ALBERT

Description: Arid countries throughout the world are heavily reliant on seawater desalination for their supply of drinking and municipal water. The desalination industry is large and rapidly growing, approaching more than 20,000 plants operating or contracted in greater than 150 countries worldwide and capacity projected to grow at a rate of 12% per year for the next several decades (http://www.desaldata.com; 2016). Desalination plants are broadly distributed worldwide, with a large and growing capacity in what will be referred to as the “Gulf” region throughout this manual. Here the Gulf refers to the shallow body of water bounded in the southwest by the Arabian Peninsula and Iran to the northeast. The Gulf is linked with the Arabian Sea by the Strait of Hormuz and the Gulf of Oman to the east and extends to the Shatt al-Arab river delta at its western end. One of the operational challenges facing the industry is also expanding globally – the phenomena termed harmful algal blooms or HABs. Blooms are cell proliferations caused by the growth and accumulation of individual algal species; they occur in virtually all bodies of water. The algae, which can be either microscopic or macroscopic (e.g., seaweeds) are the base of the marine food web, and produce roughly half of the oxygen we breathe. Most of the thousands of species of algae are beneficial to humans and the environment, but there are a small number (several hundred) that cause HABs. This number is vague because the harm caused by HABs is diverse and affects many different sectors of society (see Chapter 1). HABs are generally considered in two groups. One contains the species that produce potent toxins (Chapter 2) that can cause a wide range of impacts to marine resources, including mass mortalities of fish, shellfish, seabirds, marine mammals, and various other organisms, as well as illness and death in humans and other consumers of fish or shellfish that have accumulated the algal toxins during feeding. The second category is represented by species that produce dense blooms - often termed high biomass blooms because of the large number of cells. Cells can reach concentrations sufficient to make the water appear red (hence the common term “red tide”), though brown, green and golden blooms are also observed, while many blooms are not visible. In this manual, we define toxic algae as those that produce potent toxins (poisonous substances produced within living cells or organisms), e.g., saxitoxin. These can cause illness or mortality in humans as well as marine life through either direct exposure to the toxin or ingestion of bioaccumulated toxin in higher trophic levels e.g. shellfish. Non-toxic HABs can cause damage to ecosystems and commercial facilities such as desalination plants, sometimes because of the biomass of the accumulated algae, and in other cases due to the release of compounds that are not toxins (e.g., reactive oxygen species, mucilage) but that can still be lethal to marine animals or cause disruptions of other types. Both toxic and non-toxic HABs represent potential threats to seawater desalination facilities. Although toxins are typically removed very well by reverse osmosis and thermal desalination processes (see Chapter 10), algal toxins represent a potential health risk if they are present in sufficiently high concentrations in the seawater and if they break through the desalination process. It is therefore important for operators to be aware when toxic blooms are near their plants so they can ensure that the removal has indeed occurred (Chapter 3). High biomass blooms pose a different type of threat, as the resulting particulate and dissolved organic material can accelerate clogging of media filters or contribute to (bio)fouling of pretreatment and RO membranes which may lead to a loss of production. Impacts of HABs on desalination facilities are thus a significant and growing problem, made worse by the lack of knowledge of this phenomena among plant operators, managers, engineers, and others involved in the industry, including regulatory agencies. Recognizing this problem, the Middle East Desalination Research Center (MEDRC) and the UNESCO Intergovernmental Oceanographic Commission (IOC) organized a conference in 2012 in Muscat, Oman, to bring HAB researchers and desalination professionals together to exchange knowledge and discuss the scale of the problem and strategies for addressing it. One of the recommendations of that meeting was that a “guidance manual” be prepared to provide information to desalination plant operators and others in the industry about HABs, their impacts, and the strategies that could be used to mitigate those impacts. With support from the US Agency for International Development (USAID) and the IOC Intergovernmental Panel for Harmful Algal Blooms (IPHAB), an editorial team was assembled and potential authors contacted. For the first time, HAB scientists worked closely with desalination professionals to write chapters that were scientifically rigorous yet practical in nature – all focused on HABs and desalination. During the planning of this manual, it became clear from an informal survey of the desalination industry that generally, HAB problems are far more significant for seawater reverse osmosis (SWRO) plants than for those that use thermal desalination. Both types of processes are very effective in removing HAB toxins (Chapter 10), but the SWRO plants are far more susceptible to clogging of pretreatment granular media filters and fouling of membranes by algal organic matter and particulate biomass. Accordingly, the focus of this book is on SWRO, with only occasional reference to thermal processes. Likewise, emphasis has been placed on seawater HABs, with reference to estuarine and brackish-water HABs only when practices from those types of waters can be informative or illustrative. A brief synopsis of the book follows. Chapter 1 provides a broad overview of HAB phenomena, including their impacts, the spatial and temporal nature of their blooms, common causative species, trends in occurrence, and general aspects of bloom dynamics in coastal waters. Chapter 2 describes the metabolites of HAB cells, including toxins, taste and odor compounds. Methods for analyses are presented there, supplemented by detailed methodological descriptions of rapid toxin screening methods in Appendix 2. As discussed in Chapters 8 and 10, thermal and SWRO operations are highly effective in the removal of HAB toxins, but plant personnel should have the capability to screen for these toxins in raw and treated water to ensure that this removal has been effective. This would be critical, for example, if the public or the press were aware of a toxic HAB in the vicinity of a desalination plant intake and asked for proof that their drinking water is safe. Currently, most desalination plants do not collect data on seawater outside their plants, so they are generally unaware of the presence (now or anticipated) of a potentially disruptive HAB. Chapter 3 provides practical information on the approaches to implementing an observing system for HABs, describing sampling methods and measurement options that can be tailored to available resources and the nature of the HAB threat in a given area. Appendix 4 provides more details on methods used to count and identify HAB cells during this process. All are based on direct water sampling, but it is also possible to observe HABs from space – particularly the high biomass events. Chapter 4 describes how satellite remote sensing can be used to detect booms. The common sources of imagery (free over the Internet) are presented, as well as descriptions of the software (also free) that can be used to analyze the satellite data. It is relatively easy and highly informative for plant personnel to use this approach to better understand what is in the seawater outside their plants. The cover of this guide provides a graphic example of the incredible scale and resolution of this observational approach. Chapter 5 discusses typical water quality parameters that are measured online or in feedwater samples at desalination plants that could be used to detect blooms at the intake or evaluate process efficiency in removing algal particulates and organics. Emerging parameters that also show promise are examined to provide a resource for plant personnel. Chapter 6 looks at desalination seawater intakes that are the first point of control in minimizing the ingress of algae into the plant. A brief overview of siting considerations that may ultimately drive the location of an intake is also provided. One question asked frequently of HAB scientists is whether the blooms can be controlled or suppressed in a manner analogous to the treatment of insects or other agricultural pests on land. This has proven to be an exceedingly difficult challenge for the HAB scientific and management community, given the dynamic nature of HABs in coastal waters, their large spatial extent, and concerns about the environmental impacts of bloom control methods. Chapter 7 presents a summary of the approaches to bloom prevention and control that have been developed, and discusses whether these are feasible or realistic in the context of an individual desalination plant. Chapter 8 describes management strategies for HABs and risk assessment, including Hazard Analysis Critical Control Point (HACCP) and Alert Level Framework procedures. Once a HAB is detected, a wide range of approaches can be used to address the problems posed by the dissolved toxins associated with those blooms. Chapter 9 presents many of these pretreatment strategies and discusses their use in removing algal organic matter and particulates to prevent filter clogging and membrane fouling. This is necessary to maintain effective plant operation and avoid serious operational challenges for the reverse osmosis step. The chapter covers common pretreatments such as chlorination/dechlorination, coagulation, dissolved air flotation, granular media filtration, ultrafiltration, and cartridge filtration, in addition to discussing issues experienced due to the inefficiencies of each pretreatment on reverse osmosis. Chapter 10 then addresses the important issue of HAB toxin removal during pretreatment and desalination, and describes laboratory and pilot-scale studies that address that issue. Finally, Chapter 11 provides a series of case studies describing individual HAB events at desalination plants throughout the world, detailing the types of impacts and the strategies that were used to combat them. These studies should be of great interest to other operators as they encounter similar challenges. The manual concludes with a series of appendices that provide images and short descriptions of common HAB species (Appendix 1), rapid screening methods for HAB toxins (Appendix 2), methods to measure transparent exopolymer particles (TEP) and their precursors (Appendix 3), methods to enumerate algal cells (Appendix 4), and reverse osmosis autopsy and cleaning methods (Appendix 5).

