Reproduction Of Folsomia Candida Research Articles

Assessing the ecotoxicological effects of novel cellulose nanocrystalline glitter compared to conventional polyethylene terephthalate glitter: Toxicity to springtails (Folsomia candida)

Glitter is a type of microplastic, and thus there is a need to assess its potential impacts on the environment and to assess the potential for non-plastic cellulose nanocrystal structurally colored glitters as safe and sustainable replacements. The ecotoxicity of glitter has been mostly ignored in the research literature, with only a few published studies focusing on aquatic organisms. Therefore, an exposure experiment was conducted to examine the impact of conventional polyethylene terephthalate (PET) glitter as well as untreated and heat-treated cellulose nanocrystal (CNC) based glitter on the survival, reproduction, and length of Folsomia candida (springtail). Folsomia candida reproduction was reduced by 61% (P = 0.013) after exposure to PET glitter at 1000 mg/kg, while no significant effects were observed on F. candida survival and length. In contrast, there were no significant impacts on F. candida survival, length, or reproduction when exposed to untreated or heat-treated CNC glitter. These results indicate that exposure to PET glitter may impact soil invertebrates at the population level, and that CNC glitter has potential as a biodegradable non-plastic alternative to PET glitter to decrease detrimental effects on soil ecosystems.

Comparison of established and novel insecticides on survival and reproduction of Folsomia candida.

Neonicotinoid insecticides have been among the most widely and abundantly used insecticides for most of the current century. The effects of these substances on non-target terrestrial and aquatic organisms have resulted in a significant decrease in their use in many parts of the world. In response, the application of several novel classes of insecticides including diamides, ketoenols, pyridines, and butenolides has significantly increased. The hexapod subclass Collembola is an ecologically significant and widely distributed group of soil invertebrates often found in leaf litter and in surficial soils. In this study, the parthenogenic collembolan species Folsomia candida was exposed to six insecticides in a sandy loam soil for 28 days, including two neonicotinoids (thiamethoxam, clothianidin), a diamide (cyantraniliprole), a ketoenol (spirotetramat), a pyridine (flonicamid), and a butanolide (flupyradifurone) to assess the effect of each insecticide on survival and reproduction. Clothianidin, thiamethoxam, and cyantraniliprole (EC50s (reproduction): 0.19, 0.38, and 0.49 mg/kg soil, respectively) had a greater effect on survival and reproduction of F. candida than flupyradifurone, spirotetramat, and flonicamid (EC50s (reproduction): 0.73, >3.08, and 5.20 mg/kg soil, respectively). All significant impacts observed in this study were observed at concentrations below concentrations of the active ingredients that would be expected in agricultural soils. This article is protected by copyright. All rights reserved. Environ Toxicol Chem 2023;00:0-0. © 2023 SETAC.

Long life at low temperatures – The life-history of Folsomia candida at ecological relevant temperatures

Collembola are among the most abundant terrestrial microarthropods and are widely used in ecotoxicological testing since they are important for soil ecosystem processes (Fountain and Hopkin 2005). In their natural environment, these arthropods are often exposed to varying temperatures (Smit and Van Gestel 1997; Fountain and Hopkin 2005; Bindesbøl 2008). However, when applied as a model organism for ecotoxicological testing, experiments are performed at 20 °C; Smit and Van Gestel 1997; International Organization for Standardization (ISO) 1999; OECD 2009). The temperature choice might be beneficial concerning the timeline of these 28-day experiments (e.g., covering juvenile phase, first reproduction, and first generation hatching) but does not reflect the reality in the field. Variable climate can influence the functioning of organisms and thereby induce changes in susceptibility for toxicant stress (Smit and Van Gestel 1997; Bindesbøl 2008; de Boer et al. 2010). The presented study aims to investigate: (1) longevity of F. candida at different temperatures; (2) reproduction of the species also under different temperatures. Two different test designs were developed, each aiming to analyse a different aspect of the life cycle of F. candida. The results showed that temperature has a significant impact on the life-history traits, longevity, and reproduction of Folsomia candida. Temperatures below the standard of 20 °C significantly increased the life span up to 922.5 days at 4 °C. Furthermore, our results highlight the effect of temperature on developmental processes, such as hatching time and maturation.

