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Insights into the Evolution of an Emulsion with Demulsifying Bacteria based on Turbiscan Kaiming Peng, Xuhui Wang, Lijun Lu, Jia Liu, Xiupeng Guan, and Xiang-Feng Huang Ind. Eng. Chem. Res., Just Accepted Manuscript • DOI: 10.1021/acs.iecr.6b01347 • Publication Date (Web): 03 Jun 2016 Downloaded from http://pubs.acs.org on June 7, 2016
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Industrial & Engineering Chemistry Research
Insights into the Evolution of an Emulsion with Demulsifying Bacteria based on Turbiscan Kaiming Peng,†# Xuhui Wang,‡# Lijun Lu,‡ Jia Liu,‡ Xiupeng Guan,§ Xiangfeng Huang‡*
†
Tongji University, Shanghai, 200092, China
‡
College of Environmental Science and Engineering, State Key Laboratory of Pollution Control and Resource Reuse, Tongji University, Shanghai 200092, China
§
Beijing LDS Technology Co., Ltd., Beijing, 100101, China
*
To whom correspondence should be addressed:
Xiangfeng Huang; Telephone: +86 21 65985792; E-mail:
[email protected]. #
These authors have contributed equally to this work.
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ABSTRACT In this study, the demulsification process of four demulsifying bacteria was analyzed in situ using a newly developed method based on backscattering data from Turbiscan. First, the distribution difference of backscattering was employed to divide the entire demulsification process. Second, the Mie theory and the first order differential of the backscattering intensity along emulsion height were introduced to track emulsion variation over time. The demulsification process was divided into three stages. Consumption time, changing degree, and changing velocity during each stage varied depending on the type of bacteria. The flocculation and coalescence of water drops in the initial stage contributed substantially to the final demulsification efficiency. This study provides a powerful tool for understanding the evolution of emulsions in response to the action of various demulsifiers.
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1. Introduction Demulsification is the process of separating water and oil from an emulsion. This
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is one of the first steps during the processing of crude oil and the disposal of waste
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emulsions. Currently, chemical,1 physical,2,3 and biological4-8 methods are used for
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demulsification. Chemical demulsification has been widely applied to industrial
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production processes. However, chemical demulsifiers contain some refractory
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organic polymers, which may be hazardous for the environment.9 In contrast,
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demulsifying bacteria are characterized by a diverse structure, low toxicity,
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environmental compatibility, and high demulsifying efficiency under extreme
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conditions.7 Early studies have evaluated the demulsifying ability of bacteria, such as
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Alcaligenes sp.,10 Diezia sp.,11 and Ochrobactrum anthropi,12 isolated mainly from
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hydrocarbon-contaminated environments. The demulsifying ability has been shown to
13
depend on bacterial surface hydrophobicity, which was derived from its cell-surface
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chemical composition.13,14 To gain a better understanding of its underlying mechanism,
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the demulsification process carried out by bacteria requires further studies.
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The demulsification process has been characterized mostly with respect to
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demulsification efficiency,8,15 evolution of particle size,16-18 and comprehensive
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monitoring of the process.19-23 The bottle test is the most widely used method for
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studying demulsification efficiency, but it provides limited information. Both laser
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light scattering16,18 and microscopy8,17 have been used to characterize demulsification
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performance by observing the evolution of particle size, yet dilution or staining
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disturbs the stability of the emulsion, thereby reducing test accuracy.5,15 The entire
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demulsification process can be monitored using the recently developed
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Turbiscan19,21-23 and Low-Field Nuclear Magnetic Resonance (LF-NMR)
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methods.20,24 LF-NMR provides precise information about phase separation and
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particle size distribution, but its high cost and strict requirements for the test
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environment severely limit its widespread applicability. Turbiscan is based on the
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principle of multiple light scattering and it has been used to monitor the evolution of
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emulsions according to the intensity of backscattering (BS) and transmission (T).
