Effects of copper on growth, reproduction, survival and haemoglobin in Daphnia magna

The effects of additions of CuSO4 X 5H2O to final concentrations between 0.0004 and 105 micrograms Cu l-1 on growth, reproduction, survival and haemoglobin content of Daphnia magna were studied in hard reconstituted water and compared to the response in the dilution water without addition of copper. Concentrations of copper are nominal values. The 48-hr EC50 (immobilization) for unfed neonates was 6.5 micrograms Cu l-1 and the 48-hr and 21-day LC50 for fed neonates were 18.5 and 1.4 microgram Cu l-1, respectively. Growth expressed as body length of juveniles after 7 days and adult females after 21 days was only reduced in survivors at the highest non-lethal concentration (6.6 micrograms Cu l-1). Reproduction was stimulated by low concentrations of copper. Optimal reproduction after 21 days was found between 0.001 and 0.1 microgram Cu l-1. Higher concentrations were partially inhibitory (0.4 microgram Cu l-1), stimulatory (0.8 and 1.6 microgram Cu l-1) or completely inhibitory (3.2 micrograms Cu l-1 and above). The stimulatory peak around 1 microgram Cu l-1 was accompanied by a reduced survival (above 0.4 microgram Cu l-1). The Zero Equivalent Point (ZEP) for reproduction at non-reduced survival was 0.23 microgram Cu l-1. This concentration should be "safe" for D. magna under prevailing conditions (reconstituted water with a hardness of 250 mg l-1 as CaCo3 and a synthetic diet based on fish food and baby gruel). The haemoglobin content was affected by copper in a complex pattern which was not related to growth, reproduction or survival.     

Derivation of a toxicity-based model to predict how water chemistry influences silver toxicity to invertebrates

The effect of altering water chemistry on acute silver toxicity to three invertebrate species, two Daphnids, Daphnia magna and Daphnia pulex, as well as an amphipod Gammarus pulex was assessed. In addition, the physiological basis of Ag(I) toxicity to G. pulex was examined. Daphnia magna and D. pulex were more sensitive than G. pulex and 48 h LC(50) values in synthetic ion poor water were 0.47, 0.65 and 2.1 microg Ag(I) l(-1), respectively. Increasing water [Cl(-)] reduced Ag(I) toxicity in all species, and increasing water [Ca(2+)] from 50 to 1,500 microM reduced Ag(I) toxicity in G. pulex. Whole body Na(+) content, but not K(+) or Ca(2+) was significantly reduced in G. pulex exposed to 6 microg Ag(I) l(-1) for 24 h, but there was no inhibition of whole body Na(+)/K(+)-ATPase activity. Both increasing water [Cl(-)] and [Ca(2+)] reduced this Ag(I)-induced Na(+) loss. For D. magna, the presence of 10 mg l(-1) humic acid or 0.5 microM 3-mercaptoproprionic acid (3-MPA) increased the 48 h LC(50) values by 5.9 and 58.5-fold, respectively, and for D. pulex the presence of 1 microM thiosulfate increased the 48 h LC(50) value by four-fold. The D. magna toxicity data generated from this study were used to derive a Daphnia biotic ligand model (BLM). Analysis of the measured LC(50) values vs. the predicted LC(50) values for toxicity data from the present and published results where water Cl(-), Ca(2+), Na(+) or humic acid were varied showed that 91% of the measured toxicity data fell within a factor of two of the predicted LC(50) values. However, the daphnid BLM could not accurately predict G. pulex toxicity. Additionally, the Daphnia BLM was under-protective in the presence of the organic thiols 3-MPA or thiosulphate and predicted an increase in the LC(50) value of 114- and 74-fold, respectively. The Daphnia toxicity based BLM derived from the present data set is successful in predicting Daphnia toxicity in laboratory data sets in the absence of sulfur containing compounds, but shows its limitations when applied to waters containing organic thiols or thiosulphate.     

Mixture toxicity of copper and zinc to barley at low level effects can be described by the Biotic Ligand Model

Background and aims

The biotic ligand model (BLM) is a bioavailability model for metals based on the concept that toxicity depends on the concentration of metal bound to a biological binding site; the biotic ligand. Here, we evaluated the BLM to interpret and explain mixture toxicity of metals (Cu and Zn).

