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08/27/2015
Strategies for the Cost-Effective Management of Brine Wastewater from
Desalination Processes (by Arthur Rempel and Kyra Berger)
Clean water sources have recently become a scarce commodity across the globe. Brazil has
reported its worst drought in the past 50 years,[1] while South Africa expects a 32% downfall in
maize production this year alone due to a shortage of clean water. And, of course, California is
domestically affected,where all 12 of its clean-water reservoirs are at abnormally low levels (and
have been, for some time now.)
One available method to produce clean water focuses on desalination. Desalination is a process
that removes salts and other minerals from untreated water,producing water that is clean for both
human consumption and irrigation [2]. Ocean water makes up approximately 97% of the Earth’s
total water supply [3], suggesting that desalination is an attractive option as a clean water source -
especially for coastal regions, like the three aforementioned areas.
Desalination is typically conducted either via multistage flash thermal vacuum evaporation,
where saline water is boiled at extremely low pressures with excess heat,or reverse osmosis
membrane separation (ROMS),a process by which contaminated water is forced through a series
of semi-permeable membranes at high pressures to filter out salts, minerals, and residual metals.
Currently, only 1% of the Earth’s clean water supply is produced via desalination, although the
UN predicts that by the year 2025, “14% of the world’s population [will be] encountering water
scarcity [4].” Furthermore, the Western Hemisphere’s largest desalination plant is projected to
open in May of 2016 in southern California [5], which will theoretically provide 50 million
gallons of drinking water per day to the San Diego county area.
Unfortunately, high costs
(as compared to other clean
water sources) accompany
the desalination process,
predominantly due to
inefficient energy
consumption and ample
wastewater by-product,
usually referred to as brine
water.
Brine water is highly
concentrated salt water,
which also contains other
impurities like precious
metals that were used to purify the water during the desalination process. Due to its high salt
concentrations (typically about 30%, whereas ocean water usually spans the 1-5% range), brine
water will sink upon reentering the ocean,detrimentally affecting marine life and posing major
environmental concerns. Currently, a plethora of permits and federalregulations are required for
disposing brine water in sewer systems or in the ocean,which significantly contributes to the high
economic and energetic costs associated with desalination.
That is, the desalination process can consume as little as 3kWh/m3
(ROMS) [2], although this
value can reach anywhere from 13.5 up to 25.5kWh/m3
, in the case of thermal desalination. For
context, fresh water supplies typically require a maximum of 0.2kWh/m3
for treatment –
significantly less than any desalination process. Desalinated water costs on average $2,000 per
Figure 1. General schematic ofthe desalination process
08/27/2015
acre-foot (1acre-foot is about 3.26x105
gal, or the equivalent amount of water consumed on
average,annually by a family of five) [5], which is four times as much as money spent on water
from fresh sources; these high costs typically arise due to the difficulty in managing the brine by-
product. Storage facilities charge,on average,between $2.00 and $2.50 to store one cubic meter
of brine [8], which, in the case of the aforementioned desalination plant, would equate to
somewhere between $378,500 and $473,125 per day, assuming that one gallon of brine is
produced for every gallon of purified water [5].
A series of brine management strategies exist and are implemented in desalination plants across
the globe, although they are extremely dependent on a variety of variables: location, land
availability, air moisture content, legal/federal permitting requirements, and economic feasibility.
Brine concentrators and evaporation ponds are attractive options – both methods allow for
additional water recovery from brine wastewater (up to 94%) [7], and completely remove the
salts from the environment “by ultimately sequestering the remaining brine in a landfill or in a
closed and sealed evaporation pond.” Thus, the combination of these brine concentrators and
evaporation ponds are deemed environmentally desirable. Figure 2 below shows a general
schematic of General Electric’s brine concentrator [9].
Sadly, however, excessive costs
and energy consumption are
accompanied by these
environmental benefits,
rendering these processes
infeasible more often than not.
Brine concentrators typically
consume between 60 and
100kWh per 1000 gallons of
brine – assuming a cost of
$0.77/kWh, a brine concentrator
will generally require $4600-
$7700 per day to process 1 mgd
(million gallons per day) of
brine [8]. Or, in the case of the
plant from above, a daily charge
between $230,000 and
$385,000. Notice that these costs are between 20-40% lower than those of the storage facility
mentioned earlier, but they are not feasible or efficient by any means.
Table 1 below further illustrates the high costs associated with treating 10 mgd of brine with these
two strategies as compared to other methods [7]. Additionally, Table 2 depicts the energy
consumption pertaining to all of the specified methods, clearly highlighting the excess energy
required for brine concentrators in comparison to the other methods.
Table 1. Costs of evaporation ponds and brine concentrators compared to other strategies
Figure 2. General Schematic of a brine concentrator
08/27/2015
Table 2. Energy consumption of various brine-wastewater treatment methods
In addition to energy and management costs, brine wastewater also suffers from economic
opportunity costs via the lack of recovering useful byproducts. These byproducts may consist of
selenium, nitrates, gypsum and calcium compounds, which “are widely used in the building
industry for drywall, plaster, and cement [10].” Other byproducts could consist of magnesium
salts, which are useful in the medical industry, and boron, which is a recent hot topic in high-
efficiency electronics. Finally, if purified appropriately, any recovered sea salt could be sold as a
raw material to further increase profitability.
