Leaching potential and forms of phosphorus in deep row applied biosolids underlying hybrid poplar

Biosolids deep row incorporation (DRI) offers an alternative recycling approach for bioenergy crop production, but phosphorus additions in excess of the vegetation requirements can potentially impair water quality. The effects of DRI of anaerobically digested (AD) and lime-stabilized (LS) biosolids at four rates (213, 426 Mg ha⁻¹ for AD and 328, 656 Mg ha⁻¹ for LS) and a single rate of conventional P fertilizer on leaching of PO₄-P, and TKP were investigated in a hybrid poplar plantation in a coastal plain heavy mineral mine reclamation site. The effects of AD and LS biosolids aging on the transformations and losses of P applied with the biosolids were also studied. Zero tension lysimeters were installed at the site to collect leachate. Samples were collected at least monthly for 30 months between July 2006 and December 2008. We also analyzed biosolids P (labile P, Al-, Fe-bound-P, Ca-bound-P, total P, Mehlich 1 P) fractions. The loss of P was determined and P binding constituents were described via regression analysis. Orthophosphate and TKP from the DRI biosolids leached in negligible amounts, and were similar to leaching from conventional P fertilization. Most of the P was Al- and Fe-bound in the AD biosolids and Ca-bound in the LS biosolids. Labile P decreased with decrease in organic C, which indicated that P leaching potential from the DRI biosolids decreased with aging. Our results indicated that P mobility from biosolids of the type used should not pose a water quality risk.     

Differential field response of two Mediterranean tree species to inputs of sewage sludge at the seedling stage

Land degradation and desertification is a common feature in Mediterranean landscapes due to extensive and intensive land use and natural or man induced disturbances. The ecosystem may need external inputs to recover its composition and function as soils are often impoverished and vegetal key stone species lost. We evaluated the effects of the application of fresh and air-dried biosolids in the establishment and morphological and physiological performance of seedlings of Pinus halepensis and Quercus ilex under dry Mediterranean field conditions. Seedling survival was not affected by biosolid treatments in any of the studied species both two and ten years after planting. During the first two years, growth was enhanced by the two biosolid treatments in relation to control, although the change in the biomass allocation pattern differed between species. Rooting depth was significantly enhanced by liquid biosolid in Q. ilex and marginally reduced in P. halepensis as well as the exploration of soil. As a consequence, root-to-shoot ratio reduced significantly with dry and liquid sludge due to promoted aboveground growth while maintaining and even reducing belowground fractions. An improvement of the nutritional status, of fertilized seedlings especially of phosphorus, is the explanation for the better field performance. Vector analysis revealed an important phosphorus limitation for both species that was overcome with the application of liquid (both species) and air-dried biosolid (pine). The higher growth of pine seedlings attained in the liquid biosolid treatment was coupled with a significant decrease in foliar δ¹³C, suggesting lower water use efficiency. The significant increase in foliar δ¹⁵N in the biosolid treatments in both species suggested that a large proportion of the total nitrogen uptake came from the applied biosolids. Instead, with regard to the low biosolid application rate used in the study, treatments had an overall positive effect as a restoration tool by improving nutritional status and promoting growth of planted seedlings.     

Fe enriched biosolids as fertilizers for orange and peach trees grown in field conditions

Iron enriched biosolids (FEB) from water treatment facilities are being used as an alternative to synthetic chelates in order to improve Fe uptake. The impact of this type of products on iron nutrition is not fully understood. Plant response depends on FEB composition, soil and climatic conditions and crop response. In order to study the effectiveness of FEB as fertilisers, two field experiments have been carried out. Two different commercial formulations of FEB (unmodified u-FEB and modified m-FEB) produced as a by-product of a drinking water treatment facility in Tampa (Florida, USA) were used. An orange tree (Citrus sinensis, cv. Navelina) and a peach tree (Prunus persica cv. Sudanell) field experiments took place in different locations in Spain. Macro and micronutrients were evaluated to assess mineral status of orange and peach leaf samples. Yield and fruit size were also determined. Despite the large amount of Fe bound by the organic matter on FEB, these products were less effective than synthetic chelates to improve iron uptake. No differences were found in orange yield or size. Results show that the ferric treatments improve fruit calibre, but not yield in peaches.     