Methods

The mixture toxicity of Cu and Zn to barley (Hordeum vulgare L.) was tested with a 4 days root elongation test in resin buffered nutrient solutions. Toxicity of one toxicant was tested in presence or absence of a low effect level of the other toxicant or in a ray design with constant toxicant ratios. All treatments ran at three different Ca concentrations (0.3, 2.2 and 10?mM) to reveal ion interaction effects.

Results

The 50 % effect level (EC50) of one metal, expressed as the free ion in solution, significantly (p?<?0.05) increased by adding a low level effect of the other metal at low Ca. Such antagonistic interactions were smaller or became insignificant at higher Ca levels. The Cu EC10 was unaffected by Zn whereas the Zn EC10 increased by Cu at low Ca. These effects obeyed the BLM combined with the independent action model for toxicants.

Conclusions

The BLM model explains the observed interactions by accounting for competition between both metals free ions and Ca²⁺ at the Cu and Zn biotic ligands. The implications of these findings for Cu/Zn interactions in soil are discussed.     

Cell membrane surface potential (psi0) plays a dominant role in the phytotoxicity of copper and arsenate

Negative charges at cell membrane surfaces (CMS) create a surface electrical potential (psi(0)) that affects ion concentrations at the CMS and consequently affects the phytotoxicity of metallic cations and metalloid anions in different ways. The zeta potentials of root protoplasts of wheat (Triticum aestivum), as affected by the ionic environment of the solution, were measured and compared with the values of psi(0) calculated with a Gouy-Chapman-Stern model. The mechanisms for the effects of cations (H(+), Ca(2+), Mg(2+), Na(+), and K(+)) on the acute toxicity of Cu(2+) and As(V) to wheat were studied in terms of psi(0). The order of effectiveness of the ions in reducing the negativity of psi(0) was H(+) > Ca(2+) approximately Mg(2+) > Na(+) approximately K(+). The calculated values of psi(0) were proportional to the measured zeta potentials (r(2) = 0.93). Increasing Ca(2+) or Mg(2+) activities in bulk-phase media resulted in decreased CMS activities of Cu(2+) ({Cu(2+)}(0)) and increased CMS activities of As(V) ({As(V)}(0)). The 48-h EA50{Cu(2+)}(b) ({Cu(2+)} in bulk-phase media accounting for 50% inhibition of root elongation over 48 h) increased initially and then declined, whereas the 48-h EA50{As(V)}(b) decreased linearly. However, the intrinsic toxicity of Cu(2+) (toxicity expressed in terms of {Cu(2+)}(0)) appeared to be enhanced as psi(0) became less negative and the intrinsic toxicity of As(V) appeared to be reduced. The psi(0) effects, rather than site-specific competitions among ions at the CMS (invoked by the biotic ligand model), may play the dominant role in the phytotoxicities of Cu(2+) and As(V) to wheat.     

Application of the biotic ligand model to predicting zinc toxicity to rainbow trout,fathead minnow,and Daphnia magna

The Biotic Ligand Model has been previously developed to explain and predict the effects of water chemistry on the toxicity of copper, silver, and cadmium. In this paper, we describe the development and application of a biotic ligand model for zinc (Zn BLM). The data used in the development of the Zn BLM includes acute zinc LC50 data for several aquatic organisms including rainbow trout, fathead minnow, and Daphnia magna. Important chemical effects were observed that influenced the measured zinc toxicity for these organisms including the effects of hardness and pH. A significant amount of the historical toxicity data for zinc includes concentrations that exceeded zinc solubility. These data exhibited very different responses to chemical adjustment than data that were within solubility limits. Toxicity data that were within solubility limits showed evidence of both zinc complexation, and zinc-proton competition and could be well described by a chemical equilibrium approach such as that used by the Zn BLM.     

