Herbicide effects on planktonic systems of different complexity

Bioassays of different complexity were compared with respect to their capability to predict the environmental impact of the herbicide atrazine in aquatic systems. Acute toxicity tests with Daphnia did not yield meaningful results. Sublethal tests with Daphnia (feeding inhibition, reduction of growth and reproduction) were more sensitive, but effective concentrations of atrazine were still rather high (2 mg/L). A relatively complicated artificial food chain system that incorporated direct and indirect effects on Daphnia yielded significant reduction of daphnid population growth at 0.1 mg/L. Enclosure experiments with natural communities were by far the most sensitive tools. Community responses could be measured at concentrations as low as 1 µg/L and 0.1 µg atrazine/L. At the lowest concentration, however, communities recovered after three weeks. We conclude that in complex systems indirect effects can be more important than direct effects, so that, contrary to the conditions in simple tests, non-target organisms may be the better indicators of herbicide stress to natural communities.     

A pulse-amplitude modulated fluorescence-based method for assessing the effects of photosystem II herbicides on freshwater periphyton

A test was developed that measures in vivo chlorophyll afluorescence variables to assess the apparent sensitivity of freshwaterperiphytic algae to photosystem II inhibitors. Natural periphyticcommunities from rivers were collected on artificial substrata, and theeffects of short-term exposures to two PSII herbicides (atrazine andisoproturon) on the fluorescence parameters were measured with apulse-amplitude modulated fluorometer. The EC50 for each herbicide werecalculated from fluorescence yield indices, and these results were comparedto ¹⁴C-based primary production measurements on the samecommunities. The fluorescence-based method appears to give very reliableestimations of EC50 for each pesticide we tested, ranging from 0.46 to5.18 M and 0.07 to 6.77 M for atrazine and isoproturon,respectively. This method could be used in ecotoxicology monitoringprograms, to detect changes in natural periphyton populations sensitivity,following photosystem II herbicide contamination in rivers or lakes.     

Selective real-time herbicide monitoring by an array chip biosensor employing diverse microalgae

A multiple-strain algal biosensor was constructed for the detection of herbicides inhibiting photosynthesis. Nine different microalgal strains were immobilised on an array biochip using permeable membranes. The biosensor allowed on-line measurements of aqueous solutions passing through a flow cell using chlorophyll fluorescence as the biosensor response signal. The herbicides atrazine, simazine, diuron, isoproturon and paraquat were detectable within minutes at minimal LOEC (Lowest Observed Effect Concentration) ranging from 0.5 to 100μgL⁻¹, depending on the herbicide and algal strain. The most sensitive strains in terms of EC₅₀ values were Tetraselmis cordiformis and Scherffelia dubia. Less sensitive species were Chlorella vulgaris, Chlamydomonas sp. and Pseudokirchneriella subcapitata, but for most of the strains no general sensitivity or resistance was found. The different responses of algal strains to the five herbicides constituted a complex response pattern (RP), which was analysed for herbicide specificity within the linear dose-response relationship. Comparisons of herbicide-specific RP to reference RPs of the five herbicides always showed the lowest deviation of the herbicide-specific RP tested with the reference RP of the same herbicide for the triazine and phenylurea herbicides. We therefore conclude that, in principle, identification of a specific herbicide is possible employing the algal sensor chip.     

Molecular analysis of psb A mutations responsible for various herbicide resistance phenotypes in Synechocystis 6714

Mutations conferring herbicide resistance in 3 mutant strains of the cyanobacterium Synechocystis 6714 have been characterized by gene cloning and sequencing. The mutants display very different phenotypes: DCMU-II_A is DCMU-resistant and atrazine-resistant, DCMU-II_B is DCMU-resistant and atrazine-sensitive, and Az-V is DCMU-sensitive, atrazine-resistant and presents particular photoinhibition properties. These mutants were originally obtained either by one-step selection (DCMU-II_A) or by two-step selection (DCMU-II_B and Az-V). psbA copies carrying herbicide resistance have been identified by transformation experiments as psbAI in all cases. Sequences of the psbAI copy of each mutant have been compared to the wild-type sequence. In the single mutant DCMU-II_A, a point mutation at codon 264 (SerAla) results in resistance to both DCMU and atrazine. In the double mutants DCMU-II_B and Az-V, two point mutations were found. DCMU-II_B was derived from DCMU-II_A and had acquired a second mutation at codon 255 (PheLeu) resulting in a slight increase in DCMU resistance and complete abolition of atrazine resistance. Az-V contains two changes at codons 211 (PheSer) and 251 (AlaVal) resulting in high atrazine resistance but only slight DCMU resistance.Abbreviations DCMU: 3-(3,4-dichlorophenyl)-1,1-dimethylurea - PSII: photosystem II     

