excellent potential for bioremediating uranium-polluted aqueous effluents. This revised version was published online in July 2006 with corrections to the Cover Date.     

富硒螺旋藻培养技术研究

采用富硒技术对印项螺旋藻培养进行强化,对硒（IV）浓度和亚硫酸盐的影响,以及硒的生物富集及其对藻细胞分子官能团结构的影响等进行了较为详细的研究,并对相关的可能机理进行了讨论。研究发现,硒对印顶螺旋藻生长具有刺激或抑制的双重作用。在0.02mg/L-411.00mg/L浓度范围内,硒不仅可以加快印顶螺旋藻的生长,而且还可以提高其生物量;同时,钝顶螺旋藻对硒的事集随着硒浓度的增加而增加,较为缓慢的生长利于钝顶螺旋藻对硒的富集。研究还证实,NaSO3会减轻高浓度Na2SeO3对印顶螺旋藻生长的毒性,富硒培养不会对藻细胞分子官能团结构产生损害。实验得出钝顶螺旋藻富硒培养较佳的硒处理浓度在10mg／L－40mg／L。     

Seasonal variations and inherent variability of selenium in marine biota of a tropical wetland ecosystem: implications for bioindicator species

The present study was designed to study the seasonal variations of selenium in marine biota of different trophic levels collected from Sunderban deltaic complex, northeast India. The primary objective of this work is to provide baseline data for a future environmental quality programme. In general, the sequence of Se accumulation observed in biota is as follows: Bivalve>Zooplankton>Macroalgae>Pisces>Seagrass. An elevated level of Se was recorded during monsoon season. The Se level in zooplankton (4 μg/g) was three to four times higher than seagrass. The content of various soft tissues and shell in bivalves molluscs showed an organ-specific pattern in the following order: gill > visceral MASS = mantle > adductor muscle > podium > shell. Fish contain less Se in comparison with macroalgae, zooplankton and bivalves revealing poor or insignificant trophic transfer of Se in the marine food chain. Pelecyora trigona (Bivalve) seems to be reliable indicator of Se contamination because of its high accumulation capacity. An in-depth monitoring program is recommended in order to clarify the present trend and to establish the studied biota as indicator species.     

Bioaccumulation of copper(II), lead(II) and chromium(VI) by growing Aspergillus niger

The effect of copper(II), lead(II) and chromium(VI) ions on the growth and bioaccumulation properties of Aspergillus niger was investigated as a function of initial pH and initial metal ion concentration. The optimum pH values for growth and metal ion accumulation were determined as 5.0, 4.5 and 3.5 for copper(II), lead(II) and chromium(VI) ions, respectively. Although all metal ion concentrations caused an inhibition effect on the growth of A. niger, it was capable of removing of copper(II) and lead(II) with a maximum specific uptake capacity of 15.6 and 34.4 mg g⁻¹ at 100 mg dm⁻³ initial copper(II) and lead(II) concentration, respectively. Growth of A. niger was highly effected by chromium(VI) ions and inhibited by 75 mg dm⁻³ initial chromium(VI) concentration since some inhibition occurred at lower concentrations.     

Copper biosorption by Pseudomonas cepacia and other strains

Biosorption of copper by Pseudomonas cepacia was found to be dependent on added copper concentration. Copper uptake by the cells was rapid over the range of copper concentrations tested and complete within the first 10 min of incubation time. The effect of pH on copper uptake by P. cepacia was determined using overlapping buffers over the pH range 3–8, and copper biosorption from a 10 mM copper solution was greatest at pH 7. Copper uptake (measured by analysis of cell digests) was unaffected by cyanide and azide (up to 30 mM) and by incubation of cells with a 10 mM copper solution at 4 °C. Evidence from these results suggested that copper uptake by P. cepacia cells involves surface binding and not intracellular accumulation by active transport. Biosorption of copper by various Pseudomonas isolates from metal-contaminated environments agreed well with copper biosorption by Pseudomonas strains from the National Collection of Type Cultures (NCTC).     

Ecological restoration of arsenic contaminated soil by Arundo donax L

The possible arsenic tolerance mechanisms were explored in Arundo donax L. under various supplied arsenic concentrations. The treatments included control (no metal) and five doses of arsenic trioxide i.e., 0, 50, 100, 300, 600 and 1000 μg L⁻¹ As to A. donax. The phytoextraction ability of A. donax L. plants was assessed using both the translocation and bioaccumulation factors. The transpirates were collected to analyze the arsenic concentration volatilized along-with study of anatomical characteristics of the plant parts. In general, the arsenite and arsenate accumulation linearly increased in roots, shoot and leaves with the increasing supplied arsenic levels i.e., from 2.348, 2.775 and 3.25 μg g⁻¹ at 50 μg L⁻¹ to 50, 53.125 and 64.25 μg g⁻¹ arsenite, at 1000 μg L⁻¹, from 4.075, 5.425 and 13.56 μg g⁻¹ at 50 μg L⁻¹ to 71, 62.02 and 436.219 μg g⁻¹ arsenate at 1000 μg L⁻¹, respectively. The order of arsenic accumulation in A. donax L. was: solution As(III) < Root As(III) < Shoot As(III) < Leaf As(III) < Solution As(V) < Root As(V) < Shoot As(V) < Leaf As(V). The range of arsenic volatilization by A. donax L. was 7.2–22% at higher supplied arsenic (300–1000 μg L⁻¹). Volatilization was an important mechanism to avoid toxic effects of arsenic by A. donax L. in addition to bioaccumulation.