Description: OPENASFA INPUT For bibliographic purposes this document should be cited as follows: Anderson D. M., S. F. E. Boerlage, M. B. Dixon (Eds), Harmful Algal Blooms (HABs) and Desalination: A Guide to Impacts, Monitoring and Management. Paris, Intergovernmental Oceanographic Commission of UNESCO, 2017. 539 pp. (IOC Manuals and Guides No.78.) (English.) (IOC/2017/MG/78).

Description: Published

Description: Refereed

Description: © The Author(s), 2021. This article is distributed under the terms of the Creative Commons Attribution License. The definitive version was published in Tian, Y., Liu, X., Li, J., Deng, Y., DeGiorgis, J. A., Zhou, S., Caratenuto, A., Minus, M. L., Wan, Y., Xiao, G., & Zheng, Y. Farm-waste-derived recyclable photothermal evaporator. Cell Reports Physical Science, 2(9), (2021): 100549, https://doi.org/10.1016./j.xcrp.2021.100549

Description: Interfacial solar steam generation is emerging as a promising technique for efficient desalination. Although increasing efforts have been made, challenges exist for achieving a balance among a plethora of performance indicators—for example, rapid evaporation, durability, low-cost deployment, and salt rejection. Here, we demonstrate that carbonized manure can convert 98% of sunlight into heat, and the strong capillarity of porous carbon fibers networks pumps sufficient water to evaporation interfaces. Salt diffusion within microchannels enables quick salt drainage to the bulk seawater to prevent salt accumulation. With these advantages, this biomass-derived evaporator is demonstrated to feature a high evaporation rate of 2.81 kg m−2 h−1 under 1 sun with broad robustness to acidity and alkalinity. These advantages, together with facial deployment, offer an approach for converting farm waste to energy with high efficiency and easy implementation, which is particularly well suited for developing regions.

Description: This project is supported by the National Science Foundation through grant no. CBET-1941743. This project is based upon work supported in part by the National Science Foundation under EPSCoR Cooperative Agreement no. OIA-1655221.