叔丁基对羟基茴香醚和诺氟沙星对水生生物的影响

采用急性毒性试验的方法,研究了叔丁基对羟基茴香醚(Butylated hydroxyanisole,BHA)和诺氟沙星(Norfloxacin,NFLX)对水生生物斜生栅藻和大型溞的毒性效应。结果表明大型溞在BHA和NFLX暴露下48h的LC₅₀分别为3.15mg·L^-1和194.98mg·L^-1。BHA和NFLX对斜生栅藻也有明显的毒性作用,其96h的EC₅₀分别为6.19mg·L^-1和50.18mg·L^-1。大型蚤对BHA暴露的敏感性强于斜生栅藻,而斜生栅藻对NFLX的敏感性比大型溞强。根据化学物质对鱼类和溞类的毒性评价标准,BHA和NFLX分别属于中等和低等毒性的化合物。     

A new model for predicting time course toxicity of heavy metals based on Biotic Ligand Model (BLM)

A new model for predicting time course toxicity of heavy metals was developed by extending the effective ratio of biotic ligand binding with toxic heavy metals to the total biotic ligand for 50% of test organisms (f₅₀) derived by the Biotic Ligand Model (BLM). BLM has been well-known as a useful model for prediction of heavy metal toxicity. BLM can consider the effect of exposure conditions such as pH and Ca²⁺ on heavy metal toxicity. In addition to the exposure conditions, heavy metal toxicity is strongly dependent on exposure time. In this study, BLM is extended to predict time dependency of heavy metal toxicity by connecting with the concept of primary reaction. The model developed in this study also generates the estimation of the 50% effect concentration (EC₅₀) for toxicologically unknown organisms and heavy metals. Two toxicological and kinetic constants, f_50,0 and k, were derived from the initial value of f₅₀ (f_50,0) and a time constant (k) independent of time. The model developed in this study enables us to acquire information on the toxicity of heavy metals such as Cu, Cd and Co easily.     

Biological surface coating and molting inhibition as mechanisms of TiO2 nanoparticle toxicity in Daphnia magna

The production and use of nanoparticles (NP) has steadily increased within the last decade; however, knowledge about risks of NP to human health and ecosystems is still scarce. Common knowledge concerning NP effects on freshwater organisms is largely limited to standard short-term (≤48 h) toxicity tests, which lack both NP fate characterization and an understanding of the mechanisms underlying toxicity. Employing slightly longer exposure times (72 to 96 h), we found that suspensions of nanosized (～100 nm initial mean diameter) titanium dioxide (nTiO(2)) led to toxicity in Daphnia magna at nominal concentrations of 3.8 (72-h EC(50)) and 0.73 mg/L (96-h EC(50)). However, nTiO(2) disappeared quickly from the ISO-medium water phase, resulting in toxicity levels as low as 0.24 mg/L (96-h EC(50)) based on measured concentrations. Moreover, we showed that nTiO(2) (～100 nm) is significantly more toxic than non-nanosized TiO(2) (～200 nm) prepared from the same stock suspension. Most importantly, we hypothesized a mechanistic chain of events for nTiO(2) toxicity in D. magna that involves the coating of the organism surface with nTiO(2) combined with a molting disruption. Neonate D. magna (≤6 h) exposed to 2 mg/L nTiO(2) exhibited a "biological surface coating" that disappeared within 36 h, during which the first molting was successfully managed by 100% of the exposed organisms. Continued exposure up to 96 h led to a renewed formation of the surface coating and significantly reduced the molting rate to 10%, resulting in 90% mortality. Because coating of aquatic organisms by manmade NP might be ubiquitous in nature, this form of physical NP toxicity might result in widespread negative impacts on environmental health.     