We are interested in studying whether it is possible to improve the brine concentrator/evaporation
pond system in terms of both energy and cost, since their environmental benefits are
unprecedented among other common brine-management techniques. If possible, this would not
only be economically attractive to investors and desalination firms, but would also give rise to a
new, affordable, clean, and abundant water resource.
As such, this design project aims to study the thermal treatment of brine wastewater and
subsequently perform an in-depth economic analysis to determine whether brine concentrators
and evaporation ponds can become more cost-effective waste management strategies for
desalination plants. First, we will create a scaled-down experimental set-up of a brine
concentrator, which, alongside ASPEN PLUS simulation modeling, will allow us to somewhat
mimic a brine concentrator, providing us with a basis for the scaled-down energy consumption of
our brine concentrator/evaporation pond.
We then plan on examining the energy consumption required to purify various brine samples after
altering elements of the design process,including but not limited to: batch vs. semi-continuous
vs. fully continuous, and chemical composition (for example, using organo/carbocatalysts or
anticaking agents). Additionally, we plan on exploring the possibility of purifying brine
wastewater solutions and subsequently extracting economically valuable byproducts as a method
of reducing both costs and wastes,increasing efficiency in the long run. Ideally, the results
obtained from these various alterations will allow us to project any possible energy gains in the
brine treatment process via concentrator and evaporation ponds, and in turn, lead to economic
benefits and cost reductions for the respective brine management strategies.
References:
[1]http://www.usatoday.com/story/news/world/2015/07/24/historic-droughts-wreak-havoc-usa-
brazil-n-korea/30513289/
[2]https://en.wikipedia.org/wiki/Desalination#Energy_consumption
[3]http://www.noaa.gov/ocean.html
[4]http://www.globalwaterintel.com/desalination-industry-enjoys-growth-spurt-scarcity-starts-
bite/
[5]http://www.mercurynews.com/science/ci_25859513/nations-largest-ocean-desalination-plant-
goes-up-near
08/27/2015
[6] http://www.eia.gov/electricity/monthly/epm_table_grapher.cfm?t=epmt_5_6_a
[7] http://www.usbr.gov/lc/phoenix/programs/cass/pdf/SABD.pdf
[8] http://www.greentechmedia.com/articles/read/desalination-without-the-ocean
[9] http://www.gewater.com/zero-liquid-discharge-zld.html#featuredproductssection
[10] http://cleantechnica.com/2014/02/18/tiny-solar-power-desalination-plant-solves-big-salt-
problem/

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Rempel_Berger_FINAL_Proposal

  • 1. 08/27/2015 Strategies for the Cost-Effective Management of Brine Wastewater from Desalination Processes (by Arthur Rempel and Kyra Berger) Clean water sources have recently become a scarce commodity across the globe. Brazil has reported its worst drought in the past 50 years,[1] while South Africa expects a 32% downfall in maize production this year alone due to a shortage of clean water. And, of course, California is domestically affected,where all 12 of its clean-water reservoirs are at abnormally low levels (and have been, for some time now.) One available method to produce clean water focuses on desalination. Desalination is a process that removes salts and other minerals from untreated water,producing water that is clean for both human consumption and irrigation [2]. Ocean water makes up approximately 97% of the Earth’s total water supply [3], suggesting that desalination is an attractive option as a clean water source - especially for coastal regions, like the three aforementioned areas. Desalination is typically conducted either via multistage flash thermal vacuum evaporation, where saline water is boiled at extremely low pressures with excess heat,or reverse osmosis membrane separation (ROMS),a process by which contaminated water is forced through a series of semi-permeable membranes at high pressures to filter out salts, minerals, and residual metals. Currently, only 1% of the Earth’s clean water supply is produced via desalination, although the UN predicts that by the year 2025, “14% of the world’s population [will be] encountering water scarcity [4].” Furthermore, the Western Hemisphere’s largest desalination plant is projected to open in May of 2016 in southern California [5], which will theoretically provide 50 million gallons of drinking water per day to the San Diego county area. Unfortunately, high costs (as compared to other clean water sources) accompany the desalination process, predominantly due to inefficient energy consumption and ample wastewater by-product, usually referred to as brine water. Brine water is highly concentrated salt water, which also contains other impurities like precious metals that were used to purify the water during the desalination process. Due to its high salt concentrations (typically about 30%, whereas ocean water usually spans the 1-5% range), brine water will sink upon reentering the ocean,detrimentally affecting marine life and posing major environmental concerns. Currently, a plethora of permits and federalregulations are required for disposing brine water in sewer systems or in the ocean,which significantly contributes to the high economic and energetic costs associated with desalination. That is, the desalination process can consume as little as 3kWh/m3 (ROMS) [2], although this value can reach anywhere from 13.5 up to 25.5kWh/m3 , in the case of thermal desalination. For context, fresh water supplies typically require a maximum of 0.2kWh/m3 for treatment – significantly less than any desalination process. Desalinated water costs on average $2,000 per Figure 1. General schematic ofthe desalination process