The co-occurrence of Zn-and Cu-based engineered nanoparticles in soils: The metal extractability vs. toxicity to Folsomia candida

The presence of engineered nanoparticles (ENPs) in soil gradually increases, among others due to the nano-agrochemicals application. So far, the co-existence of different ENPs in soil is poorly examined. Here, the metal extractability and toxicity of soils spiked (300 mg kg−1) singly and jointly with Zn- and Cu-based ENPs or metal salts were tested. The samples were aged for 1 and 90 days. The predicting available metal component of ENPs concentrations were determined by different methods including soil pore water collection and batch extractions with H2O, CaCl2 or DTPA. Survival and reproduction of Folsomia candida were also evaluated. The combined effect of ENPs on the extractability of metals was mainly found with DTPA characterized by the highest leaching capacity among the used extractants. In fresh soil, the mixtures of ENPs differentiated only DTPA-extractable Cu level, while aging resulted in changes in both Zn and Cu concentrations leached by CaCl2 or DTPA. However, the character of the combined effect was an ENPs- and soil type-dependent, whereas the mixtures of metal salts mostly provided higher Zn and Cu recovery than the individual compounds. The pattern of co-toxicity of metal-oxide ENPs was also time-dependent: the antagonistic and synergistic effect was observed in the samples after 1 and 90 days, respectively. However, the toxicity was weakly related with extractable concentrations in both single and joint treatment of metal compounds. The distinct joint effect patterns of ENPs imply the need for more in-depth investigation of mechanisms of activity of ENPs mixtures in soil.

Low concentration effects and different outcome in repeated reproduction tests with silver nanoparticles, silver nitrate and Folsomia candida (Collembola)

BackgroundToxicity of silver nanoparticles (AgNP) has been studied frequently due to a rise in application in various products. Various studies on AgNP toxicity with terrestrial and aquatic organisms confirmed their negative effects. In our previous experiments, strong variability was observed in the reproduction of Collembola (Folsomia candida) in different repeats. To investigate the effects of silver on the reproduction of Folsomia candida, they were exposed in laboratory-controlled conditions to AgNP and silver nitrate (AgNO3) at a concentration of 30 mg/kg dry soil for 28 days and compared to controlled individuals not exposed to silver. We repeated reproduction tests on the toxicity of silver to Folsomia candida four times throughout one year (April, July, October and January) in order to explore the temporal variability of their outcome.ResultsWhile adult survival was similar in all treatments and seasons, reproduction in the control increased from April to October. Significantly lower reproduction was found in January with only 385–424 juveniles per vessel, compared to 504–633 individuals in other months. Strong toxic effects of both silver treatments were observed in July, April and October. However, AgNP showed no toxic effects on the reproduction of F. candida in January. The relative toxicity of both substances varied between single experiments: AgNP were more toxic than AgNO3 in April and July, and less toxic in October and January.ConclusionThese findings indicate that the reproduction of F. candida in the control had a significant effect on the results of the toxicology experiments. Moreover, we demonstrated the reproductive toxicity of AgNP in soil at a much lower concentration than reported thus far. Therefore, to guarantee reliability and reproducibility, we recommend to disregard any test results where the reproduction rate of F. candida in the control is significantly different from the average in the respective laboratory, even if the validity criteria of the test are met.

The effect of composted and non-composted poultry litter on survival and reproduction of Folsomia candida

Purpose The objective was to evaluate the effect of the application of composted and non-composted poultry litter, as fertilizer in agricultural areas, on the survival and reproduction of the springtails (Folsomia candida) through standardized ecotoxicological tests. Methods The treatments included in the application of composted and non-composted poultry litter on Entisol were in the following doses 0, 10, 20, 40, 60, 80, 100 t ha-1, for the lethality test, and 0, 5, 7.5, 10, 15, 30, 40, 60 t ha-1 for th­­e reproduction test. Results For the composted litter, the LC50 value was 76.45 t ha-1 and for EC50, it was 17.96 t ha-1. For the non-composted poultry litter, the values of LC50 was 43.12t ha-1 and EC50 value was 19.36 t ha-1. Conclusion The highest toxicity was observed in the non-composted litter, emphasizing the importance of stabilization of the organic compound before its use as fertilizer.