Development of an electrostatic model predicting copper toxicity to plants

The focus of the present study was to investigate the mechanisms for the alleviation of Cu toxicity in plants by coexistent cations (e.g. Al(3+), Mn(2+), Ca(2+), Mg(2+), H(+), Na(+), and K(+)) and the development of an electrostatic model to predict 50% effect activities (EA50s) accurately. The alleviation of Cu(2+) toxicity was evaluated in several plants in terms of (i) the electrical potential at the outer surface of the plasma membrane (PM) (Ψ(0)(°)) and (ii) competition between cations for sites at the PM involved in the uptake or toxicity of Cu(2+), the latter of which is invoked by the Biotic Ligand Model (BLM) as the sole explanation for the alleviation of toxicity. The addition of coexistent cations into the bulk-phase medium reduces the negativity of Ψ(0)(°) and hence decreases the activity of Cu(2+) at the PM surface. Our analyses suggest that the alleviation of toxicity results primarily from electrostatic effects (i.e. changes in both the Cu(2+) activity at the PM surface and the electrical driving force across the PM), and that BLM-type competitive effects may be of lesser importance in plants. Although this does not exclude the possibility of competition, the data highlight the importance of electrostatic effects. An electrostatic model was developed to predict Cu(2+) toxicity thresholds (EA50s), and the quality of its predictive capacity suggests its potential utility in risk assessment of copper in natural waters and soils.     

Acclimation of Daphnia magna to environmentally realistic copper concentrations

It may be hypothesised that as the bioavailable background concentration of an essential metal increases (within natural limits), the natural tolerance (to the metal) of the acclimated/adapted organisms and communities will increase. In this study the influence of acclimation to different copper concentrations on the sensitivity of the freshwater cladoceran Daphnia magna Straus was investigated. D. magna was acclimated over three generations to environmentally relevant copper concentrations ranging from 0.5 to 100 microg Cu/l (copper activity: 7.18 x 10(-15) to 3700 x 10(-12) M Cu2+). A modified standard test medium was used as culture and test medium. Medium modifications were: reduced hardness (lowered to 180 mg CaCO3/l) and addition of Aldrich humic acid at a concentration of 5 mg DOC/l (instead of EDTA). The effects of acclimation on these organisms were monitored using acute mortality assays and long-term assays in which life table parameters, copper body concentrations and energy reserves were used as test endpoints. Our results showed a two-fold increase in acute copper tolerance with increasing acclimation concentration for second and third generation organisms. Copper acclimation concentrations up to 35 microg Cu/l (80 pM Cu2+) did not affect the net reproduction and the intrinsic growth rate. The energy reserves of the acclimated daphnids revealed an Optimal Concentration range (OCEE) and concentrations between 5 and 12 microg Cu/l (0.5-4.1 pM Cu2+) and 1 and 35 microg Cu/l (0.023-80 pM Cu2+) seemed to be optimal for first and third generation daphnids, respectively. Lower and higher copper concentrations resulted in deficiency and toxicity responses. It was also demonstrated that up to 35 microg Cu/l, third generation daphnids were able to regulate their total copper body concentration. These results clearly indicate that bioavailable background copper concentrations present in culture media have to be considered in the evaluation of toxicity test results, especially when the toxicity data are used for water quality guideline derivation and/or ecological risk assessment for metals.     

The biotic ligand model and a cellular approach to class B metal aquatic toxicity

The biotic ligand model (BLM) and a cellular molecular mechanism approach represent two approaches to the correlation of metal speciation with observed toxicity to aquatic organisms. The two approaches are examined in some detail with particular reference to class B, or soft metals. Kinetic arguments are presented to suggest situations that can arise where the BLM criterion of equilibrium between all metal species in the bulk solution and the biotic ligand may not be satisfied and what might the consequences be to BLM predictive capability. Molecular mechanisms of toxicity are discussed in terms of how a class B metal might enter a cell, how it is distributed in a cell, and how the cell might respond to the unwanted metal. Specific examples are given for copper as an organism trace essential metal, which is toxic in excess, and for silver, a non-essential metal. As class B metals all bind strongly to sulfur, regulation of these metals requires that all S(II-) species be accounted for in aquatic systems, even under oxic conditions.     

Application of saccharose as copper(II) ligand for electroless copper plating solutions

Saccharose, forming sufficiently stable complexes with copper(II) ions in alkaline solutions, was found to be a suitable ligand for copper(II) chelating in alkaline (pH>12) electroless copper deposition solutions. Reduction of copper(II)-saccharose complexes by hydrated formaldehyde was investigated and the copper deposits formed were characterized. The thickness of the compact copper coatings obtained under optimal operating conditions in 1h reaches ca. 2 microm at ambient temperature. The plating solutions were stable and no signs of Cu(II) reduction in the bulk solution were observed. Results were compared with those systems operating with other copper(II) ligands.     