A mechanism of chlorotoluron resistance in Lolium rigidum

Many biotypes of Lolium rigidum Gaud, (annual ryegrass) have developed resistance to herbicides; however, few have developed resistance to phenylurea herbicides. Two biotypes with different histories of herbicide selection pressure were six to eight times less sensitive to the phenylurea herbicide, chlorotoluron, than a susceptible biotype. Resistance was not due to differences in the herbicide target site as oxygen evolution by thylakoids isolated from resistant and susceptible biotypes was similarly inhibited by diuron and chlorotoluron. There was no difference in the uptake and distribution of chlorotoluron into resistant and susceptible plants. There was a twofold greater rate of chlorotoluron detoxification in resistant plants with N-demethylation being a major detoxification reaction. Resistant plants treated with a 3-h pulse of 120 M chlorotoluron recovered net carbon fixation after 42 h, half the time taken by susceptible plants. The mixed-function oxidase inhibitor 1-aminobenzotriazole (70 M) intensified the effects of chlorotoluron in resistant plants when applied in combination with the herbicide for 7 d. 1-Aminobenzotriazole also inhibited the metabolism of chlorotoluron in both resistant and susceptible plants. The cytochrome P-₄₅₀ inhibitor, piperonyl butoxide piperonyl butoxide, interacted with chlorotoluron when applied to plants growing in soil. Chlorotoluron applied with reduced plant dry weight to a greater extent than chlorotoluron alone. It appears, therefore, that enhanced detoxification is the major mechanism of resistance to chlorotoluron in the resistant biotypes studied.Abbreviations ABT 1-aminobenzotriazole - VLR1 Victorian L. rigidum biotype 1 — herbicide susceptible - VLR69 Victorian L. rigidum biotype 69 — herbicide resistant - WLR2 Western Australian L. rigidum biotype 2 — herbicide resistant M.W.M.B, was supported by an Australian Postgraduate Research Award and a supplementary scholarship from the Grains Research and Development Corporation. We are very grateful to Dr. E. Ebert, Ciba Geigy, Basal, Switzerland for providing [¹⁴C]chlorotoluron and standards of chlorotoluron metabolites. We express our gratitude to Dr. John Huppatz of the CSIRO Division of Plant Industry for providing ABT. We also thank Ciba Geigy Australia for providing technical-grade chlorotoluron and formulated phenylurea herbicides.     

New records of Fucus distichus subspecies for the Shetland and Orkney islands

A new fluorometric device was developed to measure the fluorescence yield of microalgae in order to detect photosystem II specific herbicides in outdoor water samples. The system was tested with respect to sensitivity and reliability with two species: Chlorella fusca (a green alga) and Phaeodactylum tricornutum (a diatom). The main advantages are the use of cell cultures without preliminary centrifugation, the evaluation of variable fluorescence from steady-state levels, and the rapidity of the measurement. Concentrations around the binding constant of inhibitors (around 10^-8 M) can be detected for dichlorophenyldimethylurea, atrazine and simazine. The new system was compared with the commercially available pulse amplitude fluorometer PAM 101; it was shown that the sensitivity was about 10 times greater than with PAM 101, working at optimal chlorophyll concentrations. The advantages and limits of both systems when applied to free-water samples are discussed.     