The forgotten role of toxicodynamics: How habitat quality alters the mite, Oppia nitens, susceptibility to zinc, independent of toxicokinetics.

Soil habitat quality is thought to influence metal toxicity via changes in speciation and thereby toxicokinetics. Here, we assessed the toxicokinetic and toxicodynamic effects of habitat quality on mite, Oppia nitens when exposed to zinc (Zn) contaminated soils. Forty-seven soils were ranked into three habitat qualities; high, medium, and low based on biological reproduction of Folsomia candida, Enchytraeus crypticus, and Elymus lanceolatus. From the 47 soils, eighteen soils (comprising of six soils from each habitat quality) were randomly selected and dosed with field relevant concentrations of Zn. Mite survival and reproduction were assessed after 28 days. Total Zn, bioaccessible Zn, Zn bioavailability, Zn body burden, lactate dehydrogenase activity (LDH) and glucose-6-phosphate dehydrogenase (G6PDH) activities of the mites were determined. Zinc toxicity and potency were much less in the high compared to low quality soils and the mites in the high habitat quality soils tolerated higher zinc body burdens (2040 ± 130 μg/g b.w) than the lower habitat quality (1180 ± 310 μg/g b.w). Lower LDH activity (20 ± 2 μU mg−1) in the high quality soils compared to lower quality soils (50 ± 8 μU mg−1) suggested that there was less stress in the high habitat quality mites. Despite changes in speciation across habitat qualities, bioavailability of zinc was similar (∼20%) irrespective of habitat quality. Our results suggest that the influence of soil properties on survival is modulated by toxicodynamics rather than toxicokinetics. Restoring habitat quality may be more important for soil invertebrate protection than metal concentration at contaminated sites.

Transgenerational and multigenerational stress gene responses to the insecticide etofenprox in Folsomia candida (Collembola)

Insecticide exposure may cause both transgenerational and multigenerational effects on populations, but the molecular mechanisms of these changes remain largely unclear. Many studies have focused on either transgenerational or multigenerational mechanisms but did neglect the comparative aspects. This study assessed whether the pyrethroid insecticide etofenprox (formulation Trebon® 30 EC) shows transgenerational and/or multigenerational effects on the survival and reproduction of Folsomia candida (Collembola). The activation of stress-related genes was studied to detect whether etofenprox modifies the expression of reproduction-associated genes in trans- and multigenerational treatments. A laboratory study was carried out for three generations with five insecticide concentrations in LUFA 2.2 soil. In the transgenerational treatment, only the parent generation (P) was exposed, but the subsequent generations were not. In the multigenerational treatment, all three generations were exposed to the insecticide in the same manner. Multigenerational exposure resulted in reduced reproduction effects over generations, suggesting that F. candida is capable of acclimating to enhanced concentration levels of etofenprox during prolonged exposure over multiple generations. In the transgenerational treatment, the heat shock protein 70 was up-regulated and cytochrome oxidase 6N4v1 expression down-regulated in a dose-dependent manner in the F2 generation. This finding raises the possibility of the epigenetic inheritance of insecticide impacts on parents. Furthermore, CYP6N4v1 expression was oppositely regulated in the trans- and multigenerational treatments. Our results draw attention to the differences in molecular level responses of F. candida to trans- and multigenerational etofenprox exposure.

Biomonitoring tools for biochar and biochar-compost amended soil under viticulture: Looking at exposure and effects

