Biosolids-amended Soils Research Articles

Effect of silver nanoparticle contaminated biosolids on the soil microbial community

This study investigated the effects of AgNPs on soil microbial communities when biosolids, containing AgNPs, were amended into soil. A field-collected sandy loam soil was amended with biosolids containing aged, PVP-coated AgNPs at measured concentrations of 3, 48, 123, 290 and 706 mg Ag kg−1 of soil (dry weight). The control treatment consisted of soil without AgNPs (Con-0) but amended with biosolids. An additional treatment of Ag+ (AgNO3) at 138 mg Ag kg−1 was included as appropriate. The AgNPs were aged in biosolids for 72 h before being spiked into soil. The impact of aged-AgNPs on the in-situ soil microbial community was assessed using a suite of microbial tests that assessed the effects on microbial growth, biomass, activity and diversity. The extractable Ag+ in AgNPs spiked soils increased with increasing AgNP concentrations and ranged from <0.1 to 3.38 mg Ag+ kg−1 soil. The extractable Ag+ in the AgNO3 treatment (i.e., 138 mg Ag kg−1) was 5 times lower than the comparable AgNP treatment (i.e., 123 mg Ag kg−1). A significant impact of AgNPs on the soil microbial community was observed with median inhibitory concentrations (IC50) ranging from 11 to >706 mg Ag kg−1. AgNP treatments showed a 10–64% reduction in microbial activities than the AgNO3 treatment at a similar total Ag concentration. The toxicity of AgNPs were more pronounced overtime, suggesting that Ag+ continued to be released from biosolid-aged AgNPs in the soil environment and likely contributed to the observed toxicity. Emergence of a silver tolerant bacterium (Rhodanobacter sp.) was observed in soils with low to moderately high AgNP concentrations (48 to 290 mg Ag kg−1). Our results suggest that AgNP exposure in soil amended with biosolids may have significant inhibitory effects on the soil microbial community despite their potential sulfidation in biosolid-amended soils.

Changes in soil microbial community structure following amendment of biosolids for seven years

ABSTRACTThe environment-friendly disposal approaches for sewage sludge remain a challenge worldwide, and agricultural application of the treated sewage sludge, i.e. biosolids, as soil conditioner and nutrient source for plants, is still one of the most promising options for dealing with the waste. In this study, we compared the effects of long-term applications of biosolids and mineral fertilizer on soil microbial community using phospholipid fatty acid profiles in an agricultural field. The microbes predominant in the mineral fertilizer soil remained the most abundant in the biosolids-amended soil. Bacterial and fungal communities presented downtrends in both absolute and relative amounts; however, percentage of Gram-positive bacteria remained unchanged. Soil pH displayed significant negative correlations with microbial communities and explained 64%, 56% and 44% of the variances in microbial biomass, bacteria and fungi, respectively, while soil NO3–-N was positively correlated with microbial biomass, bacteria and fungi (r2 = 0.53, 0.51 and 0.54, respectively).

One-time application of biosolids to ungrazed semiarid rangelands: 14 yr soil responses

Biosolids have been shown to improve forage production and soil quality on semiarid rangelands in the short term, but less is known about longer-term impacts of one-time biosolids applications. The objective of this study was to determine the effects of a single, surface biosolids application (at 20 dry Mg ha−1) on stability of soil aggregates, bulk density, total carbon (C) and nitrogen (N), permanganate-oxidizable carbon (POXC), polysaccharides, pH, nutrient availability, and soil water content (all at 0–7.5 cm depth) 14 yr following application to ungrazed rangelands in the Central interior of British Columbia. Fourteen years following the biosolids application, aboveground plant biomass was almost two times greater with biosolids application than on control, while exposed mineral soil and microbiotic crust significantly decreased in biosolids plots. Despite differences in aboveground biomass, there was no difference in total soil C and N, POXC, and polysaccharides between biosolids and control plots. Biosolids-amended soil did exhibit significantly greater mean weight diameter of water-stable aggregates, lower pH, increased spring soil water content, and increased availability of Fe3+, Zn2+, Cu2+, and phosphate ions. These findings indicate that the long-term improvements to soil on ungrazed rangeland are possible even from a single biosolids application.