Occurrence of Cu-ATPase in Dictyostelium: possible role in resistance to copper

Dictyostelium discoideum amoebae showed an uncommon resistance to Cu(2+), as pointed out through cell growth rate (EC(50) = 469 +/- 30 microM) and the neutral red cytotoxicity assay (EC(50) = 334 +/- 45 microM). Although no evidence of Cu-inducible metallothionein was found, Cu-dependent ATPase activity was cytochemically detected on pelletted, resin-embedded amoebae. This activity required Cu(2+) in the incubation medium, was sensitive to TPEN, vanadate and temperature, and showed dose-dependent increase after exposure of amoebae to 10-500 microM Cu(2+) for 7 days. Accordingly, immunofluorescence and Western blotting revealed the occurrence of a Cu-inducible, putative homologue of human Menkes (MNK) Cu-P-type ATPase. To verify if Cu-ATPase is involved in copper resistance, amoebae were exposed to low concentrations of Cu(2+) and vanadate followed by the neutral red assay. Exposure to either treatment showed no effect, while a combination caused a dramatic increase of Cu toxicity, possibly depending on Cu-ATPase inhibition.     

3种微生态制剂对大型溞存活、生殖和种群增长的影响

研究了3种微生态制剂(复合微生态制剂Ⅰ、复合微生态制剂Ⅱ和芽孢杆菌)对大型溞的急、慢性毒性影响,分析比较了3种微生态制剂的安全使用剂量以及对大型溞生殖和种群增长的影响.试验结果表明,3种微生态制剂对大型溞死亡率影响均显著(P < 0.05),从安全浓度来看,对大型溞的毒性作用依次为:复合微生态制剂Ⅱ>复合微生态制剂Ⅰ>芽孢杆菌;在安全浓度范围内,3种微生态制剂对大型溞亲代(P)的生殖和种群增长均有明显的促进作用,表现在随微生态制剂浓度的升高,P代的净生殖率(R0)和内禀增长率(rm)均显著增加(P < 0.05),其中以复合微生态制剂Ⅰ的效果最好,R0最高值为对照组的7倍,rm最高值为对照组的1.7倍;3种微生态制剂对大型溞子一代(F1)和子二代(F2)的生殖和种群增长均没有促进作用.     

Copper inclusion in cellulose using sodium d-gluconate complexes

Copper containing cellulose material is of growing interest, e.g. offering alternative in the field of antimicrobials. Solutions of copper d-gluconate complexes (Cu(2+)-DGL) were used to introduce copper ions into a swollen cellulosic matrix. A ligand exchange mechanism forms the chemical basis of the sorption process. Copper sorption in cellulose was studied in the range between pH 6 and 13. An estimate for the complex stabilities of the Cu-cellulose system could be derived from the calculated species distribution of the different Cu(2+)-DGL complexes present. Spectrophotometry and cyclic voltammetry of Cu(2+)-DGL complex solution were used to confirm the presence of different species participating in the ligand exchange reaction. The pH dependent uptake of Cu(2+) ions in the cellulose matrix can be explained on the basis of the relative stabilities of Cu(2+)-DGL complex vs. Cu(2+)-cellulose complexes. In comparison to pH 10, higher copper content was observed at pH 6 and 13. Copper content was limited by carboxyl content of cellulosic materials, thus in analogy to the structure of Cu(2+)-DGL complexes participation of the carboxyl group as complex forming site is proposed. At high Cu(2+)-concentration and longer time of immersion in the copper complex solutions formation of solid deposits was observed on the surface of the treated fibres.     