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Turbiscan offers an easier analysis process and lower cost per test, making it ideal for
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the characterization of real-time emulsion stability and monitoring of demulsification
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processes.8,22 The application of Turbiscan to the analysis of demulsification has so far been
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limited to the qualitative description of its characteristics.25-28 Lesaint et al. (2009)
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employed Turbiscan to monitor phase separation in emulsion and optimized
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parameters for the dehydration process.29 Using Turbiscan to visualize the
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demulsification process of a water-in-oil (W/O) emulsion, Wen et al. (2010) found
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that dispersed water droplets flocculated and coalesced, decreased in total numbers,
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settled to the bottom, and phase separated in W/O emulsion.15 Liu et al. (2011)
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employed delta BS intensity to explore the long-term destabilization of emulsions
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with two different biodemulsifiers.8 Meanwhile, Turbiscan quantitative evaluation
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indices such as turbiscan stability index21,30 and emulsion stability index,31 have been
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developed to analyze the demulsification process. However, these indicators capture
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only the final emulsion stability, failing to monitor the demulsification process.
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Consequently, a quantitative analysis method for the entire demulsification process is
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still not available.
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In our previous studies, we characterized the demulsifying strain Alcaligenes sp.
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S-XJ-1 from petroleum-polluted soil.10 The S-XJ-1 cells cultivated with different
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carbon sources displayed varied surface composition, cell surface properties, and
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demulsifying ratios.14,32 Here, we established a quantitative Turbiscan-based method
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to analyze the demulsification process of S-XJ-1 cells cultured with different carbon
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sources. Division of the entire demulsification process in stages and quantitative
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analysis of each stage were conducted based on BS data.
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2. Materials and methods
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2.1 Sample preparation
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The demulsifying strain Alcaligenes sp. S-XJ-1 was cultivated in modified
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mineral salts medium containing paraffin, rapeoil, octodecane, or olein as carbon
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sources, and labeled D-1, D-2, D-3, and D-4, respectively. The demulsifying bacteria
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were harvested by centrifugation, dried in a freeze drier (Scientz-10N; Ningbo Scientz
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Biotechnology, Zhejiang, China), and then used to characterize demulsifying ability.
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The cultivation and preparation process was described earlier.14
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The W/O model emulsion was prepared as in our previous report.15 Aviation
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kerosene (80 mL, containing 1.526 g Tween 80 and 0.074 g Span 80) and distilled
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water (120 mL) were mixed at 10 000 rpm with a high-speed emulsifying machine
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(WL-500CY, Shanghai Wei Yu Mechanical and Electrical Manufacture Limited
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Company, China) for 3.5 min. The fresh mixture had an emulsion breaking ratio of 0.9) in size at the
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start of demulsification. The changing velocity of particle size reached 0.31–24.30
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µm/h.
Table 1. Change of particle size as a function of time during the flocculation and coalescence stage. d0 (µm)
dt (µm)
PF&C
vD (µm/h)
D-1
8.45
15.49
83.23%
24.30 (R2=0.973)
D-2
4.01
7.30
82.06%
1.08 (R2=0.957)
D-3
7.00
11.67
66.78%
0.72 (R2=0.970)
D-4
7.84
11.69
49.21%
0.31 (R2=0.991)
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d0, initial mean diameter of water droplets.
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dt, critical mean diameter when drops begin to settle.
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PF&C, changing degree.
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vD, particle size velocity.
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3.3.2 Sedimentation stage
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In stage II, the uneven decrease in BS intensity caused the BS profiles to exhibit
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a convex “platform” which was designated as the remaining emulsion layer.15 In this
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layer, BS intensity increased as a result of the sedimentation of big drops and the
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flocculation of small droplets. The position around the bottom of the remaining layer,
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where maximum FBS,h occurred, was named sedimentation interface. Migration of the
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sedimentation interface was calculated to describe the settling process (Table 2). The
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sedimentation degree (PSE) of the water drops was calculated using the following
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formula: PSE =
2
H SE ,0 − H SE ,e H
× 100% (6)
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where HSE,0 and HSE,e are the starting and ending positions of the sedimentation
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interface, respectively; and H is the total height of the emulsion. PSE reached
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18.28–45.73%, depending on the demulsifying bacteria. For a more detailed
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description, the settling process was divided into two sections, a quick and a slow one,
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based on the settling velocity. In the quick-settling section that dominated stage II,
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water drops settled at a steady speed (vSE) of 6.92–28.39 mm/h (R2>0.85).