Growth and metal uptake of edamame [Glycine max (L.) Merr.] on soil amended with biosolids and gypsum

ABSTRACT Although biosolids are a rich source of plant nutrients, there is concern about the potential heavy metal uptake by crops grown on biosolid-amended soils. This study was conducted to determine the effects of limed or composted biosolids and flue gas desulfurization gypsum (FGDG) on edamame growth, nodule development, and metal uptake. Two consecutive crops of edamame were grown on 40 and 80 T ha−1 biosolid-amended soil with and without 10 T ha−1 FGDG. Biosolids with or without FGDG did not reduce biomass, nodules, or grain yields in the first harvest and increased yields of all three tissues in the second harvest. Lead and cadmium concentrations in grain and biomass were below the instrument detection limits. Copper, manganese, and zinc were within the ranges normally found in soybean grain. In this pot study, biosolids and FGDG did not reduce edamame growth or increase grain metal concentrations to levels of concern.

Sorption and mobility of metformin and guanylurea in soils as affected by biosolid amendment: Batch and column tests

Recent classification of metformin as an emerging contaminant warrants assessment of its fate and behaviour in the natural environment especially with land-based application of potentially contaminated wastewaters and biosolids. The present study provided further insight into the sorption mechanisms of metformin and its transformation product guanylurea in soil and upon biosolid fortification. Decreased metformin sorption (12.4%) as measured by the effective distribution coefficient (Kdeff) was observed with biosolids amendment while significant increase (2500%) in guanylurea sorption was calculated. Analysis of co-solute effects confirmed their contrasting sorption mechanisms with the absence of competitive effects in unamended soil. Results of the column tests were in good agreement with the batch sorption studies as the fitted values of retardation factors decreased and increased for metformin and guanylurea, respectively, upon addition of biosolids. The shapes of the breakthrough curves suggest slower desorption rates for both compounds in unamended soil resulting to non-equilibrium conditions and back-end tailings. However, in biosolid-amended soil columns, these tailings were less pronounced resembling equilibrium transport. Results also demonstrated enhanced mobility of both compounds upon biosolids fortification. The non-equilibrium chemical transport model fitted the measured data well (0.975 > r2 > 0.988) especially for unamended soils which suggests the existence of non-equilibrium conditions and rate-limited sorption sites.

An integrated approach to highlight biological responses of Pisum sativum root to nano-TiO2 exposure in a biosolid-amended agricultural soil

This study focused on crop plant response to a simultaneous exposure to biosolid and TiO2 at micro- and nano-scale, being biosolid one of the major sink of TiO2 nanoparticles released into the soil environment. We settled an experimental design as much as possible realistic, at microcosm scale, using the crop Pisum sativum. This experimental design supported the hypotheses that the presence of biosolid in the farming soil might influence plant growth and metabolism and that, after TiO2 spiking, the different dimension and crystal forms of TiO2 might be otherwise bioavailable and differently interacting with the plant system. To test these hypotheses, we have considered different aspects of the response elicited by TiO2 and biosolid at cellular and organism level, focusing on the root system, with an integrative approach. In our experimental conditions, the presence of biosolid disturbed plant growth of P. sativum, causing cellular damages at root level, probably through mechanisms not only oxidative stress-dependent but also involving altered signalling processes. These disturbances could depend on non-humified compounds and/or on the presence of toxic elements and of nanoparticles in the biosolid-amended soil. The addition of TiO2 particles in the sludge-amended soil, further altered plant growth and induced oxidative and ultrastructural damages. Although non typical dose-effect response was detected, the most responsiveness treatments were found for the anatase crystal form, alone or mixed with rutile. Based on ultrastructural observations, we could hypothesise that the toxicity level of TiO2 nanoparticles may depend on the cell ability to isolate nanoparticles in subcellular compartments, avoiding their interaction with organelles and/or metabolic processes.The results of the present work suggest reflections on the promising practice of soil amendments and on the use of nanomaterials and their safety for food plants and living organisms.