Advanced mine restoration protocols facilitate early recovery of soil microbial biomass,activity and functional diversity

Many ecosystem restoration programmes can take over 15 years to achieve ecosystem functioning comparable to that of an unmodified ecosystem, therefore a reliable shorter-term method of assessing and monitoring ecosystem recovery is needed to ensure that recovery is following an appropriate trajectory. Soil microbes respond to environmental change relatively quickly, and shifts in microbial communities can reflect the current status of their environment. As well as potentially acting as ‘indicator communities’, microbes play an integral role in restoring ecosystem functions. On an active opencast mine on New Zealand's West Coast, three main restoration methods are used, differing in cost and restoration effort. They range from most expensive (1) vegetation direct transfer (VDT), to (2) biosolids-amended stockpiles that are spread and replanted, and (3) untreated stockpiles that are spread and replanted. We assessed the impacts of these methods on soil microbial communities by measuring microbial biomass, dehydrogenase activity, community level physiological profile (CLPP) and functional diversity as measured by carbon substrate utilisation, where restored sites were 5 years old or less. These measures were compared to an unmodified reference ecosystem in the same location. Microbial activity and biomass were highest in pristine habitats, followed by VDT and biosolids-amended soils, then untreated stockpile soil. When compared to all other treatments untreated stockpiled soils had significantly different CLPPs and significantly reduced microbial biomass and activity; microbial biomass was an order of magnitude lower than in pristine soils. Functional diversity and richness did not differ between pristine, VDT and biosolids-amended soils, but were higher than in untreated stockpiled soils. CLPPs did not differ between pristine habitat soil and VDT soil but biosolids-amended and untreated stockpiled soils were significantly different to pristine soil. This study has shown that soil microbial communities are a valuable tool to assess restoration progress, and that ecosystem restoration can begin in a relatively short time following investment in appropriate restoration strategy, ultimately benefiting recolonisation by plants and animals.     

Accumulation and partitioning of biomass,nutrients, and trace elements in switchgrass for phytoremediation of municipal biosolids

In situ phytoremediation of municipal biosolids is a promising alternative to the land spreading and landfilling of biosolids from end-of-life municipal lagoons. Accumulation and partitioning of dry matter, nitrogen (N), phosphorus (P), and trace elements were determined in aboveground biomass (AGB) and belowground biomass (BGB) of switchgrass (Panicum virgatum L.) to determine the harvest stage that maximizes phytoextraction of contaminants from municipal biosolids. Seedlings were transplanted into 15-L plastic pails containing 3.9 kg (dry wt.) biosolids. Biomass yield components and contaminant concentrations were assessed every 14 days for up to 161 days. Logistic model fits to biomass yield data indicated no significant differences in asymptotic yield between AGB and BGB. Switchgrass partitioned significantly more N and P to AGB than to BGB. Maximum uptake occurred 86 days after transplanting (DAT) for N and 102 DAT for P. Harvesting at peak aboveground element accumulation removed 5% of N, 1.6% of P, 0.2% of Zn, 0.05% of Cd, and 0.1% of Cr initially present in the biosolids. These results will contribute toward identification of the harvest stage that will optimize contaminant uptake and enhance in situ phytoremediation of biosolids using switchgrass.     

The effect of acid pretreatment on the anaerobic digestion and dewatering of waste activated sludge

Waste activated sludge (WAS) is difficult to degrade in anaerobic digestion systems and pretreatments have been shown to speed up the hydrolysis stage. Here the effects of acid pretreatment (pH 6-1) using HCl on subsequent digestion and dewatering of WAS have been investigated. Optimisation of acid dosing was performed considering digestibility benefits and level of acid required. Pretreatment to pH 2 was concluded to be the most effective. In batch digestion this yielded the same biogas after 13 days as compared to untreated WAS at 21 days digestion. In semi-continuous digestion experiments (12 day hydraulic retention time at 35 °C) it resulted in a 14.3% increase in methane yield compared to untreated WAS, also Salmonella was eradicated in the digestate. Dewatering investigations suggested that the acid pretreated WAS required 40% less cationic polymer addition to achieve the same cake solid content. A cost analysis was also carried out.     

Sludge dewatering and stabilization in drying reed beds: Characterization of three full-scale systems in Catalonia,Spain

Optimization of sludge management can help reducing sludge handling costs in wastewater treatment plants. Sludge drying reed beds appear as a new and alternative technology which has low energy requirements, reduced operating and maintenance costs, and causes little environmental impact. The objective of this work was to evaluate the efficiency of three full-scale drying reed beds in terms of sludge dewatering, stabilization and hygienisation. Samples of influent sludge and sludge accumulated in the reed beds were analysed for pH, Electrical Conductivity, Total Solids (TS), Volatile Solids (VS), Chemical Oxygen Demand, Biochemical Oxygen Demand, nutrients (Total Kjeldahl Nitrogen (TKN) and Total Phosphorus (TP)), heavy metals and faecal bacteria indicators (Escherichiacoli and Salmonella spp.). Lixiviate samples were also collected. There was a systematic increase in the TS concentration from 1–3% in the influent to 20–30% in the beds, which fits in the range obtained with conventional dewatering technologies. Progressive organic matter removal and sludge stabilization in the beds was also observed (VS concentration decreased from 52–67% TS in the influent to 31–49% TS in the beds). Concentration of nutrients of the sludge accumulated in the beds was quite low (TKN 2–7% TS and TP 0.04–0.7% TS), and heavy metals remained below law threshold concentrations. Salmonella spp. was not detected in any of the samples, while E. coli concentration was generally lower than 460 MPN/g in the sludge accumulated in the beds. The studied systems demonstrated a good efficiency for sludge dewatering and stabilization in the context of small remote wastewater treatment plants.     