Table 2. The settling of water drops in the sedimentation stage. HSE,0 (mm)
HSE,e (mm)
PSE
tSE (h)*
vSE (mm/h) *
D-1
36.56
24.56
45.73%
0.63
28.39(R2=0.973)
D-2
31.28
18.76
31.34%
3.55
10.56(R2=0.960)
D-3
23.60
16.48
18.28%
4.05
6.92(R2=0.872)
D-4
20.36
6.20
36.68%
11.55
28.32(-)*
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*
tSE: stopping time point of the quick settling process.
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*
vSE: sedimentation velocity in the quick-settling section.
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*
- indicates an insufficient number of data points during the settling process.
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Another method used to describe the settling process is Stocks’ equation,
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whereby the settling speed of a single droplet can be accurately calculated if viscosity
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of the emulsion and real-time particle size are known. However, because these
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parameters keep changing during the demulsification process, they are difficult to
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obtain. The viscosity of an emulsion is closely related to the packing density of
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dispersed water, which also changes continously.36 The declining BS intensity
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suggested a variation in particle size. The Stocks’ equation is more suitable as the
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theoretical basis of the settling process rather than for a quantitative description of it.8
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Consequently, analysis based on real-time BS was more suitable for describing the
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settling of drops during the demulsification process.
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3.3.3 Dewatering stage
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In stage III, the sharp and consistent decline in BS intensity at the bottom of the
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emulsion was caused by the dewatering process. To enable an accurate description of
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this process, a specific BS intensity δ (δ=20% in this study) was introduced to delimit
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the dewatering region.8 Meanwhile, the rapid increase in BS intensity along sample
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height indicated the dewatering interface, which was located using the maximum FBS,h.
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The specific BS intensity δ and the maximum FBS,h allowed the precise tracking of the
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dewatering process. The dewatering degree (PDW) was calculated as follows:
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PDW =
H DW t = 24 h HW
× 100%
(7)
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where HW is the total height of all water in the emulsion (HW=0.6 × H) and HDW is the
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location of the dewatering interface. PDW ranged from 38.30 to 99.93% after 24 h of
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treatment with the four demulsifying bacteria. The dewatering process was also
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divided into a quick and slow section. In the quick section, the dewatering proceeded
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at a steady speed (R2>0.9), 6.80–19.56 mm/h, whereas in the slow section dewatering
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occurred at a slower and less steady speed (R2>0.75) with rate of 0.05–0.12 mm/h
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(Table 3). Overall, the dewatering process was stable and steady (Figure 7).
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Figure 7. Dewatering and deoiling of the emulsion. Red dashed lines indicate the
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dewatering starting time and black dashed lines at the inflection points correspond to
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the equilibrium time after which extremely slow dewatering began.
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Table 3. The dewatering process according to the migration of dewatering interface. HDW
te (h)*
PDW
(mm)
Slow-section
23.60
99.93%
3.05
19.56(R2=0.946)
0.05(R2=0.771)
D-2
17.64
75.54%
6.05
6.94(R2=0.922)
0.11(R2=0.919)
D-3
16.80
73.99%
5.55
6.80(R2=0.934)
0.12 (R2=0.909)
D-4
8.88
38.30%
12.55
7.12(R2=0.964)
0.08 (R2=0.823)
*
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vDW, dewatering velocity.
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Quick-section
D-1
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vDW (mm/h)
te, equilibrium time point for the dewatering process.