Benefits that biochar can bring to unirrigated vineyards are related mainly to soil chemistry, soil structure and water retention improvements. Little is still known about effects of biochar on soil biotic processes and organisms that mediate them. For a sustainable use of biochar in agriculture, alone or in combination with other soil amendments, there is a need for better understanding of soil-biochar-biota interactions, particularly in the long term. Here we applied an ecotoxicological monitoring programme to evaluate the effects of field plot-scale biochar and biochar-compost mixture into vineyard soil. Standard and well described laboratory bioassays were used, assessing the survival and reproduction of Folsomia candida and food consumption and biomass change of Porcellionides pruinosus. The present study examined the effects of biochar- and biochar-compost-enriched soil treatments in a commercial vineyard subjected to conventional pesticide management practices. We considered two sampling events, corresponding to: i) the time of initial application of fresh biochar and biochar-compost (T0); and ii) the 18 month-period after the application of the amendments (T18). Additionally, based on the time and rates of the pesticides application prior to the second sampling event, a theoretical exposure was estimated alongside with risk quotients. The risk quotients were elevated for certain active ingredients in the mixture (cyprodinil, propiconazole, copper oxychloride and copper sulfate). This corroborates the overall decrease in organisms' performance observed after they were exposed to the field-aged samples. The ecotoxicological response to the tested biochar and biochar-compost enriched soil was species-specific, time-dependent, and to some extent, treatment-dependent. The most sensitive endpoint obtained in the study was the reproduction output of F. candida. While freshly amended soil did not induce substantial changes on organisms' performance, the measured endpoints were significantly lower when the organisms were exposed to the treatments from the second sampling event which was subjected to various climatic factors and conventional pesticides. Regarding food consumption of P. pruinosus, and number of F. candida juveniles the effects were more pronounced in 40 t ha−1 biochar and biochar-compost amended treatments than in 4 t ha−1 treatment. Results of the study show that bioavailability of potentially toxic elements might not be prevented over time by the presence of biochar and biochar-compost in commercial vineyards that receive conventional plant protection products.

Is a Water Content of 60% Maximum Water Holding Capacity Suitable for Folsomia candida Reproduction Tests? A Study with Silver Nanoparticles and AgNO₃.

Silver nanoparticles (AgNP) are increasingly emitted to the environment due to a rise in application in various products; therefore, assessment of their potential risks for biota is important. In this study the effects of AgNP at environmentally relevant concentrations (0.6–375 µg kg−1 soil) on the soil invertebrate Folsomia candida in OECD (Organisation for Economic Co-operation and Development) soil was examined at different soil water contents. Animals were retrieved by heat extraction, which had an efficiency of about 90% compared with the floatation method. The tested water content range is set by OECD Guideline 232 (40–60% of the maximum water holding capacity, WHC), and we detected significant differences in toxicity due to these. With AgNO3, used as an ionic control, the number of juveniles significantly decreased only at 40% WHC, which might be due to dilution of the toxicant at higher soil water content. In turn, at 60% WHC, the reproduction of F. candida significantly increased in the presence of AgNP compared with in the control. However, at this water content, the required number of juveniles in the control treatment was not reached in three independent tests. The fact that the OECD validity criterion is not met indicates that the soil conditions are not suitable for reproduction at 60% WHC.

No effect of selected engineered nanomaterials on reproduction and survival of the springtail Folsomia candida

Engineered nanomaterials did not affect Folsomia candida reproduction at concentrations up to 6400 mg per kg dry soil. However, significant effects of metal salt exposure were observed.

Collembola Reproduction Decreases with Aging of Silver Nanoparticles in a Sewage Sludge-Treated Soil

Silver nanoparticles (AgNP) are integrated into various products due to their antimicrobial characteristics and hence, the application of AgNP is increasing. During production, use and disposal AgNP are emitted and enter the environment via several pathways. Soils are considered a major sink of AgNP. The aim of the present study was to determine the toxic effect of AgNP on Folsomia candida reproduction to illustrate potential impact on terrestrial ecosystems. The AgNP-dependent reduction of F. candida reproduction was studied in RefeSol 01-A, LUFA 2.2 and OECD soil at 0.3 µg – 50 mg Ag kg-1. To simulate realistic exposure pathways, effects on F. candida reproduction after the application of AgNP via sewage sludge and after aging this treatment in the soil for up to 140 days were studied using environmentally relevant concentrations. The OECD representative AgNP, NM-300K, and AgNO3, as a metal salt reference, were used in all experiments. The generated data demonstrate that the presence of AgNP in the soil in the low mg Ag kg-1 concentration range results in significant, but concentration independent inhibition of F. candida reproduction in RefeSol 01-A and LUFA 2.2. Significant inhibition of F. candida reproduction due to AgNP was also observed for soil amended with AgNP treated sludge. An increase in inhibition with aging of the AgNP in the soil was evident. In conclusion, our results demonstrate that, at environmentally relevant concentrations, AgNP adsorption to sludge and subsequent aging in soil lead to a toxic effect on soil invertebrates.