Retention-release of ciprofloxacin and azithromycin in biosolids and biosolids-amended soils

Ciprofloxacin (CIP) and azithromycin (AZ) are commonly prescribed antibiotics, often found at elevated concentrations in treated sewage sludge (biosolids), and could pose human and ecological risks when land applied. Limited retention-release data preclude assessing potential risks from the target antibiotics in biosolids and biosolids-amended soils. The present work assessed sorption-desorption of CIP and AZ in biosolids and biosolids-amended soils using the “traditional” batch equilibration method. The batch equilibration method also included un-amended soils for comparison. Release potentials of the biosolids-borne antibiotics were assessed via multiple desorption equilibrations in the presence of CaCl2, soils, PbCl2, or competing antibiotic (CIP versus AZ) solutions. Desorption kinetics of CIP from biosolids were also evaluated by the diffusive gradient in thin films technique (DGT), coupled with a diffusion transport-exchange model available in 2D-DIFs. Sorption of both antibiotics followed linear models with partitioning coefficient (Kd) values for CIP ranging between 40 and 334 L kg−1 in soils and 357 L kg−1 in biosolids, and values for AZ ranging between 11 and 202 L kg−1 in soils and 428 L kg−1 in biosolids. Antibiotic desorption from the biosolids was highly hysteretic (hysteresis coefficients < 0.003) and desorption of the biosolids-borne chemicals was extremely small (<3%) using any of the various desorption equilibration approaches. Desorption was hysteric in soils too; where desorption percentages were 4, 5, and 26% for CIP and 6, 32, and 50% for AZ in the silt loam soil, manured sand, and sand, respectively. CIP release from biosolids determined by DGT was also small (<1%), ascribed to low dissolved and labile concentrations in the solid phase and a small effective diffusion coefficient. Results obtained using equilibrium and dynamic approaches suggest that the target antibiotic bioaccessibilities from biosolids and finer-textured (typical agricultural) soils would be minimal and that biosolids (not soils) control desorption of the two biosolids-borne chemicals.

Plant toxicity and accumulation of biosolids-borne ciprofloxacin and azithromycin

Trace organic chemicals (TOrCs) in land applied biosolids can cause phytotoxicities and contaminate human and animal food chains. Information on phytotoxicity and phytoaccumulation of environmentally relevant concentrations of two antibiotic TOrCs, ciprofloxacin (CIP) and azithromycin (AZ), from biosolids-amended soils is limited. Greenhouse studies were conducted to assess the plant toxicity and accumulation of a range of environmentally relevant concentrations of biosolids-borne CIP and AZ in biosolids-amended soils. Separate studies assessed phytotoxicity potential of soil-borne CIP and AZ (soils directly spiked with the target antibiotics without biosolids) at concentrations much greater than those of environmental relevance in biosolids-amended soils. Both the biosolids-borne and the soil-borne antibiotic studies involved three plants (radish (Raphanus sativus), lettuce (Lactuca sativa), and tall fescue grass (Festuca arundinacea)) of different morphologies, physiologies, and chemical exposure scenarios. Phytotoxicity and phytoaccumulation from the biosolids-borne antibiotics were minimal at environmentally relevant concentrations, even in sand. The separate phytotoxicity experiments involving the soil-borne antibiotics revealed no observed adverse effect concentration (NOAEC) of 3.2 mg kg−1 (AZ) and 36.1 mg kg−1 (CIP) for the three plants grown in soils mimicking typical agricultural soils. These NOAEC values are about 100-fold greater than the antibiotic concentrations expected in biosolids-amended soils. NOAEC values under an unrealistic worst-case where the antibiotics were directly spiked to sand (NOAEC = 3.2 mg kg−1 for AZ; and ≥0.36 mg kg−1 for CIP) were also greater than the environmentally relevant concentrations of the biosolids-borne antibiotics. The results suggest that land application of biosolids-borne CIP and AZ pose De minimis risks to plants. Point estimates of plant bioaccumulation factors (dry weight basis) were 0.01 (CIP) and 0.1 (AZ), suggesting minimal impacts of the target TOrCs on human and/or animal food chains.