Direct triazine herbicide detection using a self-assembled photosynthetic reaction center from purple bacterium

In this study, a direct detection system for triazine derivative herbicides was developed using the photosynthetic reaction center (RC) from the purple bacterium,Rhodobacter sphaeroides, and surface plasmon resonance (SPR) apparatus. The histidine-tagged RCs were immobilized on an SPR gold chip using nickel-nitrilotriacetic acid groups as a binder for one of the triazine herbicide, atrazine. The SPR responses were proportional to the sample concentrations of atrazine in the range 0.1–1 μg/mL. The sensitivity of the direct detection of atrazine using the RC-assembled sensor chip was higher than that using the antibody-immobilized chip. The other types of herbicides, DCMU or MCPP, were not detected with such high sensitivity. The results indicated the high binding selectivity of the RC complex.     

Multiple action sites for photosystem II herbicides as revealed by delayed fluorescence

DCMU (3-(3,4-dichlorophenyl)-1,1-dimethylurea) at concentrations higher than 10 M suppresses the second time range delayed fluorescence (DF) of pea chloroplasts, due to inhibition of the oxidizing side of photosystem II (PS II). The inhibition of the reducing side of PS II resulting in the suppression of millisecond DF takes place at much lower (0.01 M) DCMU concentrations. The variation in the herbicide-affinities of the reducing and oxidizing sides of PS II is not the same for DCMU and phenol-type herbicides. The DCMU-affinity of the oxidizing side considerably increases and approximates that of the reducing side upon mild treatment of chloroplasts with oleic acid. Probably this is a result of some changes in the environment of the binding site at the oxidizing side. At DCMU concentrations higher than 1 mM, the chaotropic action of DCMU leads to the generation of millisecond luminescence which is not related to the functioning of the reaction centres.Abbreviations D-1 The 32 kDa herbicide-binding intrinsic polypeptide of PS II, the apoprotein of Q_B - D-2 The 32–34 kDa intrinsic polypeptide of PS II, probably the apoprotein of Z - DCMU 3-(3,4-dichlorophenyl)-1,1-dimethylurea - DF Delayed fluorescence - Dinoseb 2,4-dinitro-6-sec-butylphenol - DNOC 4,6-dinitro-o-cresol - F_m Maximal fluorescence yield (when all traps are closed) - F_o Constant fluorescence yield (when all traps are open) - PS Photosystem - Q_A and Q_B The primary and secondary plastoquinone acceptors of PS II, correspondingly - Z A plastoquinol electron donor, presumably associated with the D-2 protein     

Microalgae fiber optic biosensors for herbicide monitoring using sol–gel technology

Three microalgal species (Dictyosphaerium chlorelloides (D.c.), Scenedesmus intermedius (S.i.) and Scenedesmus sp. (S.s.)) were encapsulated in silicate sol–gel matrices and the increase in the amount of chlorophyll fluorescence signal was used to quantify simazine. Influence of several parameters on the preparation of the sensing layers has been evaluated: effect of pH on sol–gel gelation time; effect of algae density on sensor response; influence of glycerol (%) on the membrane stability. Long term stability was also tested and the fluorescence signal from biosensors remained stable for at least 3 weeks. D.c. biosensor presented the lowest detection limits for simazine (3.6 μg L⁻¹) and the broadest dynamic calibration range (19–860 μg L⁻¹) with IC₅₀ 125 ± 14 μg L⁻¹. Biosensor was validated by HPLC with UV/DAD detection. The biosensor showed response to those herbicides that inhibit the photosynthesis at photosystem II (triazines: simazine, atrazine, propazine, terbuthylazine; urea based herbicides: linuron). However, no significant increases of fluorescence response was obtained for similar concentrations of 2,4-D (hormonal herbicide) or Cu(II). The combined use of two biosensors that use two different genotypes, sensitive and resistant to simazine, jointly allowed improving microalgae biosensor specificity.     

Detection and quantification of triazine herbicides using algal cell fluorescence

Summary A continuous-flow system is described which, by measuring fluorescence of the unicellular alga Chlorella, is capable of measuring concentrations of the triazine herbicide, simazine, as low as 60nM (approx 12g l^-1) within 5 minutes. Further developments are suggested to achieve the desired detection limit of 0.5nM. The use of such an instrument in environmental analysis is discussed.     