3.3.4 Accompanying deoiling process Serial transformations of water drops during the three stages of demulsification 21
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were coupled with escape of the oil phase, as indicated by the sharp decline in BS
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intensity at the top of the emulsion. The deoiling interface was located using the
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minimum FBS,h, and its migration was then used to analyze the deoiling process
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(Figure 7). The deoiling degree (PDO) was calculated as follows: PDO =
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H − H DO t = 24 h HO
× 100% (8)
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where HO is the total height of the oil phase, and HDO is the location of the deoiling
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interface. PDO ranged from 38.30 to 99.93% (Table 4). According to the deoiling
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profiles, the deoiling process was divided into a quick and a slow section.
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Table
4.
Migration
of
the
deoiling
interface
during
the
demulsification process. vDo LDo
PDo Quick-section
Slow-section
D-1
26.68
15.15(R2=0.906)
0.017(R2=0.3546)
99.93%
D-2
26.52
1.64(R2=0.96)
0.176(R2=0.3546)
75.54%
D-3
25.72
1.23(R2=0.9565)
0.209(R2=0.9342)
73.99%
D-4
29.76
0.364(R2=0.9908)
38.30%
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In summary, using BS profiles and the computed FBS,h curve, the evolution of the
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demulsification process can be described quantitatively. As shown in Figure 8, the BS
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profile can serve as an indicator of deoiling, emulsion, dehydrating, and dehydrated
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areas. In addition, the FBS,h curve is sensitive to the precise location of the interfaces 22
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between adjacent areas, which was helpful for the quantitative description of the
2
demulsification process. However, neither the BS profile nor the FBS,h curve alone
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was sufficient to accurately identify the interface of sedimentation and dewatering.
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Establishing these interfaces required the combined analysis of both profiles. Thus, by
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using both the real-time BS profile and the FBS,h curve, the demulsifying process
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could be thoroughly analyzed.
Deoiling area
Ⅰ Emulsion area
Ⅱ Dehydrating area Ⅲ Dehydrated area BS(%)
7
FBS,h
8
Figure 8. Diagram of the analysis method for the demulsification process.
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3.4 Comparing the demulsification process of four demulsifying
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bacteria Bacteria growing on four distinct carbon sources exhibited different consumption
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times and completion degrees at each stage (Figure 9). In terms of performance, D-1
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showed the highest demulsification ratio (93% within 3.05 h), followed by D-2, D-3,
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and D-4. In addition, D-1 reached the highest competition degree: 83.23% in stage I,
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45.73% in stage II, and 99.93% in stage III. The largest difference between the four
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demulsifying bacteria was observed in stage I, where competition degree and 23
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consumption time varied the most.
2 3 4
Figure 9. Diagram of the demulsification process by four demulsifying bacteria. We reported previously that demulsifying bacteria cultivated in paraffin, rapeoil,
5
octodecane, and olein presented different surface composition, 14 various surface
6
properties,32 and diverse adhesion capability to water-oil interface.8,15 D-1, cultivated
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with paraffin as carbon source, was rich in protein (32%), displayed a higher surface
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hydrophobicity, and could easily reach the water-oil interface.14 Those characteristics
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facilitated bacterial adhesion and aggregation onto the interface, promoted the
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destruction of interfacial film, and accelerated the flocculation and coalescence of
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dispersed droplets. This in turn, resulted in a faster settling of drops and contributed to
12
better phase separation.12,15
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4. Conclusions
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In this study, a new method based on Turbiscan was developed to quantitatively
15
analyze the biological demulsification process. According to the BS profiles, the
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demulsification process was accurately divided into three stages: flocculation and
17
coalescence of water drops, sedimentation of dispersed water drops, and the 24
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dewatering process. Each stage was evaluated using changing degree and velocity. It
2
was found that performance of the demulsifying bacteria in the flocculation and
3
coalescence stage was enough to derive their overall demulsifying capability. Using
4
this novel analysis method, a more comprehensive and detailed analysis of the entire
5
demulsification process was performed contributing to a better understanding of the
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demulsification mechanism.
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ACKNOWLEDGMENTS
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The authors gratefully acknowledge financial support from the National Natural
9
Science Foundation of China (grant no. 51478325) and China Postdoctoral Science
10
Foundation (grant no. 2016M591711).
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