Sources and Fate of Cyclic Phenylmethylsiloxanes in One Municipal Wastewater Treatment Plant and Biosolids-Amended Soil

cis-/ trans-2,4,6-Triphenyl-2,4,6-trimethylcyclotrisiloxanes ( cis-P3 and trans-P3) and cis-/ trans-2,4,6,8-tetraphenyl-2,4,6,8-tetramethylcyclotetrasiloxanes ( cis-P4 and trans-P4a,b,c) were detected in personal care products [<LOD-54.2 μg/g, detection frequencies (df) = 14.5-15.5%, n = 110] collected from a Chinese city, suggesting their potential release to local municipal wastewater treatment plant (WWTP). In the local WWTP, per capita mass loadings of P3 and P4 were 43.4-340 μg/d in influents, while neither P3 nor P4 was detected in effluents. Due to large solid/water distribution coefficients (apparent Log Kd = 3.42-3.99), sorption to sludge had a dominant contribution (95.6-99.2%) to phenylmethylsiloxanes removal in the WWTP. As amended by biosolids containing phenylmethylsiloxanes [66.2 ng/g to 2.63 μg/g dw (dry weight)] from this WWTP, concentrations (<LOD -255 ng/g dw, df = 27.5-52.5%, n = 120) of six phenylmethylsiloxane isomers in soils from one commercial forest were significantly higher than those (<LOD) in the reference area without biosolids application, but no increasing trend was found at six sampling events during July 2015 to February 2017. Simulated experiments indicated that hydrolysis half-lives of phenylmethylsiloxanes (1.50-6.50 d for P3, 16.5-65.4 d for P4) in soil were 4.74-46.3 times shorter than volatilization half-lives (51.9-120 d for P3, 158-376 d for P4). For both cyclic phenylmethylsiloxanes, their trans-isomers had lower (1.14-1.82 times) degradation rates than their cis-isomers.

Effects of Biochar and Biosolid on Adsorption of Nitrogen, Phosphorus, and Potassium in Two Soils

Increasing the retention of nutrients by agricultural soils is of great interest to minimize losses of nutrients by leaching and/or surface runoff. Soil amendments play a role in nutrient retention by increasing the surface area and/or other chemical processes. Biochar (BC) is high carbon-containing by-product of pyrolysis of carbon-rich feedstocks to produce bioenergy. Biosolid is a by-product of wastewater treatment plant. Use of these by-products as amendments to agricultural soils is beneficial to improve soil properties, soil quality, and nutrient retention and enhance carbon sequestration. In this study, the adsorption of NH4-N, P, and K by a sandy soil (Quincy fine sand (QFS)) and a silty clay loam soil (Warden silty loam (WSL)) with BC (0, 22.4, and 44.8 mg ha−1) and biosolid (0 and 22.4 mg ha−1) amendments were investigated. Adsorption of NH4-N by the QFS soil increased with BC application at lower NH4-N concentrations in equilibrium solution. For the WSL soil, NH4-N adsorption peaked at 22.4 mg ha−1 BC rate. Biosolid application increased NH4-N adsorption by the WSL soil while decreased that in the QFS soil. Adsorption of P was greater by the WSL soil as compared to that by the QFS soil. Biosolid amendment significantly increased P adsorption capacity in both soils, while BC amendment had no significant effects. BC and biosolid amendments decreased K adsorption capacity by the WSL soil but had no effects on that by the QFS soil. Ca release with increasing addition of K was greater by the WSL soil as compared to that by the QFS soil. In both the soils, Ca release was not influenced by BC amendment while it increased with addition of biosolid. The fit of adsorption data for NH4-N, P, and K across all treatments and in two soils was better with the Freundlich model than that with the Langmuir model. The nutrients retained by BC or biosolid amended soils are easily released, therefore are readily available for the root uptake in cropped soils.

