Abstract

Wastewater algal treatment systems show improved economic viability and enhanced energy return on investment if integrated with biofuel production. One option is to anaerobically digest the algae to generate bio-methane. This method is appropriate for relatively low lipid filamentous algae typical of turf scrubbers®. But unbalanced carbon-to-nitrogen (C/N) ratio and the resistance of algae to biodegradation can limit biomass conversion into bio-methane. To evaluate options to enhance bio-methane production, an indigenous assembly of macro-algae was established and cultivated in CO2-infused secondary wastewater effluent, then harvested and either anaerobically digested using pretreatments or co-digested with sewage sludge. Results were used to develop methane production kinetic models and perform an AD system energy balance analysis to assess the feasibility of pretreatment and co-digestion for a scaled process. Floways were dominated by Ulothrix and Oedogonium algae and had periphyton biomass production rates that averaged 3.7±0.4 g VS m-2 d-1 (±1SD) during the initial 7-day colonization period. Biomass increased by 62% in the second half of the 14-day experiment. Ultimate methane yield from harvested biomass was improved relative to controls (30613 mL gVS-1) through thermal pretreatment by 15%, dilute acid by 5%, dilute alkali by 17%, acid- and alkali-assisted thermochemical pretreatments by 23 and 27%, respectively. However, all pretreatment methods undermined the energy balance parameters including Net Energy Ratio (NER) and Net Energy Efficiency (NEE) due to the heat required for thermal pretreatments and electricity needed to produce chemical reagents. In contrast, co-digestion of algal biomass with sewage sludge enhanced methane generation yielding up to 4013 mL gVS-1 at algae to sludge ratio of 20% to 80%. Co-digestion with sludge also strongly improved AD system energy balance. NER and NEE increased from 2.8 and 73% for algae alone to 4.3 and 81% for a 20%:80% algae to sludge mix respectively. Moreover, the Net Energy Recovery during co-digestion reached 39% compared to 26% and 33% when algae or sewage sludge were processed as single-substrates. Thus, co-digestion of algae with sewage sludge serves as an attractive option for maximizing energy gain from AD of biomass harvested from filamentous algal treatment systems.

Highlights

  • Nutrient over-enrichment has resulted in the impairment of more than 189,000 km of rivers and 6,800 km2 of freshwater in the US (EPA, 2018)

  • Natural polycultures of benthic algae can be utilized to remove wastewater nutrients and their resulting biomass can serve as an affordable feedstock for bioenergy

  • While biomass pretreatment methods and co-digestion are often suggested as an effective means for improving algal biodegradation for enhanced biomethane production, they should be applied with caution due to their high requirement for additional energy inputs

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Summary

Introduction

Nutrient over-enrichment has resulted in the impairment of more than 189,000 km of rivers and 6,800 km of freshwater in the US (EPA, 2018). These nutrients cause eutrophication and contribute to the rise in harmful freshwater algal blooms (Heisler et al, 2008). Because wastewater effluent contributes substantially to the release of nutrient pollution into aquatic ecosystems (Carey and Migliaccio, 2009), advanced treatment technologies have been developed that can reduce nutrient pollution from wastewater effluent (Leo et al, 2011). Only 32% of US wastewater treatment facilities use advanced nutrient removal technologies (EPA, 2013) due to their high capital and operation costs. Algal turf scrubbers R can be used to treat aquatic ecosystems, contaminated groundwater, municipal sewage, and industrial/agricultural wastewater (Adey et al, 2011; Bohutskyi et al, 2016a)

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