Biotic ligand model development predicting Zn toxicity to the alga Pseudokirchneriella subcapitata: possibilities and limitations

Biotic ligand models have been developed for various metals (e.g. Cu, Ag, Zn) and different aquatic species. These models incorporate the effect of physico-chemical water characteristics (major cations, pH, dissolved organic carbon) on the bioavailability and toxicity of the metal. In this study, the individual effects of calcium, magnesium, potassium, sodium and pH on zinc toxicity to the green alga Pseudokirchneriella subcapitata (formerly and better known as Selenastrum capricornutum and Raphidocelis subcapitata) were investigated. Stability constants for binding to algal cells (K(BL)) were derived for those cations affecting zinc toxicity, using the mathematical approach proposed by De Schamphelaere and Janssen [Environ. Sci. Technol. 63, (2002) 48-54]. Potassium proved to be the only cation tested that did not alter zinc toxicity to algae significantly. Log (K(BL)) values for Ca, Mg and Na, derived at pH 7.5, were 3.2, 3.9 and 2.8, respectively. Toxicity tests performed at different pH values (5.5-8.0) indicated that competition between H(+) and Zn(2+) reduces zinc toxicity. However, the observed relationship between (H(+)) and the 72h-EbC(50) [expressed as microM (Zn(2+))] is not linear and suggests that pH affects the physiology of the biotic ligand. Although, in general, our findings seem to suggest that zinc toxicity to algae can be modelled as a function of key water characteristics, the results also demonstrate that the part of the conventional BLM-hypothesis-i.e. that the binding characteristics of the biotic ligand are independent of the test medium characteristics-is not valid for algae. The observed pH-dependent change of stability constants should therefore be further investigated and incorporated in future BL-modelling efforts with algae.     

Radiotracer Studies on Waterborne Copper Uptake,Distribution, and Toxicity in Rainbow Trout and Yellow Perch: A Comparative Analysis

Rainbow trout (Oncorhynchus mykiss) are often used to estimate important biotic ligand model (BLM) parameters, such as metal-binding affinity (log K) and capacity (B_max). However, rainbow trout do not typically occupy metal-contaminated environments, whereas yellow perch (Perca flavescens) are ubiquitous throughout most of North America. This study demonstrates that dynamic processes that regulate Cu uptake at the gill differ between rainbow trout and yellow perch. Rainbow trout were more sensitive to acute aqueous Cu than yellow perch, and toxicity was exacerbated in soft water relative to similar exposures in hard water. Whole body Na loss rate could account for acute Cu toxicity in both species, as opposed to new Cu uptake rate that was not as predictive. Time course experiments using radiolabelled Cu (⁶⁴Cu) revealed that branchial Cu uptake was rather variable within the first 12 h of exposure, and appeared to be a function of Cu concentration, water hardness, and fish species. After 12 h, new branchial Cu concentrations stabilized in both species, suggesting that metal exposures used to estimate BLM parameters should be increased in duration from 3 h to 12+ h. In rainbow trout, 71% of the new Cu bound to the gill was exchangeable (i.e., able to either enter the fish or be released back to the water), as opposed to only 48% in yellow perch. This suggests that at equal exposure concentrations, proportionally more branchial Cu can be taken up by rainbow trout than yellow perch, which can then go on to confer toxicity. These qualitative differences in branchial Cu handling between the two species emphasize the need to develop BLM parameters for each species of interest, rather than the current practice of extrapolating BLM results derived from rainbow trout (or other laboratory-reared species) to other species. Data reported here indicate that a one-size-fits-all approach to predictive modeling, mostly based on rainbow trout studies, may not suffice for making predictions about metal toxicity to yellow perch—that is, a species that inhabits metal-contaminated lakes around northern Canadian industrial operations.     

The toxicity and physiological effects of copper on the freshwater pulmonate snail, Lymnaea stagnalis