Environmental risk assessment of perfluoroalkyl substances and halogenated flame retardants released from biosolids-amended soils

Biosolid application is considered a sustainable management tool as it positively contributes to recycle nutrients and to improve soil properties and fertility. Nevertheless, this waste management technique involves an important input source of emerging organic pollutants in soil. To evaluate the environmental potential risk related to perfluoroalkyl substances (PFASs) and halogenated flame retardants (HFRs) due to the biosolid application to soil, a quantitative ecotoxicological risk assessment was conducted. The analyte concentrations were employed to perform an estimation of the exposure levels to contaminants in the receiving media, defining predicted environmental concentrations (PECs) for terrestrial and aquatic compartments (PECsoil, PECwater, PECsed) and for secondary poisoning via the terrestrial and aquatic food chain (PECoral, predator (T), PECoral, predator (Aq)). The risk characterization ratios (RCRs) were calculated based in the comparison of the PEC values obtained with concentrations with no effect (PNECs) on terrestrial and aquatic ecosystems. Based on the chosen scenarios and experimental conditions, no environmental risk of PFASs and HFRs released from biosolid amended soils to different environmental compartments was detected (RCRsoil, RCRoral, worm, RCRwater, RCRsed and RCRoral, fish were below 1 in all cases). Besides, the potential health risk of PFASs and HFRs to local people who live in the scenario studied and are fed on horticultural crops grown in biosolid amended soil was also below 1, indicating that the risk is not considered significant to human health in the conditions studied. This approach provides a first insight of the risks relative to biosolid amendments to further research based on fieldwork risk assessment.

Behavior of N-ethyl perfluorooctane sulfonamido acetic acid (N-EtFOSAA) in biosolids amended soil-plant microcosms of seven plant species: Accumulation and degradation

Perfluorooctane sulfonate (PFOS) precursors have been found extensively in sewage sludge and biosolids-amended soils. The degradation of these precursors are regarded as a significant source of PFOS in the environment. In this study, the accumulation of N-ethyl perfluorooctane sulfonamido acetic acid (N-EtFOSAA) in the plants of seven species, namely alfalfa, lettuce, maize, mung bean, radish, ryegrass, and soybean from biosolids-amended soil, and the degradation kinetics of N-EtFOSAA in soil-plant microcosms were evaluated over 60 days. N-EtFOSAA was found in the roots of all plant species, while was not in stems and leaves. The root concentration factors of N-EtFOSAA ranged 0.52–1.37 (pmol/groot)/(pmol/gsoil). Stepwise multiple regression analysis was used to elucidate the accumulation of N-EtFOSAA in the roots of plants. The results showed that the root protein and lipid contents explain 85.0% of the variation in root N-EtFOSAA levels (P < 0.05). Four degradation products, including N-ethyl perfluorooctane sulfonamide (N-EtFOSA), perfluorooctane sulfonamide acetate (FOSAA), perfluorooctane sulfonamide (FOSA) and PFOS were found in soils and plant roots, stems and leaves, indicating the degradation of N-EtFOSAA in soil-plant system. Degradation kinetics fitted a first-order kinetic model well. Degradation rate constants of N-EtFOSAA in the microcosms with plants ranged 0.063–0.165 d−1, which was 1.40–3.6 times higher than those without plants. Degradation rate constant of maize was relatively higher than those of other plant species. The results is the first to reveal N-EtFOSAA accumulation in plants and degradation in soil-plant microcosms.