A differential effect of 3-(3′4′ dichlorophenyl)-1,1 dimethyl urea and atrazine on fluorescence kinetics in chloroplasts

It was found that DCMU had a differential effect at two concentration ranges on variable fluorescence kinetics in isolated chloroplasts. The increase in fluorescence rate at low concentrations of DCMU was abolished by preincubation of chloroplasts with ferricyanide or formate, treatments which were shown to convert Fe in the PS II reaction center (i.e., the FeQ_A complex) into a non-oxidizable form, but it was not affected by Tris treatment. Increase in fluorescence kinetics (at the initial linear rate) at high concentrations of DCMU was found to be abolished by Tris treatment but it was only marginally affected by ferricyanide or formate treatments. The effect of Tris could be abolished by addition of hydroquinone-ascorbate, which restored electron flow to the pool of secondary acceptors.Contrary to the effect of DCMU, no such differential concentration dependence of the variable fluorescence kinetics was found for atrazine.The increase in fluorescence kinetics (at the initial linear rate) at a low concentration rate of DCMU is presumably restricted to units which contain an oxidizable Fe in the FeQ_A complex. Increase in fluorescence kinetics (at the initial linear rate) at high DCMU concentration is probably related to the effect of DCMU at the Q_B site.Abbreviations DCMU 3-(34 dichlorophenyl)-1,1 dimethyl urea - PS II Photosystem II - Tris tris (hydroxymethyl) aminomethane     

Influence of temperature on phytotoxicity of triazine herbicides to pine seedlings

The effects of temperature, over a range of 5 to 30 C, on phytotoxicity of simazine, atrazine, propazine, prometryne, prometone, and ipazine to young Pinus resinosa seedlings were investigated in growth chambers. Herbicides were applied to the soil surface and then mixed into the soil before pine seeds were planted. Development of recently germinated seedlings was then studied for 7 weeks. High temperatures greatly accelerated herbicide toxicity, but the effects of temperature varied greatly among herbicides. Atrazine and simazine were more toxic than other herbicides tested at all temperatures. Toxicity of simazine and atrazine was apparent early, whereas effects of propazine, prometryne, prometone, and ipazine were somewhat delayed. After 7 weeks maximum dry-weight production of shoots under each herbicide treatment and control occurred at 20 C, with some decreases noted at lower temperatures and marked decreases at progressively higher ones. At 20 C final seedling dry weights following treatment with simazine or atrazine were only one-third as high as in control plants. Growth was also reduced in lesser amounts by propazine, prometryne, prometone, or ipazine. Variations in phytotoxicity of different triazine herbicides appeared to be related more to their structural differences than their solubilities. Under the constant environmental conditions of the experiments, toxicity symptoms in plants treated with triazine herbicides appeared more rapidly and decisively than in previous field experiments under fluctuating environments. The influence of high temperatures in enhancing triazine toxicity appeared to involve complex interactions of physiological activity of plants and temperature effects on herbicide uptake.     

Effects of pesticides on seagrass beds

In the German Wadden Sea there has been a remarkable decline in seagrass beds. It was the aim of this study to test whether herbicide contamination could be a reason for this. Concentrations of triazine herbicides such as atrazine, simazine and terbutylazine as well as phenylurea herbicides were measured in Wadden Sea sediments within or in the neighbourhood of seagrass meadows. Sediments were thus used as a marker for medium-term contamination of the Wadden Sea. The respective concentrations were examined in relation to the density and status of the seagrass meadows. Preliminary results show that there may be a connection between seagrass decline and herbicide contamination in the parts of the Wadden Sea sampled. A comparison with other contamination is also given. Received: 11 January 1999 / Received in revised form: 1 December 1999 / Accepted: 8 December 1999     

Study of soil algae

Summary The application of the algal method for soil bioassay has been extended to herbicide (atrazine). The method is capable of detecting less than 0.5 ppm of atrazine in solution. In residual herbicide assay the method is suitable for screening soils. For herbicide requirement prediction, the technique appeared to be superior to chemical analysis and applicable to soils of widely different characteristics. This has been demonstrated with oat pot trial.-2-chloro-4-ethylamino-6 isopropylamino-s-triazine.     