Several recent studies have demonstrated that the freshwater pulmonate snail Lymnaea stagnalis is extremely sensitive to metals (Co, Ni, Pb) in chronic exposures. The objective of the current study was to evaluate the acute and chronic sensitivity of L. stagnalis to Cu and investigate the underlying mechanism(s) of toxic action. A 96-h LC50 of 31μg L(-1) Cu was estimated indicating L. stagnalis was moderately acutely sensitive to Cu relative to other aquatic organisms. However, in a 30-day chronic exposure using juvenile snails an EC20 of 1.8μg L(-1) Cu was estimated for snail growth making L. stagnalis the most sensitive organism tested to date for Cu. Hardness-based and BLM-based water quality criteria for Cu at the water quality conditions used in this study were 7.8 and 1.5μg L(-1), respectively, indicating L. stagnalis is significantly under-protected by hardness-based WQC. Investigations into the mechanism(s) of toxic action for Cu were conducted on young adult snails necessitating higher Cu exposures. Exposure to Cu at 12μg L(-1) resulted in no detectable effects on hemolymph osmolality, net Ca(2+) uptake, titratable acid excretion, or ammonia excretion. Exposure to 48μg L(-1) Cu was shown to significantly reduce (91%) net Ca(2+) uptake which is strongly correlated with shell deposition and corresponding snail growth. Snails exposed to 48μg L(-1) Cu also exhibited reduced ammonia excretion, a marked hemolymph acidosis, and a compensatory increase in titratable acid excretion. The reduction in net Ca(2+) uptake was hypothesized to be a secondary effect of Cu-induced inhibition of carbonic anhydrase, but no reduction in carbonic anhydrase activity was detected. Overall, it remains unclear whether inhibition of Ca(2+) uptake is a direct result of Cu exposure or, along with the other observed physiological effects, is secondary to an unidentified primary mode of toxic action. Given the hypersensitivity of L. stagnalis to Cu, further study into the mechanisms of action and effects of varying water chemistry on Cu toxicity is clearly warranted.     

Whole-body accumulation of copper predicts acute toxicity to an aquatic oligochaete (Lumbriculus variegatus) as pH and calcium are varied

We tested the hypothesis that whole-body accumulation of Cu at 50% mortality (i.e. the median lethal accumulation, LA50 value) in a freshwater oligochaete (Lumbriculus variegatus) is constant across a wide range of water quality, whereas the LC50 values of Cu(total) and the cupric ion (Cu(2+)) in solution are not. We exposed the worms in intermittent-flow, water-only chambers to a series of Cu concentrations at a variety of combinations of pH and water hardness (pH 6.5, 7.5 and 8.5 crossed with hardnesses of 0.5, 2, 4, 6 and 15 mEql(-1)) at 17-20 degrees C. In addition to monitoring mortality at 48 h, we determined whole-body Cu uptake in half of the replicate chambers at 6 h. LC50 values of Cu(total) and Cu(2+) increased as water hardness increased, as expected from traditional LC50 vs. hardness regressions. Moreover, LC50 values of Cu(total) remained approximately constant and LC50 values of Cu(2+) decreased considerably as pH increased, as expected from principles of cation competition and binding by inorganic ligands. However, LA50 values of Cu(body) remained approximately constant (0.17-0.34 micromol Cug(-1) dry wt.) in all pH x hardness combinations. Thus, consistent with the biotic-ligand model, Cu accumulation might be a constant predictor of acute mortality to L. variegatus whereas aqueous Cu concentrations are not.     

Preparation of selectively metal-free and metal-substituted derivatives by reaction of Cu--Zn superoxide dismutase with diethyldithiocarbamate.

Incubation of Cu--Zn superoxide dismutase with diethyldithiocarbamate at increasing ligand/protein ratios and subsequent high-speed centrifugation led to proportional removal of copper from the protein, at variance with previous results [Misra (1979) J. Biol. Chem. 254, 11623--11628]. No zinc was lost, even at very high excesses of chelating agent. In this way a copper-free protein could be readily prepared, with avoidance of the critical pH condition and the dialysis step required in a previous method employing cyanide. The holoprotein was fully reconstituted from the copper-free protein by stoicheiometric re-addition of copper. From the mixture of metal-depleted forms originated by treatment with slight diethyldithiocarbamate excess, the protein containing copper only on one subunit, [Cu1--Zn2], could be isolated by preparative column electrophoresis. This species reproducibly showed 25% more specific activity (catalytic constant per copper) than that of the native or reconstituted [Cu2--Zn2] protein. This may result from long-range conformational effects between the active sites. By adding Co2+ ions to the vacant copper site of [Cu1--Zn2] a hybrid molecule containing Cu(II) on one subunit and Co(II) in the homologous site of the other subunit was prepared. Its activity, referred to copper, was identical with that of the native protein.