Application of biosolids drives the diversity of antibiotic resistance genes in soil and lettuce at harvest

High-throughput quantitative polymerase chain reaction (PCR) of antibiotic resistance genes (ARGs) was used to profile the composition and diversity of ARGs in biosolid-amended soil and in lettuce roots and shoots. Biosolid application significantly increased the ARGs in soil and influenced the soil antibiotics resistome mainly through exogenous introduction. Four dominant ARGs occurred in sterilized and water-washed leaves, namely catB8, php, vanB and str, which accumulated to >50% of total abundance. Nine subclasses of ARGs were determined in both sterilized and water-washed leaves, and they were shared ARGs among soil, roots and shoots. This suggests that the ARGs in ready-to-eat lettuce were mainly located in endophytes and the internal route may contribute more to the ARGs in routinely consumed raw lettuce. Moreover, a previously unsuspected shift in multridrug ARGs to root and shoot compartments due to biosolid application was discovered. These results reveal that biosolid application drives the evolution and dissemination of ARGs in the soil-plant system.

Amendment of Agricultural Soil with Metal Nanoparticles: Effects on Soil Enzyme Activity and Microbial Community Composition.

Several types of engineered nanoparticles (ENPs) are being considered for direct application to soils to reduce the application and degradation of pesticides, provide micronutrients, control pathogens, and increase crop yields. This study examined the effects of different metal ENPs and their dissolved ions on the microbial community composition and enzyme activity of agricultural soil amended with biosolids. The activity of five extracellular nutrient-cycling enzymes was measured in biosolid-amended soils treated with different concentrations (1, 10, or 100 mg ENP/kg soil) of silver (nAg), zinc oxide (nZnO), copper oxide (nCuO), or titanium dioxide (nTiO2) nanoparticles and their ions over a 30-day period. At 30 days, nZnO and nCuO either had no significant effect on soil enzyme activity or enhanced enzyme activity. In contrast, Ag inhibited selected enzymes when dosed in particulate or dissolved form (at 100 mg/kg). nTiO2 either had no significant effect or slightly decreased enzyme activity. Illumina MiSeq sequencing of microbial communities indicated a shift in soil microbial community composition upon exposure to high doses of metal ions or nAg and negligible shift in the presence of nTiO2. Some taxa responded differently to nAg and Ag+. This work shows how metal ENPs can impact soil enzyme activity and microbial community composition upon introduction into soils amended with biosolids, depending on their type, concentration, and dissolution behavior, hence providing much needed information for the sustainable application of nanotechnology in agriculture.

Using nanoparticles from water treatment residuals to reduce the mobility and phytoavailability of Cd and Pb in biosolid-amended soils

Heavy metal pollution in soils amended with biosolids has been a serious problem worldwide for clean food production. Laboratory and greenhouse experiments were performed to assess the impact of water treatment residual nanoparticles (nWTRs), at different application rates (0.1, 0.2 and 0.3%), on immobilization and phytoavailability of Cd and Pb to canola (Brassica napus L.) plants in soils amended with biosolids spiked with three different rates of Cd or Pb. Application of nWTRs significantly increased the residual fractions of Cd and Pb in metal-spiked biosolid-amended soil and thereby increased the immobilization of Cd and Pb in the amended soil. The greatest immobilization of Cd and Pb was exhibited at an application rate of 0.3% nWTRs. In addition, the application of nanoparticles to the biosolid-amended soil significantly increased canola grain yield and significantly decreased Cd and Pb phytoavailability due to immobilization of Cd and Pb in the contaminated soil. The results demonstrate, for the first time, the capability of nanoscale WTRs in stabilizing heavy metals in contaminated soils and restoring degraded agricultural land.