Nutritional status of different biosolids and their impact on various growth parameters of wheat (Triticum aestivum L.)

Biosolids can be effectively recycled and applied as soil amendments for agricultural crops because they contain several important micro and macronutrients including nitrogen, phosphorus, potassium, manganese. In the current study, we evaluated the effectiveness of seven biosoilds on different growth parameters of wheat crop. The biosolids used were lime stabilized, composted, liquid mesophilic anaerobically digested (liquid MAD), thermally dried mesophilic anaerobically digested (thermally dried MAD), thermally hydrolyzed mesophilic anaerobically digested (thermally hydrolysed MAD), dewatered mesophilic anaerobically digested (dewatered MAD) and thermally dried raw biosolids. We also analysed biosolids for their nutrient contents before application. The results revealed that different types of biosolids differed in nitrogen and phosphorous contents with highest contents observed in dewatered (5.70% nitrogen, 2.32% phosphorous) and liquid biosolids (2.35% phosphorous). The plant height, plant diameter and dry weight yield of wheat was increased with the increase in concentrations of biosolids. Liquid MAD resulted in maximum plant height of 120.35 ± 3.23, 133.2 ± 3.67 and 147.25 ± 3.11 at 3.33, 6.66 and 9.99 tons/ha concentration. The highest plant diameter was recorded (1.05–1.45 cm) where mineral nitrogen was applied. The study will be helpful in replacing the synthetic fertilizer with biosolids to fulfil the nutritional requirements of agricultural crops.     

Increasing the solubility and degradability of food processing biosolids

Biosolids (BS) from food processing plants are usually put on land or in landfills. They contain nutrients and could be fed to animals, but low digestibility is a limitation. Lab tests were conducted to evaluate treatments that might increase digestibility of BS.

Biosolids were extruded or treated with chemicals and filtered; residues were incubated with proteases. Dry matter disapperance (DMD), measured as weight loss of treated material following filtration, was considered an indicator of digestibility.

The DMD of extruded BS (31–35%) was greater than oven-dried BS (20–27%). Increasing extruder temperature or speed increased DMD by small but significant amounts. Chemical treatment of BS with HCL, AP and NaOH significantly increased DMD to 60–70%; increases were larger than responses to extrusion. Responses were attained differently; on one hand, for HCL and AP treatments, about 50% of the increase in DMD was due to solubilization and 50% due to degradation. On the other hand, NaOH acted almost completely by solubilization. Increased DMD infers that BS should have increased digestibility when fed to animals, but feeding studies are needed for substantiation.     

Molecular pathogen detection in biosolids with a focus on quantitative PCR using propidium monoazide for viable cell enumeration

Sewage sludge is the solid, organic material remaining after wastewater is treated and discharged from a wastewater treatment plant. Sludge is treated to stabilize the organic matter and reduce the amount of human pathogens. Once government regulations are met, including material quality standards (e.g., E. coli levels and heavy metal content) sludge is termed “biosolids”, which may be disposed of by land application according to regulations. Live-culture techniques have traditionally been used to enumerate select pathogens and/or indicator organisms to demonstrate compliance with regulatory requirements. However, these methods may result in underestimates of viable microorganisms due to several problems, including their inability to detect viable but non-culturable (VBNC) cells. Real-time quantitative polymerase chain reaction (qPCR) is currently under investigation as a fast, sensitive, and specific molecular tool for enumeration of pathogens in biosolids. Its main limitation is that it amplifies all target DNAs, including that from non-viable cells. This can be overcome by coupling qPCR with propidium monoazide (PMA), a microbial membrane-impermeant dye that binds to extracellular DNA and DNA in dead or membrane-compromised cells, inhibiting its amplification. PMA has successfully been used to monitor the presence of viable pathogens in several different matrices. In this review the use of PMA-qPCR is discussed as a suitable approach for viable microbial enumeration in biosolids. Recommendations for optimization of the method are made, with a focus on DNA extraction, dilution of sample turbidity, reagent concentration, and light exposure time.