Toxicity of four veterinary pharmaceuticals on the survival and reproduction of Folsomia candida in tropical soils

This study aimed to evaluate the effect of veterinary pharmaceuticals (VPs) used to control endo- and ectoparasites in ruminants, on the survival and reproduction of the collembolan species Folsomia candida. Standard ecotoxicological tests were conducted in Tropical Artificial Soil and the treatments consisted of increasing dosages of four commercial products with different active ingredients: ivermectin, fipronil, fluazuron and closantel. Ecotoxicological effects were related to the class and mode of action of the different compounds. Fipronil and ivermectin were the most toxic compounds causing a significant reduction in the number of juveniles at the lowest doses tested (LOECreprod values of 0.3 and 0.2 mg kg−1 of dry soil, respectively) and similar low EC50 values (fipronil: 0.19 mg kg−1 dry soil, CL95% 0.16–0.22; ivermectin: 0.43 mg kg−1 dry soil, CL95% 0.09–0.77), although the effects observed in the former compound were possibly related to a low adult survival (LC50 of 0.62 mg kg−1 dry soil; CL95%: 0.25–1.06). For the latter compound no significant lethal effects were observed. Fluazuron caused an intermediate toxicity (EC50 of 3.07 mg kg−1 dry soil, CL95%: 2.26–3.87), and also here a decrease in adult survival could explain the effects observed at reproduction. Closantel, despite showing a significant reduction on the number of juveniles produced, no dose-response relationship nor effects higher than 50% were observed. Overall, all tested compounds, especially ivermectin, when present in soil even at sub-lethal concentrations, can impair the reproduction of collembolans and possibly other arthropods. However, the actual risk to arthropod communities should be further investigated performing tests under a more realistic exposure (e.g., by testing the dung itself as the contaminated matrix) and by deriving ecotoxicologically relevant exposure concentration in soil derived from the presence of cattle dung.

Ecotoxicological assessment of biosolids by microcosms

Biosolids have been applied as soil amendments to improve and maintain the soil fertility and faster plant growth. In spite of its beneficial use, the potential risks of land disposal should be analyzed, considering potential ecological receptors in soil and water. This work describes the use of an early warning laboratory microcosm system to evaluate the integrated ecotoxicological potential of two biosolids: BIO-1 and BIO-2 (18 and 28 months after landfarming, respectively), from an effluent treatment station in a petrochemical and industrial district. The endpoints related to habitat function were: a) germination, growth and biomass of Phaseolus vulgaris; b) survival, biomass and number of cocoons of Eisenia andrei (Oligochaeta) and; c) reproduction of Folsomia candida (Collembola). The retention function was evaluated by testing the leachates using the tropical cladoceran Latonopsis australis (Cladocera) in a 48-h acute toxicity test, and growth of the aquatic plant Lemna minor in a 7-d chronic test. Tropical artificial soil (TAS) and a natural soil (NS) from the region were used as control soils. Results showed no chronic toxicity of BIO-1 and BIO-2 to the soil organisms tested, but acute toxicity of BIO-1 in the leachate for 50% of L. australis, and chronic toxicity of both biosolid leachates to L. minor (inhibition of growth rate), indicating potential risks to aquatic ecosystems. The results confirmed the ability of this microcosm system as a rapid tool to assess biosolid toxicity over time and its potential for hazardous waste characterization in environmental risk assessment, in a screening phase.