Transfer of perfluorooctanesulfonate (PFOS), decabrominated diphenyl ether (BDE-209) and Dechlorane Plus (DP) from biosolid-amended soils to leachate and runoff water

Environmental contextThe potential of pollutants to migrate from biosolids must be considered when assessing the environmental risk associated with the application of biosolids in agriculture. We conducted semi-field tests simulating natural conditions to determine the leaching and runoff capacity of emerging organic contaminants following fortification and application of municipal biosolids. We demonstrate the transfer of pollutants from biosolid-amended soil to leachate and runoff water generated by natural rainfall. AbstractAnthropogenic perfluoroalkyl substances, PFASs, and halogenated flame retardants, HFRs, have been detected in different environmental compartments. In order to determine the fate of these compounds in the soil–water system, a semi-field simulated runoff experiment was conducted following the application of municipal organic waste. Therefore, the application of four biosolids was carried out. The biosolids were fortified with perfluorooctanesulfonate (PFOS; ~1 mg PFOS per kg biosolid), decabromodiphenyl ether (c-decaBDE; ~10 mg kg−1) and Dechlorane Plus (DP; ~0.26 mg kg−1) commercial mixtures and were applied to soil packed in 15 runoff-leaching trays (2.5 × 2 × 0.05 m). These trays were designed to collect the leachate and runoff water generated by natural rainfall. PFASs and HFRs were detected in leachate and runoff water from several rainfall events from November 2011 to May 2012 (a first rainfall event of 10.5 × 10−3 m, a second event of 16.0 × 10−3 m and a third pool event with a cumulative amount of 113.1 × 10−3 m) occurring after the initial biosolid application. The total mass distribution calculated in water samples showed a higher content in runoff samples (PFOS, 91 ± 2 %; BDE-209, 76 ± 17 %; DP, 83 ± 14 %). The order of the loamy sand soil affinity for PFOS, BDE-209 and DP was as follows: PFOS &lt; BDE-209 ≤ DP, which was predicted, either from the compounds’ water solubility, the octanol-water partition coefficient (Kow) or the organic carbon-water partition coefficient (Koc). The calculated leaching potential (Lp) index or the Groundwater Ubiquity Score (GUS), which are based on these Kocs, revealed the reverse order of potential transport to surface and groundwater respectively.

Determination of perfluoroalkyl acid isomers in biosolids, biosolids-amended soils and plants using ultra-high performance liquid chromatography tandem mass spectrometry.

Isomer-specific analysis of perfluoroalkyl acids (PFAAs) is important to accurately assess their environmental source, fate, and human risks. In this study, a method was developed for the determination of perfluorooctanoic acid (PFOA), perfluorooctane sulfonate (PFOS), and perfluorohexane sulfonate (PFHxS) isomers in biosolids, biosolids-amended soils and plants using ultra-high performance liquid chromatography-tandem mass spectrometry (UHPLC-MS/MS). The separation efficiencies of two chromatographic columns and extraction capacities of different methods were tested. Compared with the C18 column (ACQUITY UPLC BEH Shield RP18 column), the column with an alkyl perfluorinated C8 stationary phase (Epic FO LB column), in combination with the distinct MS/MS transitions of analytes, allowed better separation of most isomers. The ion-pair extraction method showed more effective matrix separation than that of the alkaline digestion method, with recoveries ranging from 79.6-105% for biosolids, 80.4-116% for soils, and 68.0-114% for plant tissues. The method detection limits ranged from 10 to 55, 3-13, and 8-58pg/g dry weight for biosolids, soil, and plants, respectively. This method was applied successfully to quantify individual isomers in biosolids, biosolids-amended soils and plants. Six PFOA, eight PFOS, and two PFHxS isomers were found in the samples, with linear isomers being the dominant species. Further analysis revealed that the translocation potentials of branched isomers within plants were higher than those of linear isomers.

Potential Use of Biosolids to Reforest Degraded Areas with New Zealand Native Vegetation.