  • 2. 08/27/2015 acre-foot (1acre-foot is about 3.26x105 gal, or the equivalent amount of water consumed on average,annually by a family of five) [5], which is four times as much as money spent on water from fresh sources; these high costs typically arise due to the difficulty in managing the brine by- product. Storage facilities charge,on average,between $2.00 and $2.50 to store one cubic meter of brine [8], which, in the case of the aforementioned desalination plant, would equate to somewhere between $378,500 and $473,125 per day, assuming that one gallon of brine is produced for every gallon of purified water [5]. A series of brine management strategies exist and are implemented in desalination plants across the globe, although they are extremely dependent on a variety of variables: location, land availability, air moisture content, legal/federal permitting requirements, and economic feasibility. Brine concentrators and evaporation ponds are attractive options – both methods allow for additional water recovery from brine wastewater (up to 94%) [7], and completely remove the salts from the environment “by ultimately sequestering the remaining brine in a landfill or in a closed and sealed evaporation pond.” Thus, the combination of these brine concentrators and evaporation ponds are deemed environmentally desirable. Figure 2 below shows a general schematic of General Electric’s brine concentrator [9]. Sadly, however, excessive costs and energy consumption are accompanied by these environmental benefits, rendering these processes infeasible more often than not. Brine concentrators typically consume between 60 and 100kWh per 1000 gallons of brine – assuming a cost of $0.77/kWh, a brine concentrator will generally require $4600- $7700 per day to process 1 mgd (million gallons per day) of brine [8]. Or, in the case of the plant from above, a daily charge between $230,000 and $385,000. Notice that these costs are between 20-40% lower than those of the storage facility mentioned earlier, but they are not feasible or efficient by any means. Table 1 below further illustrates the high costs associated with treating 10 mgd of brine with these two strategies as compared to other methods [7]. Additionally, Table 2 depicts the energy consumption pertaining to all of the specified methods, clearly highlighting the excess energy required for brine concentrators in comparison to the other methods. Table 1. Costs of evaporation ponds and brine concentrators compared to other strategies Figure 2. General Schematic of a brine concentrator
  • 3. 08/27/2015 Table 2. Energy consumption of various brine-wastewater treatment methods In addition to energy and management costs, brine wastewater also suffers from economic opportunity costs via the lack of recovering useful byproducts. These byproducts may consist of selenium, nitrates, gypsum and calcium compounds, which “are widely used in the building industry for drywall, plaster, and cement [10].” Other byproducts could consist of magnesium salts, which are useful in the medical industry, and boron, which is a recent hot topic in high- efficiency electronics. Finally, if purified appropriately, any recovered sea salt could be sold as a raw material to further increase profitability. We are interested in studying whether it is possible to improve the brine concentrator/evaporation pond system in terms of both energy and cost, since their environmental benefits are unprecedented among other common brine-management techniques. If possible, this would not only be economically attractive to investors and desalination firms, but would also give rise to a new, affordable, clean, and abundant water resource. As such, this design project aims to study the thermal treatment of brine wastewater and subsequently perform an in-depth economic analysis to determine whether brine concentrators and evaporation ponds can become more cost-effective waste management strategies for desalination plants. First, we will create a scaled-down experimental set-up of a brine concentrator, which, alongside ASPEN PLUS simulation modeling, will allow us to somewhat mimic a brine concentrator, providing us with a basis for the scaled-down energy consumption of our brine concentrator/evaporation pond. We then plan on examining the energy consumption required to purify various brine samples after altering elements of the design process,including but not limited to: batch vs. semi-continuous vs. fully continuous, and chemical composition (for example, using organo/carbocatalysts or anticaking agents). Additionally, we plan on exploring the possibility of purifying brine wastewater solutions and subsequently extracting economically valuable byproducts as a method of reducing both costs and wastes,increasing efficiency in the long run. Ideally, the results obtained from these various alterations will allow us to project any possible energy gains in the brine treatment process via concentrator and evaporation ponds, and in turn, lead to economic benefits and cost reductions for the respective brine management strategies. References: [1]http://www.usatoday.com/story/news/world/2015/07/24/historic-droughts-wreak-havoc-usa- brazil-n-korea/30513289/ [2]https://en.wikipedia.org/wiki/Desalination#Energy_consumption [3]http://www.noaa.gov/ocean.html [4]http://www.globalwaterintel.com/desalination-industry-enjoys-growth-spurt-scarcity-starts- bite/ [5]http://www.mercurynews.com/science/ci_25859513/nations-largest-ocean-desalination-plant- goes-up-near
  • 4. 08/27/2015 [6] http://www.eia.gov/electricity/monthly/epm_table_grapher.cfm?t=epmt_5_6_a [7] http://www.usbr.gov/lc/phoenix/programs/cass/pdf/SABD.pdf [8] http://www.greentechmedia.com/articles/read/desalination-without-the-ocean [9] http://www.gewater.com/zero-liquid-discharge-zld.html#featuredproductssection [10] http://cleantechnica.com/2014/02/18/tiny-solar-power-desalination-plant-solves-big-salt- problem/