Herbicide-binding to thylakoid membranes of a DCMU-resistant mutant of Chlamydomonas reinhardii

The specific binding of DCMU and atrazine to the thylakoid membranes of a uniparentally inherited DCMU-resistant mutant dr-416 of Chlamydomonas reinhardii was measured. Whole cells of the mutant can tolerate a 15-fold concentration of DCMU as compared to the parent strain. The same tolerance is found for the photosystem II activity of isolated thylakoid membranes. The mutant is not resistant against atrazine. In equilibrium-binding studies with [¹⁴C]atrazine and unlabelled DCMU, the specific binding for atrazine was found to be identical in the mutant and in the parent strain. The competitive binding of DCMU is significantly weaker for membranes of the mutant than of the parent strain, the equilibrium dissociation constants being 2.0 × 10^?7 M and 3.8 × 10^?8 M, respectively.     

Atrazine induced changes in elemental and biochemical composition and nitrate reductase activity in Chlamydomonas reinhardtii

Herbicides play an important role in agricultural practices but the introduction of these compounds into the aquatic environment can have severe consequences for non-target organisms such as microalgae. The ubiquitous green freshwater microalga Chlamydomonas reinhardtii, a model species in all aspects of microalgal physiology, was used to assess the toxicity of atrazine, one of the most widely used herbicides throughout the world. Atrazine acts on photosynthesis and therefore can affect non-target primary producers, such as microalgae.

Growth, dry weight, elemental composition, photosynthetic pigments and protein contents and nitrate reductase activity were studied. After 96 h of exposure to different atrazine concentrations all the parameters studied were affected, but different sensitivities to the herbicide were shown. Nitrate reductase (NR) activity was strongly affected even at an atrazine concentration that did not affect growth (0.1 µM); the lowest concentrations of atrazine assayed (0.1 and 0.25 µM) provoked a > 40% decrease in NR activity and NR decreased > 80% with atrazine concentrations of 0.5 µM. C/N ratio was also affected by all the atrazine concentrations assayed. Nitrate reductase activity and C/N ratio were better indicators of the cellular stress state than data on other biochemical components or growth rate. Among cell parameters assayed, the NR activity stood out as a sensitive cytotoxicity endpoint and the activity of this enzyme can be suggested as a sensitive biomarker of stress induced by atrazine in C. reinhardtii.     

Monochromatic ultraviolet light induced damage to Photosystem II efficiency and carbon fixation in the marine diatom Thalassiosira pseudonana (3H)

Low light adapted cultures of the marine diatom Thalassiosira pseudonana (3H) were cultured and incubated for 30 min under different ultraviolet (UV) wavelengths of near monochromatic light with and without background photosynthetically active radiation (PAR, 380–700 nm). Maximum damage to the quantum yield for stable charge separations was found in the UVB (280-320 nm) wavelengths without background PAR light while the damage under PAR was 30% less. UV induced damage to carbon fixation in the cells was described by a function similar to non-linear functions of inhibiting irradiance previously published with the exception that damage was slightly higher in the UVA (320–380). Various measurements of fluorescent transients were measured and the results indicate localised damage most likely on the acceptor side of the Photosystem II reaction center. However, dark adapted measurements of fluorescence transients with and without DCMU do not result in similar functions. This is also true for the relationships between fluorescence transients and carbon fixation for this species of marine diatom. The correlation between the weightings _H from measurements of carbon fixation and the quantum yield for stable charge separation as calculated from induction curves with DCMU and without DCMU is R ² 0.44 and R ² 0.78, respectively. The slopes of the two measurements are 3.8 and 1.4, respectively. The strong correlation between the weightings of the induction curves without DCMU and carbon fixation are due to a loss of electron transport from the reaction center to plastoquinone. Under these experimental conditions of constant photon flux density (PFD) this is manifested as a strong linear relationship between the decrease in the operational quantum yield of Photosystem II and carbon fixation. This revised version was published online in June 2006 with corrections to the Cover Date.     