Biosolids could potentially be used for reforestation of degraded soils in New Zealand with native vegetation. Many native plant species of New Zealand thrive in low-fertility soils, and there is scant knowledge about their nutrient requirements. Therefore, it is unclear whether they will respond positively to the addition of biosolids. We used a pot trial to determine the responses of 11 native plant species to biosolids addition (10% w/w, ∼90 Mg hm) on two distinct degraded soils, Lismore stony silt loam and a Kaikōura sand. We also intended to prove that the soil microbial activity improves with the addition of biosolids, depending on the plant species. All species grew better in Lismore stony silt loam than the Kaikōura sand. All species in the Lismore stony silt loam responded positively to biosolids. The response to biosolids addition in the Kaikōura sand was variable, with four species showing no improvement in growth when biosolids were added. The nutrient status (N, P, S, Cu, and Zn) of all species improved when the two soils were amended with biosolids. However, some plant species, especially Sol. ex Gaertn. and Raoul, showed concerning concentrations of Cd (up to 2.4 mg kg). Dehydrogenase activity of soils (indicator of soil microbial activity) increased in biosolids-amended soils, with a strong species effect. Future work should involve field trials to determine the effect of biosolids addition on the establishment of native plant communities.

The bioaccumulation of silver in Eisenia andrei exposed to silver nanoparticles and silver nitrate in soil

The bioaccumulation potential of silver from exposure to AgNO3 and Ag nanoparticles (AgNP) was investigated. In the first exposure, the bioaccumulation of Ag in Eisenia andrei was compared between AgNO3 (1.09mgAgkg−1 dry soil) and AgNPA (20nm, PVP-coated at 3.90mgAgkg−1 dry soil) when amended into a natural field soil. In a second experiment, AgNPB (40nm, PVP-coated) was added to biosolids, aged for 3 d, and then mixed into the field soil (77.95mgAgkg−1 dry soil). Results demonstrated very low bioaccumulation potential for all exposure scenarios, producing bioaccumulation factors (BAFk) of 0.89 and 0.74 for with AgNPA (20nm) and Ag+ (as AgNO3), respectively, in soil, and 0.12 AgNPB in biosolids-amended soil. Earthworms exposed to AgNPB in the biosolids-amended soil showed reduced tissue Ag concentrations following the 21-d elimination period compared to the earthworms from the AgNPA exposure in soil. Uptake of Ag into tissue was not related to the measureable Ag+ within test soil extracts, and evaluation of earthworm tissue via transmission electron microscopy (TEM) confirmed the presence of AgNP within exposed test organisms, despite differences in nanoparticle size, exposure concentrations and matrices between the tests. The growing evidence of accumulation of AgNP within test organisms warrant further long-term research efforts to evaluate the significance of the long-term fate and effects of AgNPs in general.

Speciation and fractionation of phosphorus in biosolids-amended soils: effects of water treatment residual nanoparticles

Phosphorus (P) speciation and fractionation are useful tools for assessing P mobility and potential transfer to water bodies. The current study aims to evaluate drinking water treatment residual nanoparticles (nWTRs) effects on P species in biosolids-amended soils using sequential chemical fractionation and mineral equilibrium model. Three different soil types were selected (El-Bostan, Kafr El-Dawar, Borg Al-Arab), amended with biosolids (3%), and different rates of nWTRs were applied. The P fractionation results revealed that addition of nWTRs to biosolids-amended El-Bostan soil increased the immobile aluminum phosphates from 27.30 to 88.90, 92.20, and 94.93% at 0.10, 0.20, and 0.30% application rate, respectively. Similar trend was noticed in Kafr El-Dawar soil. In Borg Al-Arab soil, nWTRs significantly (p < 0.05) increased aluminum phosphate to only 71.73% at the highest application rate (0.30%) due to its high content of calcium carbonate (35.70%). Similarly, phosphorous speciation analysis revealed that application of nWTRs significantly increased the proportions of immobile phosphate form (P sorbed to Al hydroxide) and amorphous sodium aluminum phosphate. Thus, water degradation via eutrophication can be minimized by applying nWTRs to biosolids-amended soils.