Ecotoxicity of arsenic contaminated sludge after mixing with soils and addition into composting and vermicomposting processes

Sludge coming from remediation of groundwater contaminated by industry is usually managed as hazardous waste despite it might be considered for further processing as a source of nutrients. The ecotoxicity of phosphorus rich sludge contaminated with arsenic was evaluated after mixing with soil and cultivation with Sinapis alba, and supplementation into composting and vermicomposting processes. The Enchytraeus crypticus and Folsomia candida reproduction tests and the Lactuca sativa root growth test were used. Invertebrate bioassays reacted sensitively to arsenic presence in soil-sludge mixtures. The root elongation of L. sativa was not sensitive and showed variable results. In general, the relationship between invertebrate tests results and arsenic mobile concentration was indicated in majority endpoints. Nevertheless, significant portion of the results still cannot be satisfactorily explained by As chemistry data. Composted and vermicomposted sludge mixtures showed surprisingly high toxicity on all three tested organisms despite the decrease in arsenic mobility, probably due to toxic metabolites of bacteria and earthworms produced during these processes. The results from the study indicated the inability of chemical methods to predict the effects of complex mixtures on living organisms with respect to ecotoxicity bioassays.

Ecotoxicological effects of pig manure on Folsomia candida in subtropical Brazilian soils

The effects of pig manure, from diets incorporating veterinary pharmaceuticals, on survival and reproduction of Folsomia candida were evaluated. Manures derived from the following diets: corn and soymeal (CS); 85% CS diet+15% wheat meal (TR); CS diet+100ppm doxycycline+50ppm colistin+2500ppm Zn oxide (CSa); TR diet+100ppm doxycycline+50ppm colistin+2500ppm Zn oxide (TRa). Manures were tested in two subtropical soils representative of southern (Oxisol and Entisol). Despite the antibiotics no significant differences were found between the four manures within each soil. However, strong differences were found on the toxicity between soils. In Oxisol, LC50 values were around 100m3ha−1, and EC50 values around 80m3ha−1. In Entisol these were much lower, with LC50 values oscillating around 20m3ha−1 and EC50 values between 10–15m3ha−1. The observed toxicity on both soils was attributed to excess of nitrogen, Cu and Zn in the highest doses. The strong difference between soils could be explained by soil properties, namely CEC, organic matter, and clay contents that were lower in Entisol, indicating a poor ability to retain contaminants increasing their availability in soil. Results suggest that the application of these residues should be regulated not only using a volume-based criterion, but should incorporate data on soil properties, complemented by an ecotoxicological assessment.

Effect of activated carbon or biochars on toxicity of different soils contaminated by mixture of native polycyclic aromatic hydrocarbons and heavy metals.

Activated carbon (AC), biochar from wheat straw (BCS), and biochar from willow (BCW) were added to the soils sampled from areas of strong anthropogenic influence at doses of 0.5%, 1%, 2.5%, or 5% (w/w) and incubated for 2 mo. At the end of this period, the toxicity of the soils was measured. The effect of AC and biochars on the toxicity of the soils varied based on soil, type of amendment, dose, and test organism. For most of the parameters tested, the highest effectiveness of AC in terms of reduction of toxicity was observed in soil POPI (from bitumen processing plant area). In the case of the remaining soils, after the addition of AC varied results were observed, in which a reduction or an increase of toxicity, relative to the control soil, occurred. As in the case of AC, biochars also caused a significant reduction of phytotoxicity of soil POPI. In soils KB (from coking plant area, industrial waste deposit) and KOK (from coking plant area, coking battery), the reduction or increase of toxicity depended on biochar dose. Compared with the biochars, the effectiveness of AC in the reduction of toxicity depended also on soil, type of amendment, dose, and test organism. Generally, the AC was more effective than biochars in relation to mortality and reproduction of Folsomia candida (in all soils) and for reduction of luminescence inhibition of Vibrio fischeri (in POPI soil).

Efeito de Herbicidas sobre a Biota de Invertebrados do Solo em Área de Restauração Florestal