In situ nutrient assays of periphyton growth in a lowland Costa Rican stream

Nutrient limitation of primary production was experimentally assessed using an in situ bioassay technique in the Quebrada Salto, a third-order tropical stream draining the northern foothills of the Cordillera Central in Costa Rica. Bioassays employed artificial substrata enriched with nutrients that slowly diffuse through an agar-sand matrix (Pringle & Bowers, 1984). Multiple comparisons of regression coefficients, describing chlorophyll-a accrual through time for different nutrient treatments, revealed positive micronutrient effect(s). Micronutrient treatment combinations (Fe, B, Mn, Zn, Co, Mo, EDTA), supplemented with and without nitrate and phosphate, exhibited significantly greater chlorophyll-a accrual over all other treatments (P < 0.05), supporting over three times that of the control after 14-d of substratum colonization. Neither of the major nutrients (N or P) produced a significant stimulation, although the N treatment displayed 50% more chlorophyll-a than the control after 14-d. Similarly, Si, EDTA, and Si + N + P treatments did not exhibit chlorophyll-a response curves that were significantly different from the control. During the experiment, mean NH₄-N and (NO₂ + NO₃)-N concentrations in the Salto were 2.0 µM (28.6 µg · l^–1) and 7.2 µM (100.2 µg · l ^–1), respectively. High concentrations of PO₄-P ( = 2.0 µM; 60.9 µg · l^–1) and TP ( = 3.0 µM; 94.0 µg · l^–1) were also found, and consequently low molar N:P ratios = 4.7). Despite the potential for N limitation in the system, both N and P appear to be at growth saturating levels. This may be due to micronutrient limitation and/or light limitation of periphyton growth in densely shaded upstream portions of the stream.     

A chlorophyll a fluorescence-based Lemna minor bioassay to monitor microbial degradation of nanomolar to micromolar concentrations of linuron

A plant-microbial bioassay, based on the aquatic macrophyte Lemna minor L. (duckweed), was used to monitor biodegradation of nano- and micromolar concentrations of the phenylurea herbicide linuron. After 7 days of exposure to linuron, log-logistic-based dose-response analysis revealed significant growth inhibition on the total frond area of L. minor when linuron concentrations > or = 80 nM were added to the bioassay. A plant-protective effect was obtained for all concentrations > 80 nM by inoculation with either a bacterial consortium or Variovorax paradoxus WDL1, which is probably the main actor in this consortium. The outcome of the plant-microbe-toxicant interaction was also assessed using pulse amplitude-modulated chlorophyll a fluorescence and chlorophyll a fluorescence imaging. Linuron toxicity to L. minor became apparent as a significant decrease in the effective quantum yield (Delta F/Fm') within 90 min after exposure of the plants to linuron concentrations > or = 160 nM. Inoculation of the bioassay with the linuron-degrading bacteria neutralized the effect on the effective quantum yield at concentrations > or = 160 nM, indicating microbial degradation of these concentrations. The chlorophyll a fluorescence-based Lemna bioassay described here offers a sensitive, fast and cost-effective approach to study the potential of biodegrading microorganisms to break down minute concentrations of photosynthesis-inhibiting xenobiotics.     

Detection of rapid induction kinetics with a new type of high-frequency modulated chlorophyll fluorometer

A newly developed modulation fluorometer is described which operates with 1 sec light pulses from a light-emitting diode (LED) at 100 KHz. Special amplification circuits assure a highly selective recording of pulse fluorescence signals against a vast background of non-modulated light. The system tolerates ratios of up to 1:10⁷ between measuring light and actinic light. Thus it is possible to measure the dark fluorescence yield and record the kinetics of light-induced changes. A high time resolution allows the recording of the rapid relaxation kinetic following a saturating single turnover flash. Examples of system performance are given. It is shown that following a flash the reoxidation kinetics of photosystem II acceptors are slowed down not only by the inhibitor DCMU, but by a number of other treatments as well. From a light intensity dependency of the induction kinetics the existence of two saturated intermediate levels (I₁ and I₂) is apparent, which indicates the removal of three distinct types of fluorescence quenching in the overall fluorescence rise from F₀ to F_max.Abbreviations Q_A and Q_B consecutive electron acceptors of photosystem II - PS II photosystem II - P 680 reaction center chlorophyll of photosystem II - F₀ minimum fluorescence yield following dark adaptation - F_max maximum fluorescence yield - DCMU 3-(3, 4-dichlorophenyl)-1, 1-dimethyl-urea - DCCD N,N-dicyclohexylcarbodiimide - PQ plastoquinone - DAD diaminodurene Dedicated to Prof. L.N.M. Duysens on the occasion of his retirement.