RESUMO O controle químico de plantas daninhas é um método eficaz utilizado em florestas plantadas e em áreas de restauração florestal, favorecendo o desenvolvimento das mudas florestais e a redução dos custos de intervenção. Entretanto, se essa estratégia não for aplicada de maneira correta, pode-se tornar um potencial causador de impactos negativos aos organismos do solo e aos processos ecológicos que esses participam. Avaliou-se o efeito do uso de herbicidas na biota do solo por meio da amostragem da comunidade da fauna edáfica e testes ecotoxicológicos de reprodução e sobrevivência de Folsomia candida eEnchytraeus crypticus, em área-alvo de restauração florestal recém-implantada. O delineamento experimental adotado foi de blocos casualizados com quatro tratamentos e cinco repetições. Os tratamentos consistiram da aplicação dos herbicidas pós-emergentes mesotrione (0,4 L ha-1), fluazifop-P-butyl (1,0 L ha-1) e nicosulfuron (1,5 L ha-1), aplicados em área total nas parcelas, mais o controle (sem aplicação). Na área de estudo, foram realizadas duas aplicações dos herbicidas com intervalos de seis meses, onde as parcelas foram correspondentes aos tratamentos em ambas as aplicações. Em cada parcela, foram realizadas quatro coletas de solo, sendo a primeira (coleta 1) seis dias antes da segunda aplicação dos herbicidas na área. As demais, após um (coleta 2), oito (coleta 3) e 22 dias (coleta 4) dessa mesma aplicação. A comunidade da fauna do solo foi avaliada por meio do método de funis de Berlese modificado, utilizando-se uma amostra de solo por parcela. Em laboratório, os indivíduos foram contados e identificados em grandes grupos. Os ensaios ecotoxicológicos de sobrevivência e reprodução de F. candida e E. crypticus foram realizados a partir de uma amostra composta de solo por tratamento. Um dia após a aplicação do herbicida mesotrione, verificou-se diminuição da riqueza média nos índices Shannon Weaver e Pielou e na reprodução de E. crypticus. Concluiu-se que a dupla aplicação dos herbicidas fluazifop-P-buthyl e nicosulfuron, nas respectivas doses de 1,0 e 1,5 L ha-1, não promoveu impactos negativos para os invertebrados do solo. Os efeitos negativos apresentados pelo mesotrione, mesmo que temporários, remeteu a uma ponderação sobre o uso desse em áreas de restauração florestal.

Collembolan reproduction in soils from a long-term fertilisation experiment opposes the Growth Rate Hypothesis

The Growth Rate Hypothesis (GRH) predicts better performance of fast-reproducing species in environments with increased P content. Thus far, most studies were performed in aquatic ecosystems; only few studies focused on soil ecosystems. In this study, soils from a long-term experiment (Static Fertilization Experiment, Bad Lauchstädt, Germany) that differ in P content by the factor 3 were used. We tested the influence of NPK fertilised, PK fertilised and unfertilised soils on the reproduction of Folsomia candida. In order to evaluate the effect of unit size, we compared the collembolan reproduction test as recommended by the OECD (large unit) with a recently introduced miniaturized version (small unit). Furthermore, the tests were combined with a predator–prey relationship using the gamasid mite Hypoaspis aculeifer. Even though significant differences between soils were found, reproduction was lowest at highest P content, which contradicts the GRH. In addition, predation and unit size had a strong influence on the reproduction. Both unit sizes proved feasible in predator–prey experiments, with stronger effects of mites on reproduction in the small unit due to higher relative predator density.

The variability of standard artificial soils: Effects on the survival and reproduction of springtail (Folsomia candida) and potworm (Enchytraeus crypticus)

Recent studies have documented significant variability in the basic properties of artificial soil which is used as a standard medium in soil bioassays. Variability in key soil properties could confound the interpretation of toxicity data and bias the output of bioassays. The main aims of this study were (i) to identify the variability in the endpoints survival and reproduction of Folsomia candida and Enchytraeus crypticus related to the artificials soils prepared in different laboratories and (ii) to identify the specific physico-chemical properties of the artificial soils which influence the bioassays results. The results of reproduction tests showed that nearly all tested artificial soils were suitable for the survival and reproduction of both organisms as the validity criteria from the test standards were fulfilled. However, numbers of juveniles varied significantly among soils. The most important factor for F. candida performance was a coarser soil structure. C:N ratio (<22.6) were important for the reproduction of E. crypticus. Both species tolerated a pH (KCl) of artificial soils in the range of 4.27–6.8 and even low TOC (1.5%). Thus, it is possible to reduce peat content in artificial soils, which may increase the comparability of results to those for natural soils.